Energy Conservation Program for Consumer Products: Energy Conservation Standards for Residential Furnace Fans, 38129-38211 [2014-15387]
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Vol. 79
Thursday,
No. 128
July 3, 2014
Part II
Department of Energy
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10 CFR Parts 429 and 430
Energy Conservation Program for Consumer Products: Energy
Conservation Standards for Residential Furnace Fans; Final Rule
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Federal Register / Vol. 79, No. 128 / Thursday, July 3, 2014 / Rules and Regulations
FOR FURTHER INFORMATION CONTACT:
DEPARTMENT OF ENERGY
10 CFR Parts 429 and 430
[Docket Number EERE–2010–BT–STD–
0011]
RIN 1904–AC22
Energy Conservation Program for
Consumer Products: Energy
Conservation Standards for
Residential Furnace Fans
Office of Energy Efficiency and
Renewable Energy, Department of
Energy.
ACTION: Final rule.
AGENCY:
Pursuant to the Energy Policy
and Conservation Act of 1975 (EPCA),
as amended, the U.S. Department of
Energy (DOE) must prescribe energy
conservation standards for various
consumer products and certain
commercial and industrial equipment,
including residential furnace fans.
EPCA requires DOE to determine
whether such standards would be
technologically feasible and
economically justified, and would save
a significant amount of energy. In this
final rule, DOE is adopting new energy
conservation standards for residential
furnace fans. DOE has determined that
the prescribed energy conservation
standards for these products would
result in significant conservation of
energy, and are technologically feasible
and economically justified.
DATES: The effective date of this rule is
September 2, 2014. Compliance with the
prescribed standards established for
residential furnace fans in this final rule
is required on and after July 3, 2019.
ADDRESSES: The docket for this
rulemaking, which includes Federal
Register notices, public meeting
attendee lists and transcripts,
comments, and other supporting
documents/materials, is available for
review at www.regulations.gov. All
documents in the docket are listed in
the www.regulations.gov index.
However, not all documents listed in
the index may be publicly available,
such as information that is exempt from
public disclosure.
A link to the docket Web page can be
found at: https://www1.eere.energy.gov/
buildings/appliance_standards/
rulemaking.aspx/ruleid/41. The
www.regulations.gov Web page contains
simple instructions on how to access all
documents, including public comments,
in the docket.
For further information on how to
review the docket, contact Ms. Brenda
Edwards at (202) 586–2945 or by email:
Brenda.Edwards@ee.doe.gov.
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SUMMARY:
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Mr. Ron Majette, U.S. Department of
Energy, Office of Energy Efficiency
and Renewable Energy, Building
Technologies Office, EE–5B, 1000
Independence Avenue SW.,
Washington, DC 20585–0121.
Telephone: (202) 586–7935. Email:
Ronald.Majette@ee.doe.gov.
Mr. Eric Stas, U.S. Department of
Energy, Office of the General Counsel,
GC–71, 1000 Independence Avenue
SW., Washington, DC 20585–0121.
Telephone: (202) 586–9507. Email:
Eric.Stas@hq.doe.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Summary of the Final Rule
A. Benefits and Costs to Consumers
B. Impact on Manufacturers
C. National Benefits and Costs
D. Conclusion
II. Introduction
A. Authority
B. Background
1. Current Standards
2. History of Standards Rulemaking for
Residential Furnace Fans
III. General Discussion
A. Test Procedures
B. Product Classes and Scope of Coverage
C. Technological Feasibility
1. General
2. Maximum Technologically Feasible
Levels
D. Energy Savings
1. Determination of Savings
2. Significance of Savings
E. Economic Justification
1. Specific Criteria
a. Economic Impact on Manufacturers and
Commercial Customers
b. Savings in Operating Costs Compared To
Increase in Price (Life-Cycle Costs)
c. Energy Savings
d. Lessening of Utility or Performance of
Equipment
e. Impact of Any Lessening of Competition
f. Need of the Nation To Conserve Energy
g. Other Factors
2. Rebuttable Presumption
IV. Methodology and Discussion
A. Market and Technology Assessment
1. Definition and Scope of Coverage
2. Product Classes
3. Technology Options
a. Fan Housing and Airflow Path Design
Improvements
b. Inverter Controls for PSC Motors
c. High-Efficiency Motors
d. Multi-Stage or Modulating Heating
Controls
e. Backward-Inclined Impellers
B. Screening Analysis
1. Screened-Out Technologies
2. Remaining Technologies
a. High-Efficiency Motors
b. Backward-Inclined Impellers
C. Engineering Analysis
1. Efficiency Levels
a. Baseline
b. Percent Reduction in FER
2. Manufacturer Production Cost (MPC)
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a. Production Volume Impacts on MPC
b. Inverter-Driven PSC Costs
c. Furnace Fan Motor MPC
d. Motor Control Costs
e. Backward-Inclined Impeller MPC
f. Other Components
D. Markups Analysis
E. Energy Use Analysis
F. Life-Cycle Cost and Payback Period
Analysis
1. Installed Cost
2. Operating Costs
3. Furnace Fan Lifetime
4. Discount Rates
5. Compliance Date
6. Base-Case Efficiency Distribution
7. Payback Period
G. Shipments Analysis
H. National Impact Analysis
1. National Energy Savings Analysis
2. Net Present Value Analysis
I. Consumer Subgroup Analysis
J. Manufacturer Impact Analysis
1. Overview
2. Government Regulatory Impact Model
a. Government Regulatory Impact Model
Key Inputs
b. Government Regulatory Impact Model
Scenarios
3. Discussion of Comments
a. Conversion Costs
b. Cumulative Regulatory Burden
c. Scope of MIA Coverage
d. Markups Analysis
e. Employment Impacts
f. Consumer Utility
g. Small Businesses
K. Emissions Analysis
L. Monetizing Carbon Dioxide and Other
Emissions Impacts
1. Social Cost of Carbon
a. Monetizing Carbon Dioxide Emissions
b. Development of Social Cost of Carbon
Values
c. Current Approach and Key Assumptions
M. Utility Impact Analysis
N. Employment Impact Analysis
O. Comments on Proposed Standards
V. Analytical Results and Conclusions
A. Trial Standard Levels
B. Economic Justification and Energy
Savings
1. Economic Impacts on Consumers
a. Life-Cycle Cost and Payback Period
b. Consumer Subgroup Analysis
c. Rebuttable Presumption Payback
2. Economic Impact on Manufacturers
a. Industry Cash-Flow Analysis Results
b. Impacts on Employment
c. Impacts on Manufacturing Capacity
d. Impacts on Subgroups of Manufacturers
e. Cumulative Regulatory Burden
3. National Impact Analysis
a. Significance of Energy Savings
b. Net Present Value of Consumer Costs
and Benefits
c. Indirect Impacts on Employment
4. Impact on Product Utility or
Performance
5. Impact of Any Lessening of Competition
6. Need of the Nation To Conserve Energy
7. Other Factors
C. Conclusions
1. Benefits and Burdens of Trial Standard
Levels Considered for Residential
Furnace Fans
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2. Summary of Benefits and Costs
(Annualized) of Today’s Standards
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Orders 12866
and 13563
B. Review Under the Regulatory Flexibility
Act
C. Review Under the Paperwork Reduction
Act
D. Review Under the National
Environmental Policy Act of 1969
E. Review Under Executive Order 13132
F. Review Under Executive Order 12988
G. Review Under the Unfunded Mandates
Reform Act of 1995
H. Review Under the Treasury and General
Government Appropriations Act, 1999
I. Review Under Executive Order 12630
J. Review Under the Treasury and General
Government Appropriations Act, 2001
K. Review Under Executive Order 13211
L. Review Under the Information Quality
Bulletin for Peer Review
M. Congressional Notification
VII. Approval of the Office of the Secretary
I. Summary of the Final Rule
Title III, Part B of the Energy Policy
and Conservation Act of 1975 (EPCA or
the Act), Public Law 94–163 (42 U.S.C.
6291–6309, as codified), established the
Energy Conservation Program for
Consumer Products Other Than
Automobiles. Pursuant to EPCA, any
new or amended energy conservation
standard that DOE prescribes for certain
products, such as furnace fans, must be
designed to achieve the maximum
improvement in energy efficiency that is
38131
technologically feasible and
economically justified. (42 U.S.C.
6295(o)(2)(A)). Furthermore, the new or
amended standard must result in a
significant conservation of energy. (42
U.S.C. 6295(o)(3)(B)). In accordance
with these and other statutory
provisions discussed in this notice, DOE
proposes amended energy conservation
standards for furnace fans. The
proposed standards shall have a fan
energy rating (FER) value that meets or
is less than the values shown in Table
I.1. These standards would apply to all
products listed in Table I.1 and
manufactured in, or imported into, the
United States on or after manufactured
on and after July 3, 2019.
TABLE I.1.—ENERGY CONSERVATION STANDARDS FOR COVERED RESIDENTIAL FURNACE FANS
Product class
FER*
(watts/cfm)
Percent
increase over
baseline
(percent)
Non-Weatherized, Non-Condensing Gas Furnace Fan (NWG–NC) ...................................................
Non-Weatherized, Condensing Gas Furnace Fan (NWG–C) .............................................................
Weatherized Non-Condensing Gas Furnace Fan (WG–NC) ..............................................................
Non-Weatherized, Non-Condensing Oil Furnace Fan (NWO–NC) .....................................................
Non-Weatherized Electric Furnace/Modular Blower Fan (NWEF/NWMB) .........................................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan (MH–NWG–NC) ....................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan (MH–NWG–C) ...............................
Mobile Home Electric Furnace/Modular Blower Fan (MH–EF/MB) ....................................................
Mobile Home Non-Weatherized Oil Furnace Fan (MH–NWO) ...........................................................
Mobile Home Weatherized Gas Furnace Fan (MH–WG) ...................................................................
FER = 0.044 x QMax + 182
FER = 0.044 x QMax + 195
FER = 0.044 x QMax + 199
FER = 0.071 x QMax + 382
FER = 0.044 x QMax + 165
FER = 0.071 x QMax + 222
FER = 0.071 x QMax + 240
FER = 0.044 x QMax + 101
Reserved ...........................
Reserved ...........................
46
46
46
12
46
12
12
46
........................
........................
* QMax is the airflow, in cfm, at the maximum airflow-control setting measured using the final DOE test procedure at 10 CFR part 430, subpart
B, appendix AA.
A. Benefits and Costs to Consumers
Table I.2 presents DOE’s evaluation of
the economic impacts of today’s
standards on consumers of residential
furnace fans, as measured by the average
life-cycle cost (LCC) savings and the
median payback period (PBP). The
average LCC savings are positive for all
product classes.
TABLE I.2—IMPACTS OF ENERGY CONSERVATION STANDARDS ON CONSUMERS OF RESIDENTIAL FURNACE FANS
Average LCC
savings
(2013$)
Product class
Non-Weatherized, Non-Condensing Gas Furnace Fan ..........................................................................................
Non-weatherized, Condensing Gas Furnace Fan ...................................................................................................
Weatherized Non-Condensing Gas Furnace Fan ...................................................................................................
Non-Weatherized, Non-Condensing Oil Furnace Fan ............................................................................................
Non-weatherized Electric Furnace/Modular Blower Fan .........................................................................................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan ....................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ...........................................................................
Mobile Home Electric Furnace/Modular Blower Fan ...............................................................................................
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B. Impact on Manufacturers
The industry net present value (INPV)
is the sum of the discounted cash flows
to the industry from the base year
through the end of the analysis period
(2014 to 2048). Using a real discount
rate of 7.8 percent, DOE estimates that
the INPV for manufacturers of
residential furnace fans is $349.6
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million.1 Under today’s standards, DOE
expects that manufacturers may lose up
to 16.9 percent of their INPV, which is
approximately $59.0 million. Total
conversion costs incurred by industry
prior to the compliance date are
expected to reach $40.6 million.
1 DOE calculated a present value in 2014; all
monetary values in this document are expressed in
2013 dollars unless explicitly stated otherwise.
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Median payback period
(years)
$506
$341
$447
$46
$204
$36
$35
$85
5.4
5.8
4.4
1.7
3.2
2.7
2.3
4.1
C. National Benefits and Costs 2
DOE’s analyses indicate that today’s
standards would save a significant
amount of energy. The lifetime energy
savings for residential furnace fans
purchased in the 30-year period that
begins in the year of compliance with
the standards (2019–2048) amount to
2 All monetary values in this section are
expressed in 2013$ and are discounted to 2014.
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3.99 quadrillion Btu (quads 3). The
estimated annual energy savings in 2030
(0.07 quads) are equivalent to 0.3
percent of total U.S. residential energy
use in 2012.
The cumulative net present value
(NPV) of total consumer costs and
savings of today’s standards for
residential furnace fans ranges from
$10,024 million (at a 7-percent discount
rate) to $28,810 million (at a 3-percent
discount rate). This NPV expresses the
estimated total value of future
operating-cost savings minus the
estimated increased product costs for
residential furnace fans purchased in
2019–2048.
In addition, today’s standards are
expected to have significant
environmental benefits. The energy
savings would result in cumulative
emission reductions of approximately
180.6 million metric tons (Mt) 4 of
carbon dioxide (CO2), 695.0 thousand
tons of methane (CH4), 235.7 thousand
tons of sulfur dioxide (SO2), 84.0
thousand tons of nitrogen oxides (NOX),
6.2 thousand tons of nitrous oxide
(N2O), and 0.4 tons of mercury (Hg).5
The cumulative reduction in CO2
emissions through 2030 amounts to 34
million Mt.
The value of the CO2 reductions is
calculated using a range of values per
metric ton of CO2 (otherwise known as
the Social Cost of Carbon, or SCC)
developed by a recent Federal
interagency process.6 The derivation of
the SCC values is discussed in section
IV.L. Using discount rates appropriate
for each set of SCC values, DOE
estimates that the net present monetary
value of the CO2 emissions reductions is
between 1,134 million to 16,799
million. DOE also estimates that the net
present monetary value of the NOX
emissions reductions is $53.1 million at
a 7-percent discount rate, and $110.8
million at a 3-percent discount rate.7
Table I.3 summarizes the national
economic costs and benefits expected to
result from today’s standards for
residential furnace fans.
TABLE I.3—SUMMARY OF NATIONAL ECONOMIC BENEFITS AND COSTS OF RESIDENTIAL FURNACE FANS ENERGY
CONSERVATION STANDARDS*
Present value
million 2013 $
Category
Discount rate
(percent)
Benefits
Consumer Operating Cost Savings .......................................................................................................................
CO2 Reduction Monetized Value ($12.0/t case)** ................................................................................................
CO2 Reduction Monetized Value ($40.5/t case)** ................................................................................................
CO2 Reduction Monetized Value ($62.4/t case)** ................................................................................................
CO2 Reduction Monetized Value ($119/t case)** .................................................................................................
NOX Reduction Monetized Value (at $2,684/ton)** ..............................................................................................
Total Benefits† .......................................................................................................................................................
13,409
34,999
1,134
5,432
8,694
16,799
53
111
18,894
40,542
7
3
5
3
2.5
3
7
3
7
3
Costs
Consumer Incremental Installed Costs .................................................................................................................
3,385
6,189
7
3
15,509
34,353
7
3
Net Benefits
Including CO2 and NOX† Reduction Monetized Value .........................................................................................
* This table presents the costs and benefits associated with residential furnace fans shipped in 2019–2048. These results include benefits to
consumers which accrue after 2048 from the products purchased in 2019–2048. The results account for the incremental variable and fixed costs
incurred by manufacturers due to the standard, some of which may be incurred in preparation for the rule.
** The CO2 values represent global monetized values of the SCC, in 2013$, in 2015 under several scenarios of the updated SCC values. The
first three cases use the averages of SCC distributions calculated using 5%, 3%, and 2.5% discount rates, respectively. The fourth case represents the 95th percentile of the SCC distribution calculated using a 3% discount rate. The SCC time series used by DOE incorporate an escalation factor. The value for NOX is the average of the low and high values used in DOE’s analysis.
† Total Benefits for both the 3% and 7% cases are derived using the series corresponding to average SCC with 3-percent discount rate.
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The benefits and costs of today’s
standards, for products sold in 2019–
2048, can also be expressed in terms of
annualized values. The annualized
monetary values are the sum of: (1) The
annualized national economic value of
the benefits from operating the product
that meets the new or amended standard
(consisting primarily of operating cost
savings from using less energy, minus
increases in equipment purchase and
installation costs, which is another way
of representing consumer NPV), and (2)
the annualized monetary value of the
benefits of emission reductions,
including CO2 emission reductions.8
3 A quad is equal to 1015 British thermal units
(Btu).
4 A metric ton is equivalent to 1.1 short tons.
Results for NOX and Hg are presented in short tons.
5 DOE calculated emissions reductions relative to
the Annual Energy Outlook 2013 (AEO 2013)
Reference case, which generally represents current
legislation and environmental regulations for which
implementing regulations were available as of
December 31, 2012.
6 Technical Update of the Social Cost of Carbon
for Regulatory Impact Analysis Under Executive
Order 12866, Interagency Working Group on Social
Cost of Carbon, United States Government (May
2013; revised November 2013) (Available at:
https://www.whitehouse.gov/sites/default/files/omb/
assets/inforeg/technical-update-social-cost-ofcarbon-for-regulator-impact-analysis.pdf).
7 DOE is investigating valuation of avoided Hg
and SO2 emissions.
8 DOE used a two-step calculation process to
convert the time-series of costs and benefits into
annualized values. First, DOE calculated a present
value in 2014, the year used for discounting the
NPV of total consumer costs and savings, for the
time-series of costs and benefits using discount
rates of three and seven percent for all costs and
benefits except for the value of CO2 reductions. For
the latter, DOE used a range of discount rates, as
shown in Table I.4. From the present value, DOE
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Although adding the value of
consumer savings to the values of
emission reductions provides a valuable
perspective, two issues should be
considered. First, the national operating
cost savings are domestic U.S. consumer
monetary savings that occur as a result
of market transactions, whereas the
value of CO2 reductions is based on a
global value. Second, the assessments of
operating cost savings and CO2 savings
are performed with different methods
that use different time frames for
analysis. The national operating cost
savings is measured for the lifetime of
residential furnace fans shipped in
2019–2048. The SCC values, on the
other hand, reflect the present value of
all future climate-related impacts
resulting from the emission of one
metric ton of carbon dioxide in each
year. These impacts continue well
beyond 2100.
Estimates of annualized benefits and
costs of today’s standards are shown in
Table I.4. The results under the primary
estimate are as follows. Using a 7percent discount rate for benefits and
costs other than CO2 reduction (for
which DOE used a 3-percent discount
rate along with the SCC series that has
a value of $40.5/t in 2015), the cost of
the residential furnace fans standards in
today’s final rule is $358 million per
year in increased equipment costs,
while the benefits are $1416 million per
38133
year in reduced equipment operating
costs, $312 million in CO2 reductions,
and $5.61 million in reduced NOX
emissions. In this case, the net benefit
amounts to $1,376 million per year.
Using a 3-percent discount rate for all
benefits and costs and the SCC series
that has a value of $40.5/t in 2015, the
cost of the residential furnace fans
standards in today’s rule is $355 million
per year in increased equipment costs,
while the benefits are $2010 million per
year in reduced operating costs, $312
million in CO2 reductions, and $6.36
million in reduced NOX emissions. In
this case, the net benefit amounts to
$1,973 million per year.
TABLE I.4—ANNUALIZED BENEFITS AND COSTS OF STANDARDS FOR RESIDENTIAL FURNACE FANS
Primary
estimate *
Discount rate
Low net benefits
estimate *
High net benefits
estimate *
million 2013$/year
Benefits
Consumer Operating Cost
Savings.
CO2 Reduction (at $12.0/t
case) **.
CO2 Reduction (at $40.5/t
case) **.
CO2 Reduction (at $62.4/t
case) **.
CO2 Reduction (at $119/t
case) **.
NOX Reduction (at $2,684/
ton) **.
Total Benefits † ..................
7% .....................................
3% .....................................
5% .....................................
1416 ..................................
2010 ..................................
90 ......................................
1167 ..................................
1626 ..................................
77 ......................................
1718
2467
108
3% .....................................
312 ....................................
268 ....................................
377
2.5% ..................................
459 ....................................
393 ....................................
555
3% .....................................
965 ....................................
828 ....................................
1166
7%
3%
7%
7%
3%
3%
5.61 ...................................
6.36 ...................................
1,512 to 2,387 ...................
1,734 .................................
2,106 to 2,981 ...................
2,328 .................................
4.80 ...................................
5.35 ...................................
1,249 to 2,000 ...................
1,439 .................................
1,708 to 2,459 ...................
1,899 .................................
6.82
7.86
1,833 to 2,891
2,102
2,583 to 3,641
2,852
314 ....................................
304 ....................................
410
419
935 to 1,685 ......................
1,125 .................................
1,404 to 2,155 ...................
1,595 .................................
1,423 to 2,481
1,692
2,164 to 3,222
2,433
.....................................
.....................................
plus CO2 range ...........
.....................................
plus CO2 range ...........
.....................................
Costs
Consumer Incremental
Product Costs.
7% .....................................
3% .....................................
358 ....................................
355 ....................................
Net Benefits
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Total † .........................
7%
7%
3%
3%
plus CO2 range ...........
.....................................
plus CO2 range ...........
.....................................
1,154
1,376
1,750
1,973
to 2,029 ...................
.................................
to 2,625 ...................
.................................
* This table presents the annualized costs and benefits associated with residential furnace fans shipped in 2019–2048. These results include
benefits to consumers which accrue after 2048 from the products purchased from 2019–2048. The results account for the incremental, variable,
and fixed costs incurred by manufacturers due to the standard, some of which may be incurred in preparation for the rule. The Primary, Low
Benefits, and High Benefits Estimates utilize projections of energy prices and housing starts from the AEO 2013 Reference case, Low Estimate,
and High Estimate, respectively. In addition, incremental product costs reflect a flat rate for projected product price trends in the Primary Estimate, a slightly increasing rate for projected product price trends in the Low Benefits Estimate, and a slightly declining rate for projected product
price trends in the High Benefits Estimate. The methods used to derive projected price trends are explained in section IV.F.
** The CO2 values represent global monetized values of the SCC, in 2013$, in 2015 under several scenarios of the updated SCC values. The
first three cases use the averages of SCC distributions calculated using 5%, 3%, and 2.5% discount rates, respectively. The fourth case represents the 95th percentile of the SCC distribution calculated using a 3% discount rate. The SCC time series used by DOE incorporate an escalation factor. The value for NOX is the average of the low and high values used in DOE’s analysis.
† Total Benefits for both the 3% and 7% cases are derived using the series corresponding to the average SCC with a 3% discount rate. In the
rows labeled ‘‘7% plus CO2 range’’ and ‘‘3% plus CO2 range,’’ the operating cost and NOX benefits are calculated using the labeled discount
rate, and those values are added to the full range of CO2 values.
then calculated the fixed annual payment over a 30year period (2019 through 2048) that yields the
same present value. The fixed annual payment is
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the annualized value. Although DOE calculated
annualized values, this does not imply that the
time-series of cost and benefits from which the
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annualized values were determined is a steady
stream of payments.
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D. Conclusion
Based on the analyses culminating in
this final rule, DOE found the benefits
to the nation of the standards (energy
savings, consumer LCC savings, positive
NPV of consumer benefit, and emission
reductions) outweigh the burdens (loss
of INPV and LCC increases for some
users of these products). DOE has
concluded that the standards in today’s
final rule represent the maximum
improvement in energy efficiency that is
technologically feasible and
economically justified, and would result
in significant conservation of energy.
II. Introduction
The following section briefly
discusses the statutory authority
underlying today’s final rule, as well as
some of the relevant historical
background related to the establishment
of standards for residential furnace fans.
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A. Authority
Title III, Part B 9 of the Energy Policy
and Conservation Act of 1975 (EPCA or
the Act), Public Law 94–163 (42 U.S.C.
6291–6309, as codified) established the
Energy Conservation Program for
Consumer Products Other Than
Automobiles, a program covering most
major household appliances
(collectively referred to as ‘‘covered
products’’),10 which includes the types
of residential furnace fans that are the
subject of this rulemaking. (42 U.S.C.
6295(f)(4)(D))
Pursuant to EPCA, DOE’s energy
conservation program for covered
products consists of essentially of four
parts: (1) Testing; (2) labeling; (3) the
establishment of Federal energy
conservation standards; and (4)
certification and enforcement
procedures. The Federal Trade
Commission (FTC) is primarily
responsible for labeling, and DOE
implements the remainder of the
program. Subject to certain criteria and
conditions, DOE is required by EPCA to
consider and establish energy
conservation standards for ‘‘electricity
used for purposes of circulating air
through duct work’’ (which DOE has
referred to in shorthand as residential
‘‘furnace fans’’). (42 U.S.C. 6295(f)(4)(D))
DOE is also required by EPCA to
develop test procedures to measure the
energy efficiency, energy use, or
estimated annual operating cost of each
covered product prior to the adoption of
9 For editorial reasons, upon codification in the
U.S. Code, Part B was redesignated Part A.
10 All references to EPCA in this document refer
to the statute as amended through the American
Energy Manufacturing Technical Corrections Act
(AEMTCA), Public Law 112–210 (Dec. 18, 2012).
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an energy conservation standard. (42
U.S.C. 6295(o)(A)(3) and (r))
Manufacturers of covered products must
use the prescribed DOE test procedure
as the basis for certifying to DOE that
their products comply with the
applicable energy conservation
standards adopted under EPCA and
when making representations to the
public regarding the energy use or
efficiency of those products. (42 U.S.C.
6293(c) and 6295(s)) Similarly, DOE
must use these test procedures to
determine whether the products comply
with standards adopted pursuant to
EPCA. (42 U.S.C. 6295(s)) The DOE test
procedures for residential furnace fans
currently appear at title 10 of the Code
of Federal Regulations (CFR) part 430,
subpart B, appendix AA.
DOE must follow specific statutory
criteria for prescribing new or amended
standards for covered products,
including furnace fans. As indicated
above, any standard for a covered
product must be designed to achieve the
maximum improvement in energy
efficiency that is technologically
feasible and economically justified. (42
U.S.C. 6295(o)(2)(A) and (3)(B))
Furthermore, DOE may not adopt any
standard that would not result in the
significant conservation of energy. (42
U.S.C. 6295(o)(3)) Moreover, DOE may
not prescribe a standard: (1) For certain
products, including residential furnace
fans, if no test procedure has been
established for the product, or (2) if DOE
determines by rule that the standard is
not technologically feasible or
economically justified. (42 U.S.C.
6295(o)(3)(A)–(B)) In deciding whether a
standard is economically justified, DOE
must determine whether the benefits of
the standard exceed its burdens. (42
U.S.C. 6295(o)(2)(B)(i)) DOE must make
this determination after receiving
comments on the proposed standard,
and by considering, to the greatest
extent practicable, the following seven
factors:
(1) The economic impact of the standard
on manufacturers and consumers of the
products subject to the standard;
(2) The savings in operating costs
throughout the estimated average life of the
covered products in the type (or class)
compared to any increase in the price, initial
charges, or maintenance expenses for the
covered products that are likely to result
from the standard;
(3) The total projected amount of energy (or
as applicable, water) savings likely to result
directly from the standard;
(4) Any lessening of the utility or the
performance of the covered products likely to
result from the standard;
(5) The impact of any lessening of
competition, as determined in writing by the
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Attorney General, that is likely to result from
the standard;
(6) The need for national energy and water
conservation; and
(7) Other factors the Secretary of Energy
(Secretary) considers relevant.
(42 U.S.C. 6295(o)(2)(B)(i)(I)–(VII))
EPCA, as codified, also contains what
is known as an ‘‘anti-backsliding’’
provision, which prevents the Secretary
from prescribing any standard that
either increases the maximum allowable
energy use or decreases the minimum
required energy efficiency of a covered
product. (42 U.S.C. 6295(o)(1)) Also, the
Secretary may not prescribe an amended
or new standard if interested persons
have established by a preponderance of
the evidence that the standard is likely
to result in the unavailability in the
United States of any covered product
type (or class) of performance
characteristics (including reliability),
features, sizes, capacities, and volumes
that are substantially the same as those
generally available in the United States.
(42 U.S.C. 6295(o)(4))
Further, EPCA, as codified,
establishes a rebuttable presumption
that a standard is economically justified
if the Secretary finds that the additional
cost to the consumer of purchasing a
product complying with an energy
conservation standard level will be less
than three times the value of the energy
savings during the first year that the
consumer will receive as a result of the
standard, as calculated under the
applicable test procedure. (See 42 U.S.C.
6295(o)(2)(B)(iii))
Additionally, under 42 U.S.C.
6295(q)(1), the statute specifies
requirements when promulgating an
energy conservation standard for a
covered product that has two or more
subcategories. DOE must specify a
different standard level for a type of
class of covered product that has the
same function or intended use, if DOE
determines that products within such
group: (A) Consume a different kind of
energy from that consumed by other
covered products within such type (or
class); or (B) have a capacity or other
performance-related feature which other
products within such type (or class) do
not have and such feature justifies a
higher or lower standard. (42 U.S.C.
6295(q)(1)) In determining whether a
performance-related feature justifies a
different standard for a group of
products, DOE must consider such
factors as the utility to the consumer of
such a feature and other factors DOE
deems appropriate. Id. Any rule
prescribing such a standard must
include an explanation of the basis on
which such higher or lower level was
established. (42 U.S.C. 6295(q)(2))
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Federal energy conservation
requirements generally supersede State
laws or regulations concerning energy
conservation testing, labeling, and
standards. (42 U.S.C. 6297(a)–(c)) DOE
may, however, grant waivers of Federal
preemption for particular State laws or
regulations, in accordance with the
procedures and other provisions set
forth under 42 U.S.C. 6297(d)).
Finally, pursuant to the amendments
contained in the Energy Independence
and Security Act of 2007 (EISA 2007),
Public Law 110–140, any final rule for
new or amended energy conservation
standards promulgated after July 1,
2010, is required to address standby
mode and off mode energy use. (42
U.S.C. 6295(gg)(3)) Specifically, when
DOE adopts a standard for a covered
product after that date, it must, if
justified by the criteria for adoption of
standards under EPCA (42 U.S.C.
6295(o)), incorporate standby mode and
off mode energy use into a single
standard, or, if that is not feasible, adopt
a separate standard for such energy use
for that product. (42 U.S.C.
6295(gg)(3)(A)–(B)) The furnace fan
energy rating metric does not account
for the electrical energy consumption in
standby mode and off mode, because
energy consumption in those modes is
being fully accounted for in the DOE
energy conservation standards for
residential furnaces and residential
central air conditioners (CAC) and heat
pumps (HP). Manufacturers will be
required to use the new metrics and
methods adopted in those rulemakings
for the purposes of certifying to DOE
that their products comply with the
applicable energy conservation
standards adopted pursuant to EPCA
and for making representations about
the efficiency of those products. (42
U.S.C. 6293(c); 42 U.S.C. 6295(s))
B. Background
1. Current Standards
Currently, no Federal energy
conservation standards apply to
residential furnace fans.
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2. History of Standards Rulemaking for
Residential Furnace Fans
Pursuant to 42 U.S.C. 6295(f)(4)(D),
DOE must consider and prescribe new
energy conservation standards or energy
use standards for electricity used for
purposes of circulating air through duct
work. DOE has interpreted this statutory
language to allow regulation of the
electricity use of any electricallypowered device applied to residential
central heating, ventilation, and airconditioning (HVAC) systems for the
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purpose of circulating air through duct
work.
DOE initiated the current rulemaking
by issuing an analytical Framework
Document, ‘‘Rulemaking Framework for
Furnace Fans’’ (June 1, 2010). DOE then
published the Notice of Public Meeting
and Availability of the Framework
Document for furnace fans in the
Federal Register on June 3, 2010. 75 FR
31323. See https://
www1.eere.energy.gov/buildings/
appliance_standards/rulemaking.aspx/
ruleid/41. The Framework Document
explained the issues, analyses, and
process that DOE anticipated using to
develop energy conservation standards
for residential furnace fans. DOE held a
public meeting on June 18, 2010 to
solicit comments from interested parties
regarding DOE’s analytical approach.
DOE originally scheduled the comment
period on the Framework Document to
close on July 6, 2010, but due to the
large number and broad scope of
questions and issues raised, DOE
subsequently published a notice in the
Federal Register reopening the
comment period from July 15, 2010
until July 27, 2010, to allow additional
time for interested parties to submit
comments. 75 FR 41102 (July 15, 2010).
As a concurrent effort to the
residential furnace fan energy
conservation standard rulemaking, DOE
also initiated a test procedure
rulemaking for residential furnace fans.
On May 15, 2012, DOE published a
notice of proposed rulemaking (NOPR)
for the test procedure in the Federal
Register. 77 FR 28674. In that NOPR,
DOE proposed to establish methods to
measure the performance of covered
furnace fans and to obtain a value for
the proposed metric, referred to as the
‘‘fan efficiency rating’’ (FER).11 DOE
held the test procedure NOPR public
meeting on June 15, 2012, and the
comment period closed on July 30,
2012. After receiving comments on the
NOPR alleging significant manufacturer
burden associated with the proposed
test procedure, DOE determined that an
alternative test method should be
developed. DOE published in the
Federal Register an SNOPR on April 2,
2013, which contained its revised test
procedure proposal and an explanation
of the changes intended to reduce
burden. 78 FR 19606. DOE proposed to
adopt a modified version of the
alternative test method recommended
by the Air-Conditioning, Heating, and
11 In the May 15, 2012 NOPR for the test
procedure, DOE referred to FER as ‘‘fan efficiency
rating.’’ However, in the April 2, 2013 test
procedure SNOPR, DOE proposed to rename the
metric as ‘‘fan energy rating,’’ thereby keeping the
same abbreviation (FER).
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Refrigeration Institute (AHRI) and other
furnace fan manufacturers to rate the
electrical energy consumption of
furnace fans. DOE concluded that the
AHRI-proposed method provides a
framework for accurate and repeatable
determinations of FER that is
comparable to the test method
previously proposed by DOE, but at a
significantly reduced test burden. DOE
published in the Federal Register a final
rule on January 3, 2014, which
contained the final test procedure for
residential furnace fans. 79 FR 500.
To further develop the energy
conservation standards for residential
furnace fans, DOE gathered additional
information and performed a
preliminary technical analysis. This
process culminated in publication in the
Federal Register of a Notice of Public
Meeting and the Availability of the
Preliminary Technical Support
Document (TSD) on July 10, 2012. 77 FR
40530. DOE published a NOPR in the
Federal Register and made available an
accompanying NOPR TSD on October
25, 2013. 78 FR 64068. In that
document, DOE requested comment on
the following matters discussed in the
TSD: (1) Additional FER values; (2) the
methodology for accounting for the
relationship between FER and airflow
capacity; (3) the reasonableness of the
values that DOE used to characterize the
rebound effect with high-efficiency
residential furnace fans; (4) DOE’s
estimate of the base-case efficiency
distribution of residential furnace fans
in 2018; (5) the long-term market
penetration of higher-efficiency
residential furnace fans; (6) data
regarding manufacturer product costs
for furnace fan equipment and
components; (7) the effect of standards
on future furnace fan equipment
shipments; (8) whether there are
features or attributes of the more energyefficient furnace fans that manufacturers
would produce to meet the standards in
the proposed rule that might affect how
they would be used by consumers; (9)
data that would refine the analytical
timeline; (10) input on average
equipment lifetimes; (11) the new SCC
values used to determine the social
benefits of CO2 emissions reductions
over the rulemaking analysis period;
and (12) input on the cumulative
regulatory burden. Id. DOE also invited
written comments on these subjects, as
well as any other relevant issues. A PDF
copy of the NOPR TSD is available at
https://www.regulations.gov/
#!documentDetail;D=EERE-2010-BTSTD-0011-0068.
The NOPR TSD provided an overview
of the activities DOE undertook in
developing proposed energy
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conservation standards for residential
furnace fans, and discussed the
comments DOE received in response to
the Preliminary Analysis. It also
described the analytical methodology
that DOE used and each analysis DOE
had performed up to that point. These
analyses were as follows:
• A market and technology
assessment addressed the scope of this
rulemaking, identified the potential
product classes of residential furnace
fans, characterized the markets for these
products, and reviewed techniques and
approaches for improving their
efficiency;
• A screening analysis reviewed
technology options to improve the
efficiency of furnace fans, and weighed
these options against DOE’s four
prescribed screening criteria;
• An engineering analysis developed
relationships that show the
manufacturer’s cost of achieving
increased efficiency;
• A markups analysis developed
distribution channel markups that relate
the manufacturer production cost (MPC)
to the cost to the consumer;
• An energy use analysis estimated
the annual energy use of furnace fans at
various potential standard levels;
• A life-cycle cost (LCC) analysis
calculated, at the consumer level, the
discounted savings in operating costs
throughout the estimated average life of
the product, compared to any increase
in installed costs likely to result directly
from the adoption of a given standard;
• A payback period (PBP) analysis
estimated the amount of time it would
take consumers to recover the higher
expense of purchasing more-energyefficient products through lower
operating costs;
• A shipments analysis estimated
shipments of residential furnace fans
over the time period examined in the
analysis (30 years), which were used in
performing the national impact analysis;
• A national impact analysis assessed
the aggregate impacts at the national
level of potential energy conservation
standards for residential furnace fans, as
measured by the net present value of
total consumer economic impacts and
national energy savings;
• A manufacturer impact analysis
estimated the financial impact of new
energy conservation standards on
manufacturers and calculated impacts
on competition, employment, and
manufacturing capacity;
• A consumer subgroup analysis
evaluated variations in customer
characteristics that might cause a
standard to affect particular consumer
sub-populations (such as low-income
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households) differently than the overall
population;
• An emissions analysis assessed the
effects of the considered standards on
emissions of carbon dioxide (CO2),
sulfur dioxide (SO2) nitrogen oxides
(NOX), mercury (Hg), nitrous oxide
(N20), and methane (CH4);
• An emissions monetization
estimated the economic value of
reductions in CO2 and NOX emissions
from the considered standards;
• A utility impact analysis estimated
selected effects of the considered
standards on electric utilities;
• An employment impact analysis
assessed the impacts of the considered
standards on national employment; and
• A regulatory impact analysis (RIA)
evaluated alternatives to amended
energy conservation standards in order
to assess whether such alternatives
could achieve substantially the same
regulatory goal at a lower cost.
The NOPR public meeting took place
on December 3, 2013. At this meeting,
DOE presented the methodologies and
results of the analyses set forth in the
NOPR TSD. The numerous comments
received since publication of the
October 2013 NOPR, including those
received at the NOPR public meeting,
have contributed to DOE’s resolution of
the issues raised by interested parties.
The submitted comments include a
comment from the American Council for
an Energy-Efficiency Economy (ACEEE);
a joint comment from the American
Fuel and Petrochemical Manufacturers
(AFPM), the U.S. Chamber of Commerce
(the Chamber), the Council of Industrial
Boiler Owners (CIBO), the American
Forest and Paper Association (AF&PA),
and the American Petroleum Institute
(API); a comment from the American
Gas Association (AGA); a comment from
the Air-Conditioning, Heating, and
Refrigeration Institute (AHRI); a
comment from the American Public Gas
Association (APGA); a joint comment
from the Appliance Standards
Awareness Project (ASAP), Alliance to
Save Energy (ASE), National Consumer
Law Center (NCLC) and the Natural
Resources Defense Council (NRDC); a
second joint comment from California
Investor-Owned Utilities (CA IOUs)
including Pacific Gas and Electric
Company (PG&E), Southern California
Edison (SCE), Southern California Gas
Company (SCGC), and San Diego Gas
and Electric (SDGE); a comment from
the Cato Institute; a comment from
China WTO (WTO); a comment from
Earthjustice; a comment from Edison
Electric Institute (EEI); a comment from
the George Washington University
Regulatory Studies Center; a comment
from Goodman Global, Inc. (Goodman);
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a comment from Heating, AirConditioning and Refrigeration
Distributers International (HARDI); a
comment from Johnson Controls; a
comment from Laclede Gas Company
(Laclede); a comment from a comment
from Lennox International, Inc.
(Lennox); a comment from the Mercatus
Center at George Mason University; a
comment from Morrison Products, Inc.
(Morrison); a comment from Mortex
Product, Inc. (Mortex); a comment from
the National Association of
Manufacturers (NAM); a joint comment
from the Northwest Energy Efficiency
Alliance (NEEA) and the Northwest
Power and Conservation Council
(NPCC); a comment from the Northeast
Energy Efficiency Partnerships (NEEP);
a comment from Rheem Manufacturing
Company (Rheem); a comment from
Southern Company; a comment from
Ingersoll Rand; and a comment from
Unico, Incorporated. Comments made
during the public meeting by those not
already listed include Nidec Motor
Corporation (Nidec) and the motor
manufacturer Regal Beloit. This final
rule summarizes and responds to the
issues raised in these comments. A
parenthetical reference at the end of a
quotation or paraphrase provides the
location of the item in the public record.
III. General Discussion
A. Test Procedures
DOE published the furnace fan test
procedure final rule in the Federal
Register on January 3, 2014. 79 FR 499.
DOE’s test procedure for furnace fans
(hereinafter referred to as ‘‘the test
procedure’’) is codified in appendix AA
of subpart B of part 430 of the code of
federal regulations (CFR).The test
procedure is applicable to circulation
fans used in weatherized and nonweatherized gas furnaces, oil furnaces,
electric furnaces, and modular blowers.
The test procedure is not applicable to
any non-ducted products, such as
whole-house ventilation systems
without ductwork, central airconditioning (CAC) condensing unit
fans, room fans, and furnace draft
inducer fans.
DOE aligned the test procedure with
the DOE test procedure for furnaces by
incorporating by reference specific
provisions from an industry standard
that is also incorporated by reference in
the DOE test procedure for furnaces.
DOE’s test procedure for furnaces is
codified in appendix N of subpart B of
part 430 of the CFR. The DOE furnace
test procedure incorporates by reference
American National Standards Institute
(ANSI)/American Society of Heating,
Refrigerating and Air Conditioning
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Engineers (ASHRAE) 103–1993, Method
of Testing for Annual Fuel Utilization
Efficiency of Residential Central
Furnaces and Boilers (ASHRAE 103–
1993). The DOE furnace fan test
procedure incorporates by reference the
definitions, test setup and equipment,
and procedures for measuring steadystate combustion efficiency provisions
of the 2007 version of ASHRAE 103
(ASHRAE 103–2007). In addition to
these provisions, the test procedure
includes provisions for apparatuses and
procedures for measuring temperature
rise, external static pressure, and
furnace fan electrical input power. The
test procedure also incorporates by
reference provisions for measuring
temperature and external static pressure
from ANSI/ASHRAE 37–2009, Methods
of Testing for Rating Electrically Driven
Unitary Air-Conditioning and Heat
Pump Equipment (ASHRAE 37–2009).
There are no differences between the
2005 version (which is already
incorporated by reference in the CFR)
and the 2009 version of the ASHRAE 37
provisions incorporated by reference for
the furnace fan test procedure. The test
procedure also establishes calculations
to derive the rating metric, fan energy
rating (FER), for each furnace fan basic
model based on the results of testing per
the test method for furnace fans codified
consistent with the CFR definition for
‘‘mobile home furnace.’’ All provisions
and statements regarding mobile homes
and mobile home furnaces are
applicable to manufactured homes and
manufactured home furnaces.
in appendix AA of subpart B of part 430
of the CFR.
FER is the estimated annual electrical
energy consumption of a furnace fan
normalized by: (a) The estimated total
number of annual fan operating hours
(1,870); and (b) the airflow in the
maximum airflow-control setting. For
the purposes of the furnace fan test
procedure, the estimated annual
electrical energy consumption is the
sum of the furnace fan electrical input
power (in Watts), measured separately
for multiple airflow-control settings at
different external static pressures
(ESPs), multiplied by national average
operating hours associated with each
setting. These ESPs are determined by a
reference system, based on operation at
maximum airflow that represents
national average ductwork system
characteristics. Table III.1 includes the
reference system ESP values by
installation type that are specified by
the test procedure. In previous
rulemaking documents for the furnace
fan test procedure and energy
conservation standard rulemaking, DOE
used the term ‘‘manufactured home
furnace’’ to be synonymous with
‘‘mobile home furnace,’’ as defined in
the Code of Federal Regulation (CFR).
10 CFR 430.2. DOE will use the term
‘‘mobile home’’ hereinafter to be
TABLE III.1—REQUIRED REFERENCE
SYSTEM CRITERIA (I.E., ESP AT
MAXIMUM AIRFLOW) BY FURNACE
FAN INSTALLATION TYPE
ESP at
maximum
airflow
(in. wc)
Installation type
Units with an internal evaporator coil ............................
Units designed to be paired
with an evaporator coil ......
Units designed to be installed in a mobile home 12
0.50
0.65
0.30
The test procedure requires
measurements for the airflow-control
settings that correspond to fan operation
while performing the cooling function
(which DOE finds is predominantly
associated with the maximum airflowcontrol setting), heating function, and
constant-circulation function. Table III.2
describes the required airflow-control
settings by product type.
TABLE III.2—AIRFLOW-CONTROL SETTINGS AT WHICH MEASUREMENTS ARE REQUIRED FOR EACH PRODUCT TYPE
Product type
Airflow-control
setting 1
Airflow-control
setting 2
Airflow-control
setting 3
Single-stage Heating .............................
Multi-stage or Modulating Heating ........
Default constant-circulation .................
Default constant-circulation .................
Default heat .........................................
Default low heat ...................................
Absolute maximum.*
Absolute maximum.
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* For the purposes of the test procedure, ‘‘absolute maximum’’ airflow-control setting refers to the airflow-control setting that achieves the maximum attainable airflow at the operating conditions specified by the test procedure.
As shown in Table III.2, for products
with single-stage heating, the three
airflow-control settings to be tested are:
The default constant-circulation setting;
the default heating setting; and the
absolute maximum setting. For products
with multi-stage heating or modulating
heating, the airflow-control settings to
be tested are: The default constantcirculation setting; the default low
heating setting; and the absolute
maximum setting. The absolute lowest
airflow-control setting is used to
represent constant circulation if a
default constant-circulation setting is
not specified. DOE defines ‘‘default
airflow-control settings’’ as the airflow-
control settings for installed use
specified by the manufacturer in the
product literature shipped with the
product in which the furnace fan is
integrated. See Section 2.2 of Appendix
AA to Subpart B of 10 CFR part 430.
Manufacturers typically provide
detailed instructions for setting the
default heating airflow-control setting to
ensure that the product in which the
furnace fan is integrated operates safely.
In instances where a manufacturer
specifies multiple airflow-control
settings for a given function to account
for varying installation scenarios, the
highest airflow-control setting specified
for the given function shall be used for
the DOE test procedure. High heat and
reduced heat shall be considered
different functions for multi-stage
heating units. Manufacturer installation
guides also provide detailed
instructions regarding compatible
thermostats and how to wire them to
achieve the specified default settings.
The Watt measurements for
calculating FER are weighted using
designated annual operating hours for
each function (i.e., cooling, heating, and
constant circulation) that represent
national average operation. Table III.3
shows the estimated national average
operating hours for each function.
12 Mobile home external static pressure is much
lower because there is no return air ductwork in
mobile homes. Also, the United States Department
of Housing and Urban Development (HUD)
requirements for mobile homes stipulate that the
ductwork for cooling should be designed for 0.3 in.
water column (wc). 24 CFR 3280.715.
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TABLE III.3—ESTIMATED NATIONAL AVERAGE OPERATING HOUR VALUES FOR CALCULATING FER
Operating mode
Variable
Heating .........................................................................................................................................
Cooling .........................................................................................................................................
Constant Circulation ....................................................................................................................
HH
CH
CCH
Single-stage
(hours)
830
640
400
Multi-stage
or modulating
(hours)
830/HCR
640
400
input rate to the measured maximum
heat input rate.
The FER equation is:
comments that were not addressed in
the test procedure final rule document.
AHRI, Goodman, Morrison, Rheem,
Southern Company, Johnson Controls,
and Ingersoll Rand commented that
DOE’s schedule for finalizing the test
procedure did not provide interested
parties with sufficient time to evaluate
product performance in accordance
with the final test procedure in order to
develop and submit substantive
comments on the standards proposed in
the NOPR. (AHRI, No. 98 at p. 2, 3;
Goodman, No. 102 at pp. 7, 8; Morrison,
No. 108 at p. 3; Rheem, No. 83 at p. 1;
Southern Company, No. 85 at p. 2;
Johnson Controls, No. 95 at p. 3;
Ingersoll Rand, No. 43 at p. 33) Ingersoll
Rand added that the comments they
have submitted to date are based on the
proposed test procedure, not the final
test procedure. (Ingersoll Rand, No. 107
at pp. 2, 10) AGA and Allied Air agree
and recommend that DOE delay
promulgation of standards to give
interested parties and DOE more time to
conduct analyses using the final test
procedure. (AGA, No. 110 at pp. 3, 4;
Allied Air, Public Meeting Transcript,
No. 43 at p. 48) Goodman recommended
a delay of three months for this type of
product and testing. (Goodman, No. 102
at p. 3) Prior to publication of the test
procedure final rule, EEI expressed
support for DOE issuing a supplemental
notice of proposed rulemaking (SNOPR)
for the standard if changes were made
to the test procedure final rule that had
significant impacts on DOE’s analyses
results. (EEI, No. 87 at p. 3) APGA and
Southern Company also recommended
that DOE publish a standards SNOPR.
(APGA, No. 90 at p. 2; Southern
Company, No. 43 at p. 37)
DOE recognizes that interested parties
need sufficient time to collect and
evaluate relevant fan performance data
in order to submit meaningful
comments on the proposed energy
conservation standard for furnace fans.
Thus, on December 24, 2013, DOE
posted a pre-publication test procedure
final rule notice to regulations.gov and
issued a 30-day extension of the
standards NOPR comment period to
provide interested parties with time to
evaluate DOE’s proposed standards
using the final test procedure.
AHRI, Johnson Controls, and
Morrison stated that, even with the
comment period extension, the 20 days
between the publication of the test
procedure final rule on January 3, 2014
and the close of the standards NOPR
comment period on January 23, 2014
did not provide interested parties with
sufficient time to assess the energy
conservation standards NOPR based on
the provisions within the final test
procedure. AHRI added that DOE was
obligated to issue the NOPR on the
proposed energy conservation standards
after the issuance of the final rule on the
furnace fan test procedures per Section
7(c) of Appendix A to Subpart C of 10
CFR part 430. (AHRI, No. 98 at pp. 2,
3; Johnson Controls, No. 95 at p. 3;
Morrison, No. 108 at p. 3) Mortex stated
that they were not able to test any of
their products according to the final test
procedure by the time the energy
conservation standard NOPR comment
period closed. (Mortex, No. 104 at p. 2)
Ingersoll Rand commented that DOE’s
standards NOPR analyses are invalid
because they were not based on the test
procedure final rule. (Ingersoll Rand,
No. 107 at p. 2, 10). NEEA and NPCC
provided there is a need for product
testing using the final test procedure,
and a re-assessment of the derivation of
the proposed FER equations and
standard levels. NEEA and NPCC added
that they do not support a decision on
DOE received comments from
interested parties regarding the furnace
fan test procedure in response to the
furnace fan energy conservation
standard (ECS) NOPR. Interested
parties’ comments on the test procedure
are summarized below. DOE addressed
many of these issues in the test
procedure final rule, published in the
Federal Register on January 3, 2014. (79
FR 514). The publication of the test
procedure final rule occurred after the
standards NOPR public meeting, held
on December 3, 2013, but before the
close of the standards NOPR comment
period on January 23, 2014. For
comments that were addressed in the
test procedure final rule, a reference to
the applicable discussion contained in
the test procedure final rule document
is provided. DOE’s detailed response is
provided in this document for
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ER03JY14.000
(HCR) to account for variation in time
spent in this mode associated with
turndown of heating output. The HCR is
the ratio of the measured reduced heat
Where:
CH = annual furnace fan cooling operating
hours;
EMax = furnace fan electrical consumption at
maximum airflow-control setting
operating point;
HH = annual furnace fan heating operating
hours;
EHeat = furnace fan electrical consumption at
the default heating airflow-control
setting operating point for units with
single-stage heating or the default lowheating airflow control setting operating
point for units with multi-stage heating;
CHH = annual furnace fan constant
circulation hours;
ECirc = furnace fan electrical consumption at
the default constant-circulation airflowcontrol setting operating point (or
minimum airflow-control setting
operating point if a default constantcirculation airflow-control setting is not
specified);
QMax = airflow at maximum airflow-control
setting operating point; and
1000 = constant to put metric in terms of
watts/1000cfm, which is consistent with
industry practice.
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For multi-stage heating or modulating
heating products, the specified
operating hours for the heating mode are
divided by the heating capacity ratio
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standards before there is sufficient data
with which to verify that the proposed
FER values will not disqualify from
compliance the majority of the very
products upon which they are founded,
and for which DOE’s economic analyses
are valid. (NEEA and NPCC, No. 96 at
p. 2)
DOE disagrees with AHRI and
Morrison that the extended comment
period was insufficient. DOE issued a
test procedure SNOPR for furnace fans
on April 2, 2013. 78 FR 19606. DOE did
not make changes to the test procedure
between the SNOPR and final rule that
would significantly alter FER values for
most products. Interested parties that
conducted testing in accordance with
the test procedure SNOPR proposal
should not have to retest most furnace
models to derive an FER value that is
consistent with the final test procedure.
For most furnaces, the FER value should
not change or the FER value can be
recalculated per the final test procedure
requirements using the raw data
measured according to the SNOPR test
method. Therefore, notwithstanding the
20 days between the test procedure final
rule and the close of the standards
NOPR comment period, interested
parties still had over nine months
between the publication of the test
procedure SNOPR and the close of the
standards NOPR comment period to
collect and evaluate fan performance
data that is relevant to DOE’s proposed
standards. DOE received data that could
be used to derive FER values that meet
the final test procedure requirements
from multiple manufacturers during this
period.
DOE agrees with NEEA and NPCC
that its proposed standards should be
assessed based on FER values that are
reflective of performance as measured
by the final test procedure. For the
reasons stated above, DOE was able to
use much of the FER data it has
collected in previous phases of this
rulemaking to generate FER values that
meet the requirements of the final test
procedure. DOE also conducted testing
prior to and during the development of
the test procedure final rule that
generated a broad set of results to enable
DOE to derive FER values that are
consistent with the requirements of the
final test procedure. In addition, DOE
continued to collect and use data from
publicly-available product literature.
DOE relied on the mathematical
methods outlined in the test procedure
NOPR for using this data to model fan
performance and estimate FER values
that meet the final test procedure
requirements. 77 FR 28690 (May 15,
2012). DOE recognizes that this method
is not identical to the final test
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procedure method. However, DOE
believes the FER values generated in
this manner are still relevant because
the final test method is similar to the
test method proposed by AHRI (with
support from Goodman, Ingersoll Rand,
Lennox, and Morrison) in response to
the test procedure NOPR, which they
argued would result in accurate and
repeatable FER values that are
comparable to the FER values resulting
from the methods proposed in the
NOPR. (AHRI, No. 16 at p. 3; Goodman,
No. 17 at p. 4; Ingersoll Rand, No. 14 at
p. 1; Morrison, No. 21 at p. 3.) For these
reasons, Ingersoll Rand’s comment
stating that DOE’s standards NOPR
analyses are invalid because they are
not based on the test procedure final
rule is inaccurate. The standards
proposed in the NOPR and those
established by this final rule are based
on relevant FER data.
Goodman stated that DOE’s
modifications to the test procedure
since the April 2013 test procedure
SNOPR will have a significant impact
on FER. Goodman referred specifically
to the modification in the test procedure
that specifies that airflow be calculated
based on firing the product in the
absolute maximum airflow-control
setting if that setting is a default heating
setting. According to Goodman, most
furnaces allow heating operation at the
highest airflow setting. Thus, instead of
heating airflow setting being a midrange temperature rise as typically set
by factory default, it will now be a lowrange temperature rise at a much higher
and less efficient setting for FER
calculation (and a setting that will not
be typical of a field installation).
(Goodman, No. 102 at p. 7) Ingersoll
Rand echoed Goodman’s statement,
adding that the modification would also
result in higher watts in heating mode
and a higher FER value than would have
resulted using the procedure in the
SNOPR for a majority of furnaces.
(Ingersoll Rand, No. 107 at pp. 2, 10).
DOE disagrees with Goodman’s and
Ingersoll Rand’s comments. DOE
expects that both interested parties have
misinterpreted the test procedure
requirement. DOE recognizes that
product controls can be altered from
factory settings to allow heating in the
absolute maximum airflow-control
setting. The test procedure does not
allow for this practice. The test
procedure only requires testing in
factory-set configurations. Specific to
the modification in question, the test
procedure requires heating in the
absolute maximum airflow-control
setting only if that setting is a default
heat setting. See Section 8.6.1.2 of
Appendix AA to Subpart B of 10 CFR
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part 430. By definition, as outlined in
the test procedure, a default heating
airflow-control setting is factory-set and
specified for installed-use as a heat
setting by the manufacturer. See Section
2.2 of Appendix AA to Subpart B of 10
CFR part 430. Consequently, the
resulting temperature rise is also
factory-set by the manufacturer, and the
measured performance will be
representative of field use. In addition,
the test procedure SNOPR and final rule
requirements for EHeat (the watts in
heating mode input for FER) are
consistent and the measured values for
this input should not change. The
impacts of the modification in question
are explained in more detail in the test
procedure final rule. 79 FR 514 (January
3, 2014).
AHRI commented that in the final test
procedure that was published on
January 3, 2014, DOE introduced a
change within the test procedure that
increases the measured FER. AHRI
stated that DOE decided not to
implement AHRI’s recommendation that
a furnace be fired at the maximum
airflow rate to calculate the maximum
airflow. Instead, according to AHRI, the
final rule specifies that the maximum
airflow is determined by applying the
airflow equation for a heating setting
and adjusting to the maximum setting
based on pressure measurements. AHRI
claims that this approach results in an
increase of the measured FER and was
not accounted within the analyses
associated with the energy conservation
standards NOPR TSD that was issued on
October 25, 2013. AHRI recommends
that DOE reevaluate the analyses within
the entire TSD due to this single change.
(AHRI, No. 98 at p. 3, 4)
DOE introduced the change referred
to by AHRI in the April 2, 2013 test
procedure SNOPR. A detailed
discussion of DOE’s reasoning for that
change are provided in that notice. 78
FR 19616. DOE made additional
changes to this provision in the test
procedure final rule by requiring that
the product under test be fired at the
maximum airflow rate to calculate the
maximum airflow for furnaces for which
the maximum airflow-control setting is
a default heat setting (consistent with
AHRI’s recommendation). See Section
8.6.1.2 of Appendix AA to Subpart B of
10 CFR part 430. DOE disagrees with
AHRI that the change in question will
result in higher FER values. DOE fan
performance tests, including tests
following the final test procedure, show
that the maximum airflow calculated
when firing the product under test in
the maximum airflow control setting is
typically lower than when applying the
airflow equation for a heating setting
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and adjusting to the maximum setting
based on pressure measurements.
Consequently, FER values would be
lower if they were derived using airflow
values calculated when firing in the
maximum airflow-control setting. AHRI
did not provide data to the contrary. As
stated above, DOE’s proposed standards
and the standards established by this
document are valid because they are
based on FER values that are consistent
with the final test procedure (to include
FER values employing the airflow
adjustment method in question).
AHRI, Morrison, and Ingersoll Rand
commented that they are opposed to
DOE eliminating the HCR from the
denominator of the FER equation.
According to AHRI, DOE did not
provide a sound technical justification
for such a modification and
unnecessarily penalized the FER values
associated with multi-stage and
modulating units. (AHRI, No. 98 at p. 2,
3; Morrison, No. 108 at p. 3, 4; Ingersoll
Rand, No. 107 at p. 2, 10)
As discussed in the test procedure
final rule, DOE found that including
HCR in the denominator of the FER
equation resulted in percent reductions
in estimated annual energy
consumption, as calculated for FER, of
15 percent. 79 FR 515 (January 3, 2014).
Further, DOE found percent reductions
in FER of approximately 30 percent
when comparing single-stage products
using constant-torque brushless
permanent magnet (BPM) motors to
multi-stage products using constanttorque BPM motors. DOE eliminated
HCR from the FER equation because, as
a result, percent reductions in FER
dropped to 15 percent on average,
which is consistent with percent
reduction in estimated annual energy
consumption. 79 FR 515 (January 3,
2014). DOE did not receive any new
FER values for products that use a
constant-torque BPM motor and multistage heating. DOE was also unable to
find data in the public domain with
which to calculate new FER values to
represent such products. In the absence
of new data, DOE used the raw airflow,
ESP, and fan electrical energy
consumption data for single-stage
furnaces with constant-torque BPM
motors to generate FER values reflecting
the addition of theoretical multi-stage
heating capabilities. Single-stage
furnaces using constant-torque BPM
motors typically have additional
airflow-control settings that provide less
airflow than the factory-set heating
airflow-control setting. Theoretically,
these airflow-control settings could be
used for a low heat setting in a multistage heating configuration. DOE
identified as many models as possible
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that meet this criterion and for which
DOE has sufficient data to calculate
theoretical FER values for a multi-stage
configuration. For each model, DOE first
calculated the temperature rise in the
default heating setting based on the
airflow, thermal efficiency and input
heat rating in that setting. Next, DOE
used a variation of the same relationship
between these parameters to calculate
the theoretical low input capacity that
would achieve the same temperature
rise for each available airflow-control
setting below the heat setting. DOE then
evaluated the HCR for each of the lower
airflow-control settings based on the
theoretical input capacity of the lower
setting and the rated input capacity of
the default heat setting. DOE selected
the low airflow-control setting that
produced an HCR between 0.4 and 0.9
that was closest to 0.7 to represent the
theoretical low heating setting. DOE
chose these criteria based on
investigation of typical HCR values
observed in currently available
products. Finally, DOE calculated
estimated annual energy consumption
and an FER value using the single-stage
model’s data for the absolute maximum
and constant circulation airflow-control
settings and the data for the theoretical
low heating setting for the heating
airflow-control setting. DOE’s new data
shows that multi-staging reduces
estimated annual energy consumption
by an average of 14 percent and FER by
an average of 12 percent. These findings
are consistent with DOE’s previous
findings and support its decision to
eliminate HCR from the denominator of
the FER calculation.
Ingersoll Rand stated that the final
test procedure reduces the estimated
savings associated with BPM motors.
Ingersoll Rand commented that BPM
motors consume more power as static
pressure increases than permanent-split
capacitor (PSC) motors. (Ingersoll Rand,
No. 107 at p. 2, 10)
DOE addressed this issue in the
energy conservation standards NOPR.
78 FR 64084 (October 25, 2013). While
BPM motors consume more power as
static pressure increases, they also
provide more airflow. FER is
normalized by airflow to account for
this difference in behavior between
BPM and PSC motors. In addition, the
standards established in this document
are a function of airflow. BPM motordriven fan performance is evaluated
relative to PSC motor-driven fans that
provide the same amount of airflow at
the same reference system static
pressure as a result. Interested parties
did not provide any evidence that these
methods are inappropriate for
evaluating relative fan performance.
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China WTO commented that FER
includes factors, such as HCR, to
account for multi-stage heating but does
not include analogous factors for multistage cooling. (China WTO, No. 92 at p.
1)
DOE considered accounting for fan
performance during multi-stage cooling
operation for the test procedure NOPR.
77 FR 28680. DOE did not include
factors for multi-stage cooling in the
final test procedure because the
presence and capacity of low-stage
cooling is dependent on the cooling
system with which a product containing
a furnace fan is paired. DOE found in its
review of publicly-available product
literature that detailed characteristics of
the cooling system are not typically
provided. Consequently, entities
performing the DOE furnace fan test
procedure cannot identify the airflowcontrol setting that would be designated
for low-stage cooling operation. In
addition, multi-stage heating is not
necessarily associated with multi-stage
cooling capability (e.g., multi-stage
cooling equipment is much less
common than multi-stage heating
equipment).
China WTO stated that the final test
procedure does not provide a method
for calculating the maximum airflow
when the maximum airflow-control
setting is only designated for cooling.
(China WTO, No. 92 at p. 1)
The method for calculating the
maximum airflow when the maximum
airflow-control setting is only
designated for cooling is provided in the
final rule and in Section 9 of appendix
AA of subpart B of part 430 of the CFR.
79 FR 524 (January 3, 2014).
The California Investor Owned
Utilities (CA IOU) commented that they
observed a potential error in the
calculation of airflow in the final test
procedure. Specifically, CA IOU
recommended that DOE include the
humidity ratio in pounds water vapor
per pounds dry air. CA IOU submits that
this addition will increase the accuracy
of the calculation of specific volume of
test room air in cubic feet per pound of
dry air to calculate airflow. (CA IOU,
No. 106 at p. 4)
The equation for calculating airflow
in the final test procedure already
includes the humidity ratio in pounds
water vapor per pounds dry air as
codified in Section 9 of appendix AA of
subpart B of part 430 of the CFR.
CA IOU recommended that in
addition to reporting FER, which is the
basis for the performance standard, DOE
require manufacturers to report
individual mode electrical energy
consumption values (e.g., EHeat, EMax,
and ECirc). According to CA IOU,
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reporting these values would greatly
facilitate the development of more
targeted energy efficiency incentive
programs, and manufacturers already
have to measure and perform these
calculations for the composite FER. CA
IOU recognizes that EMax could
represent fan electrical energy
consumption in either heating or
cooling mode depending on the
product. Nonetheless, CA IOU also
recommends that DOE require
manufacturers to report fan electrical
energy consumption in cooling mode
even if not included in FER because
having it as an additional data point
could be useful for the development of
utility programs across the country. CA
IOU stated that energy efficiency
incentive programs typically require a
rigorous level of review and justification
for implementation. Gaps in
performance data of commercially
available equipment is one of the main
limiting factors in program
development, contributing to the
lengthy and resource-intensive data
collection and verification processes. In
the case of this rulemaking,
manufacturers will already be required
to test their products in heating, cooling,
and constant circulation modes. CA IOU
believes that the minimal extra effort
required by manufacturers to report
these values would be outweighed by
the opportunity for utilities and other
public agencies to develop incentive
programs using these performance
metrics, which in turn would positively
impact manufacturers of high
performing products. For these reasons,
CA IOU strongly urge DOE to require
manufacturers to report tested and
calculated metrics that feed into a
composite metric for the standard.
ASAP, ASE, NCLC, and NRDC,
hereinafter referred to as ASAP, et al.,
agree. (ASAP, et al., No. 105 at p. 3)
At this time, DOE is declining to
adopt reporting requirements for
individual mode electrical consumption
values as the CA IOU suggests. While
DOE is open to considering additional
reporting metrics in the future, DOE
believes that establishing a Federal test
procedure and metric (i.e., FER) will
provide utility programs with a basis for
establishing meaningful incentive
programs as the CA IOUs desire.
Further, DOE believes that reporting the
aggregated electrical consumption (i.e.,
the FER metric) will provide market
differentiation amongst currentlyavailable models, thereby allowing the
utility programs to set voluntary levels
for incentive programs at meaningful
levels to obtain energy savings. If data
and analyses are provided, which show
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the disaggregated levels are necessary
for the proper execution of utility
incentive programs, DOE will consider
modifying the certification requirements
for furnace fans.
Unico pointed out that DOE presents
the required minimum reference system
ESP values inconsistently across
rulemaking documents. Unico noticed
that in some documents DOE presents
these values as a range for each
installation type, and in other
rulemaking documents DOE presents
only the lower value within each range
with an asterisk. (Unico, No. 93 at p. 6)
As explained in the test procedure
final rule, DOE’s test experience
confirms manufacturer concerns that
specific ESP values are difficult to
achieve and maintain when measuring
airflow. The final test procedure
specifies that products maintain an ESP
level between the minimum reference
system value and 0.05 in. wc. above that
minimum value to allow for slight
variations. 79 FR 508 (January 3, 2014).
Consequently, DOE presents the
minimum required ESP values as a
range in Section 8.6.1.2 in appendix AA
of subpart B of part 430 in the CFR or
as the minimum value with an asterisk
accompanied by the explanation above
in other DOE documents.
AHRI commented that DOE should
provide the option of employing an
alternative efficiency determination
method (AEDM) to determine FER.
AHRI insists that an AEDM is critical for
manufacturers to implement new
requirements on a timely basis while
minimizing burden. AHRI believes that
the number of furnace fan basic models
will be greater than the number of
furnace basic models. According to
AHRI, the pressure drop due to the gas
heat exchanger will require that each
furnace basic model also be considered
as a furnace fan basic model. AHRI
added that additional furnace fan basic
models would be created in order to
account for the type of installation.
AHRI also pointed out that many
furnace fan manufacturers also produce
several other DOE regulated products.
AHRI submits that rather than requiring
manufacturers to spend valuable
resources on conducting several tests,
DOE should recognize that those
resources could be better spent on
innovating more efficient products.
(AHRI, No. 98 at p. 13)
DOE provided a detailed discussion of
this issue in the test procedure final
rule. 79 FR 513 (January 3, 2014). DOE
currently does not allow the use of
AEDMs for residential products, with
the exception of central air conditioners
and heat pumps due to the uniquely
large number of combinations of split-
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system air conditioners and heat pumps
that are rated. DOE recognizes that the
number of furnace fan basic models may
outnumber furnace basic models for the
reasons AHRI lists. Even so, DOE
expects the number of basic models of
furnace fans to be significantly less than
the number of basic models of
residential central air conditioners and
heat pumps (CAC and HP) for which
alternative rating methods are currently
allowed. DOE has not found the
residential furnace fan market to be
highly customized (i.e., containing
many unique built-to-order designs) and
expects that manufacturers will be able
to group similar individual furnace fan
types into basic models to reduce testing
burden. DOE notes that it currently has
over 1 million CAC combinations
certified in the Compliance Certification
Management System (CCMS) compared
to approximately 12,500 certified
furnace basic models. Consequently,
DOE does not agree with AHRI’s
assertion that an alternative rating
method needs to be considered at this
time. Should AHRI or the industry
provide additional data or
substantiation for its requests
demonstrating why testing furnace fans
are unique, as compared to the majority
of other residential products for which
AEDMs are not allowed, then DOE may
consider such requests in a separate
rulemaking.
B. Product Classes and Scope of
Coverage
Although the title of 42 U.S.C. 6295(f)
refers to ‘‘furnaces and boilers,’’ DOE
notes that 42 U.S.C. 6295(f)(4)(D) was
written using notably broader language
than the other provisions within the
same section. Specifically, that statutory
provision directs DOE to ‘‘consider and
prescribe energy conservation standards
or energy use standards for electricity
used for purposes of circulating air
through duct work.’’ Such language
could be interpreted as encompassing
electrically-powered devices used in
any residential HVAC product to
circulate air through duct work, not just
furnaces, and DOE has received
numerous comments on both sides of
this issue. However, in this rulemaking,
DOE is only covering those circulation
fans that are used in furnaces and
modular blowers. DOE is using the term
‘‘modular blower’’ to refer to HVAC
products powered by single-phase
electricity that comprise an encased
circulation blower that is intended to be
the principal air-circulation source for
the living space of a residence. A
modular blower is not contained within
the same cabinet as a residential
furnace, CAC, or heat pump. Instead,
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modular blowers are designed to be
paired with separate residential HVAC
products that provide heating and
cooling, typically a separate CAC/HP
coil-only unit. DOE finds that modular
blowers and electric furnaces are very
similar in design. In many cases, the
only difference between a modular
blower and electric furnace is the
presence of an electric resistance
heating kit. DOE is aware that some
modular blower manufacturers offer
electric resistance heating kits to be
installed in their modular blower
models so that the modular blowers can
be converted to stand-alone electric
furnaces. In addition, FER values for
modular blowers can be easily
calculated using the final test
procedure. DOE addresses the furnace
fans used in modular blowers in this
rulemaking for these reasons. As a result
of the extent of the current rulemaking,
DOE is not addressing public comments
that pertain to fans in other types of
HVAC products.
When evaluating and establishing
energy conservation standards, DOE
divides covered products into product
classes by the type of energy used or by
capacity or other performance-related
features that justify a different standard.
In making a determination whether a
performance-related feature justifies a
different standard, DOE must consider
such factors as the utility to the
consumer of the feature and other
factors DOE determines are appropriate.
(42 U.S.C. 6295(q)) For this rulemaking,
DOE differentiates between product
classes based on internal structure and
application-specific design differences
that impact furnace fan energy
consumption. Details regarding how
internal structure and applicationspecific design differences that impact
furnace fan energy consumption are
included in chapter 3 of the final rule
technical support document (TSD). DOE
includes the following product classes
for this rulemaking.
• Non-Weatherized, Non-Condensing
Gas Furnace Fan (NWG–NC)
• Non-Weatherized, Condensing Gas
Furnace Fan (NWG–C)
• Weatherized Non-Condensing Gas
Furnace Fan (WG–NC)
• Non-Weatherized, Non-Condensing
Oil Furnace Fan (NWO–NC)
• Non-Weatherized Electric Furnace/
Modular Blower Fan (NWEF/NWMB)
• Mobile Home Non-Weatherized, NonCondensing Gas Furnace Fan (MH–
NWG–NC)
• Mobile Home Non-Weatherized,
Condensing Gas Furnace Fan (MH–
NWG–C)
• Mobile Home Electric Furnace/
Modular Blower Fan (MH–EF/MB)
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• Mobile Home Weatherized Gas
Furnace Fan (MH–WG)
• Mobile Home Non-Weatherized Oil
Furnace Fan (MH–NWO)
Each product class title includes
descriptors that indicate the
application-specific design and internal
structure of its included products.
‘‘Weatherized’’ and ‘‘non-weatherized’’
are descriptors that indicate whether the
HVAC product is installed outdoors or
indoors, respectively. Weatherized
products also include an internal
evaporator coil, while non-weatherized
products are not shipped with an
evaporator coil but may be designed to
be paired with one. ‘‘Condensing’’ refers
to the presence of a secondary,
condensing heat exchanger in addition
to the primary combustion heat
exchanger in certain furnaces. The
presence of an evaporator coil or
secondary heat exchanger significantly
impacts the internal structure of an
HVAC product, and in turn, the energy
performance of the furnace fan
integrated in that HVAC product.
‘‘Mobile home’’ products meet certain
design requirements that allow them to
be installed in mobile homes (e.g., a
more compact cabinet size). Descriptors
for ‘‘gas,’’ ‘‘oil,’’ or ‘‘electric’’ indicate
the type of fuel that the HVAC product
uses to produce heat, which determines
the type and geometry of the primary
heat exchanger used in the HVAC
product.
C. Technological Feasibility
1. General
In each energy conservation standards
rulemaking, DOE conducts a screening
analysis based on information gathered
on all current technology options and
prototype designs that could improve
the efficiency of the products or
equipment that are the subject of the
rulemaking. As the first step in such an
analysis, DOE develops a list of
technology options for consideration in
consultation with manufacturers, design
engineers, and other interested parties.
DOE then determines which of those
means for improving efficiency are
technologically feasible. DOE considers
technologies incorporated in
commercially-available products or in
working prototypes to be
technologically feasible. 10 CFR part
430, subpart C, appendix A, Section
4(a)(4)(i).
After DOE has determined that
particular technology options are
technologically feasible, it further
evaluates each technology option in
light of the following additional
screening criteria: (1) Practicability to
manufacture, install, and service; (2)
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adverse impacts on product utility or
availability; and (3) adverse impacts on
health or safety. 10 CFR part 430,
subpart C, appendix A, Section
4(a)(4)(ii)–(iv). Additionally, it is DOE
policy not to include in its analysis any
proprietary technology that is a unique
pathway to achieving a certain
efficiency level. Section IV.B of this
document discusses the results of the
screening analysis for residential
furnace fans, particularly the designs
DOE considered, those it screened out,
and those that are the basis for the tcrial
standard levels (TSLs) in this
rulemaking. For further details on the
screening analysis for this rulemaking,
see chapter 4 of the final rule TSD.
2. Maximum Technologically Feasible
Levels
When DOE proposes to adopt a new
standard for a type or class of covered
product, it must determine the
maximum improvement in energy
efficiency or maximum reduction in
energy use that is technologically
feasible for such product. (42 U.S.C.
6295(p)(1)) Accordingly, in the
engineering analysis, DOE determined
the maximum technologically feasible
(‘‘max-tech’’) improvements in energy
efficiency for residential furnace fans,
using the design parameters for the
most-efficient products available on the
market or in working prototypes. The
max-tech levels that DOE determined
for this rulemaking are described in
section IV.C of this final rule and in
chapter 5 of the final rule TSD.
D. Energy Savings
1. Determination of Savings
For each TSL, DOE projected energy
savings from the products that are the
subjects of this rulemaking purchased
during a 30-year period that begins in
the year of compliance with amended
standards (2019–2048).13 The savings
are measured over the entire lifetime of
products purchased in the 30-year
period.14 DOE used the NIA model to
estimate the NES for products
purchased over the above period. The
model forecasts total energy use over the
analysis period for each representative
product class at efficiency levels set by
each of the considered TSLs. DOE then
13 DOE also presents a sensitivity analysis that
considers impacts for products shipped in a 9-year
period.
14 In the past, DOE presented energy savings
results for only the 30-year period that begins in the
year of compliance. In the calculation of economic
impacts, however, DOE considered operating cost
savings measured over the entire lifetime of
products purchased during the 30-year period. DOE
has chosen to modify its presentation of national
energy savings to be consistent with the approach
used for its national economic analysis.
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compares the aggregated energy use at
each TSL to the base-case energy use to
obtain the NES. The NIA model is
described in section IV. H of this
document and in chapter 10 of the final
rule TSD.
DOE used its NIA spreadsheet model
to estimate energy savings from
amended standards for the products that
are the subject of this rulemaking. The
NIA spreadsheet model (described in
section IV. H of this notice) calculates
energy savings in site energy, which is
the energy directly consumed by
products at the locations where they are
used. For electricity, DOE reports
national energy savings in terms of the
primary (source) energy savings, which
are the savings in the energy that is used
to generate and transmit the site
electricity. To convert site energy to
primary energy, DOE derives annual
conversion factors from the model used
to prepare the Energy Information
Administration’s (EIA) Annual Energy
Outlook 2013 (AEO 2013).
DOE also has begun to estimate fullfuel-cycle energy savings. 76 FR 51282
(August 18, 2011), as amended at 77 FR
49701 (August 17, 2012). The full-fuelcycle (FFC) metric includes the energy
consumed in extracting, processing, and
transporting primary fuels (i.e., coal,
natural gas, petroleum fuels), and thus
presents a more complete picture of the
impacts of energy efficiency standards.
DOE’s evaluation of FFC savings is
driven in part by the National Academy
of Science’s (NAS) report on FFC
measurement approaches for DOE’s
Appliance Standards Program.15 The
NAS report discusses that FFC was
primarily intended for energy efficiency
standards rulemakings where multiple
fuels may be used by a particular
product. In the case of this rulemaking
pertaining to residential furnace fans,
only a single fuel—electricity—is
consumed by the product. DOE’s
approach is based on the calculation of
an FFC multiplier for each of the energy
types used by covered products.
Although the addition of FFC energy
savings in the rulemakings is consistent
with the recommendations, the
methodology for estimating FFC does
not project how fuel markets would
respond to this particular standards
rulemaking. The FFC methodology
simply estimates how much additional
energy, and in turn how many tons of
emissions, may be displaced if the
15 ‘‘Review of Site (Point-of-Use) and Full-FuelCycle Measurement Approaches to DOE/EERE
Building Appliance Energy-Efficiency Standards,’’
(Academy report) was completed in May 2009 and
included five recommendations. A copy of the
study can be downloaded at: https://www.nap.edu/
catalog.php?record_id=12670.
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estimated fuel were not consumed by
the products covered in this rulemaking.
It should be noted that inclusion of FFC
savings has not affected DOE’s choice of
the energy conservation standards
adopted in today’s final rule. For more
information on FFC energy savings, see
section IV. H.2.
2. Significance of Savings
EPCA prohibits DOE from adopting a
standard for a covered product that
would not result in significant energy
savings. (42 U.S.C. 6295(o)(3)(B))
Although the term ‘‘significant’’ is not
defined in EPCA, the U.S. Court of
Appeals for the District of Columbia, in
Natural Resources Defense Council v.
Herrington, 768 F.2d 1355, 1373 (D.C.
Cir. 1985), opined that Congress
intended ‘‘significant’’ energy savings in
this context to be savings that were not
‘‘genuinely trivial.’’ The energy savings
for today’s standards (presented in
section V of this notice) are nontrivial,
and, therefore, DOE considers them
‘‘significant’’ within the meaning of
section 325 of EPCA.
E. Economic Justification
1. Specific Criteria
As discussed in section II.A, EPCA
provides seven factors to be evaluated in
determining whether a potential energy
conservation standard is economically
justified. (42 U.S.C. 6295(o)(2)(B)(i)(I)–
(VII)) The following sections generally
discuss how DOE is addressing each of
those seven factors in this rulemaking.
For further details and the results of
DOE’s analyses pertaining to economic
justification, see sections IV and V of
today’s document.
Economic Impact on Manufacturers and
Commercial Customers
In determining the impacts of a
potential new or amended energy
conservation standard on
manufacturers, DOE conducts a
manufacturer impact analysis (MIA), as
discussed in section IV.J. DOE first
determines a potential standard’s
quantitative impacts using an annual
cash flow approach. This step includes
both a short-term assessment (based on
the cost and capital requirements
associated with new or amended
standards during the period between the
announcement of a regulation and the
compliance date of the regulation) and
a long-term assessment (based on the
costs and marginal impacts over the 30year analysis period). The impacts
analyzed include: (1) Industry net
present value (INPV) (which values the
industry based on expected future cash
flows); (2) cash flows by year; (3)
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changes in revenue and income; and (4)
other measures of impact, as
appropriate. Second, DOE analyzes and
reports the potential impacts on
different types of manufacturers, paying
particular attention to impacts on small
manufacturers. Third, DOE considers
the impact of new or amended
standards on domestic manufacturer
employment and manufacturing
capacity, as well as the potential for
new or amended standards to result in
plant closures and loss of capital
investment, as discussed in section
IV.N. Finally, DOE takes into account
cumulative impacts of other DOE
regulations and non-DOE regulatory
requirements on manufacturers.
For individual customers, measures of
economic impact include the changes in
LCC and the PBP associated with new
or amended standards. These measures
are discussed further in the following
section. For consumers in the aggregate,
DOE also calculates the national net
present value of the economic impacts
applicable to a particular rulemaking.
DOE also evaluates the LCC impacts of
potential standards on identifiable
subgroups of consumers that may be
affected disproportionately by a national
standard.
Savings in Operating Costs Compared to
Increase in Price (Life-Cycle Costs)
EPCA requires DOE to consider the
savings in operating costs throughout
the estimated average life of the covered
product compared to any increase in the
price of the covered product that are
likely to result from the standard. (42
U.S.C. 6295(o)(2)(B)(i)(II)) DOE conducts
this comparison in its LCC and PBP
analysis.
The LCC is the sum of the purchase
price of a product (including the cost of
its installation) and the operating costs
(including energy, maintenance, and
repair costs) discounted over the
lifetime of the equipment. To account
for uncertainty and variability in
specific inputs, such as product lifetime
and discount rate, DOE uses a
distribution of values, with probabilities
attached to each value. For its analysis,
DOE assumes that consumers will
purchase the covered product in the
first year of compliance with new
standards.
The LCC savings and the PBP for the
considered efficiency levels are
calculated relative to a base-case
scenario, which reflects likely market
trends in the absence of new or
amended standards. DOE identifies the
percentage of consumers estimated to
receive LCC savings or experience an
LCC increase, in addition to the average
LCC savings associated with a particular
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standard level. DOE’s LCC analysis is
discussed in further detail in section
IV.F.
Energy Savings
Although significant conservation of
energy is a separate statutory
requirement for adopting an energy
conservation standard, EPCA also
requires DOE, in determining the
economic justification of a standard, to
consider the total projected energy
savings that are expected to result
directly from the standard. (42 U.S.C.
6295(o)(2)(B)(i)(III)) DOE uses NIA
spreadsheet results in its consideration
of total projected savings. For the results
of DOE’s analyses related to the
potential energy savings, see section V.B
of this notice and chapter 10 of the final
rule TSD.
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Lessening of Utility or Performance of
Equipment
In establishing product classes, and in
evaluating design options and the
impact of potential standard levels, DOE
follows EPCA’s requirement to develop
standards that would not lessen the
utility or performance of the products
under consideration. (42 U.S.C.
6295(o)(2)(B)(i)(IV)) DOE has
determined that none of the TSLs
presented in today’s final rule would
reduce the utility or performance of the
products under consideration in this
rulemaking. During the screening
analysis, DOE eliminated from
consideration any technology that
would adversely impact customer
utility. See section IV.B of this notice
and chapter 4 of the final rule TSD for
further details.
Impact of Any Lessening of Competition
EPCA requires DOE to consider any
lessening of competition that is likely to
result from setting new or amended
standards. It also directs the Attorney
General of the United States (Attorney
General) to determine the impact, if any,
of any lessening of competition likely to
result from a proposed standard and to
transmit such determination to the
Secretary within 60 days of the
publication of a proposed rule, together
with an analysis of the nature and
extent of the impact. (42 U.S.C.
6295(o)(2)(B)(i)(V) and (ii))
To assist the Department of Justice
(DOJ) in making such a determination,
DOE provided DOJ with copies of both
the NOPR and NOPR TSD for review. In
its assessment letter responding to DOE,
DOJ concluded that the proposed energy
conservation standards for residential
furnace fans are unlikely to have a
significant adverse impact on
competition. DOE is publishing the
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Attorney General’s assessment at the
end of this final rule.
Need of the Nation To Conserve Energy
Another factor that DOE must
consider in determining whether a new
or amended standard is economically
justified is the need for national energy
and water conservation. (42 U.S.C.
6295(o)(2)(B)(i)(VI)) The energy savings
from new or amended standards are
likely to provide improvements to the
security and reliability of the Nation’s
energy system. Reductions in the
demand for electricity may also result in
reduced costs for maintaining the
reliability of the Nation’s electricity
system. DOE conducts a utility impact
analysis to estimate how new or
amended standards may affect the
Nation’s needed power generation
capacity, as discussed in section IV.M.
Energy savings from energy
conservation standards are also likely to
result in environmental benefits in the
form of reduced emissions of air
pollutants and greenhouse gases
associated with energy production (i.e.,
from power plants). For a discussion of
the results of the analyses relating to the
potential environmental benefits of
today’s standards, see sections IV.K,
IV.L and V.B.6 of this notice. DOE
reports the expected environmental
effects from today’s standards, as well as
from each TSL it considered, in chapter
13 of the final rule TSD. DOE also
reports estimates of the economic value
of emissions reductions resulting from
the considered TSLs in chapter 14 of the
final rule TSD.
Other Factors
EPCA allows the Secretary, in
determining whether a new or amended
standard is economically justified, to
consider any other factors that the
Secretary deems to be relevant. (42
U.S.C. 6295(o)(2)(B)(i)(VII)) There were
no other factors considered for today’s
final rule.
2. Rebuttable Presumption
As set forth in 42 U.S.C.
6295(o)(2)(B)(iii), EPCA provides for a
rebuttable presumption that an energy
conservation standard is economically
justified if the additional cost to the
consumer of a product that meets the
new or amended standard is less than
three times the value of the first-year
energy (and, as applicable, water)
savings resulting from the standard, as
calculated under the applicable DOE
test procedure. DOE’s LCC and PBP
analyses generate values that calculate
the PBP for consumers of products
subject to potential new and amended
energy conservation standards. These
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analyses include, but are not limited to,
the 3-year PBP contemplated under the
rebuttable presumption test. However,
DOE routinely conducts an economic
analysis that considers the full range of
impacts to consumers, manufacturers,
the Nation, and the environment, as
required under 42 U.S.C.
6295(o)(2)(B)(i). The results of these
analyses serve as the basis for DOE’s
evaluation of the economic justification
for a potential standard level (thereby
supporting or rebutting the results of
any preliminary determination of
economic justification). The rebuttable
presumption payback calculation is
discussed in section IV.F of this
rulemaking and chapter 8 of the final
rule TSD.
IV. Methodology and Discussion
A. Market and Technology Assessment
DOE develops information that
provides an overall picture of the
market for the products concerned,
including the purpose of the products,
the industry structure, manufacturers,
market characteristics, and technologies
used in the products. This activity
includes both quantitative and
qualitative assessments, based primarily
on publicly-available information. The
subjects addressed in the market and
technology assessment for this
residential furnace fans rulemaking
include: (1) A determination of the
scope of this rulemaking; (2) product
classes; (3) manufacturers; (4) quantities
and types of products sold and offered
for sale; (5) retail market trends; (6)
regulatory and non-regulatory programs;
and (7) technologies or design options
that could improve the energy efficiency
of the product(s) under examination.
The key findings of DOE’s market
assessment are summarized below. See
chapter 3 of the final rule TSD for
further discussion of the market and
technology assessment.
1. Definition and Scope of Coverage
EPCA provides DOE with the
authority to consider and prescribe new
energy conservation standards for
electricity used to circulate air through
duct work. (42 U.S.C. 6295(f)(4)(D)) DOE
adopted the term ‘‘furnace fan’’ as
shorthand to describe the range of
products encompassed by this statutory
mandate. In the preliminary analysis,
DOE interpreted its statutory mandate
by defining ‘‘furnace fan’’ to include
‘‘any electrically-powered device used
in residential central heating,
ventilation, and air-conditioning
(HVAC) systems for the purpose of
circulating air through duct work.’’ 77
FR 40530, 40532 (July 10, 2012). DOE
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considered a typical furnace fan as
consisting of a fan motor and its
controls, an impeller, and a housing, all
of which are components of an HVAC
product that includes additional
components, including the cabinet.
In response to the preliminary
analysis, many interested parties
disagreed with DOE’s definition of
‘‘furnace fan’’ and corresponding
approach to set component-level
regulations, which they warned would
ignore system effects that could impact
both fan and HVAC system energy
consumption. California investor-owned
utilities CA IOUs suggested that
‘‘furnace fan’’ should be defined as a
unit consisting of a fan motor, its
controls, an impeller, shroud, and
cabinet that houses all of the heat
exchange material for the furnace.
According to CA IOUs, their suggested
definition would reduce ambiguity and
ensure that the components in HVAC
products that affect furnace fan energy
consumption are considered in this
rulemaking. (CA IOUs, No. 56 at p. 1)
Ingersoll Rand went further and
suggested a system-level regulatory
approach, where the entire duct and
furnace system would be regulated,
maintaining that such approach would
produce a more useful metric to
consumers when evaluating
performance. (Ingersoll Rand, PA Public
Meeting Transcript, No. 43 at p. 42)
Conversely, NEEP observed that by
regulating fan energy use separately, the
individual efficiency of the component
is considered when it would otherwise
be ignored by manufacturers. (NEEP,
No. 51 at p. 3) Rheem commented that
some designs require higher air velocity
to improve heat transfer but also require
more electrical consumption to drive
the blower at the higher velocity.
(Rheem, PA Public Meeting Transcript,
No. 43 at p. 63) Rheem commented that
turbulent flow is considerably more
efficient for heat transfer than laminar
flow,16 but more energy is required to
move turbulent air. (Rheem, No. 54 at p.
10) Similarly, Lennox and Morrison
commented that in order to improve
heating and cooling efficiency, often a
second heating coil is added, but this
also leads to higher electrical
consumption by the furnace fan.
16 ‘‘Laminar flow’’ is as term to describe when all
fluid particles move in paths parallel to the overall
flow direction (i.e., in layers). Laminar flow may
occur when the flow channel is small and the speed
is low. ‘‘Turbulent flow’’ is characterized by a threedimensional movement of the fluid particles
superimposed on the overall direction of motion.
Turbulent flow may occur when the flow speed is
higher and when there are obstacles in the channel
that disrupt the flow profile. The turbulent flow
intensifies the heat transfer, thus resulting in more
efficient heat exchange.
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(Lennox, No. 43 at p. 64; Morrison, No.
43 at p. 64) Ingersoll Rand argued that
as the efficiency of the furnace fan
motor increases, it dissipates less heat,
and consequently, the furnace will
consume more gas to compensate and
meet the desired house heat load.
(Ingersoll Rand, No. 43 at p. 66)
In the NOPR, DOE responded by
explaining that DOE is required by
EPCA to consider and prescribe new
energy conservation standards or energy
use standards for electricity used for
purposes of circulating air through duct
work. (42 U.S.C. 6295(f)(4)(D))
Consequently, in the context of furnace
fans, DOE does not have latitude to
apply only a single standard for the
larger HVAC product (which is already
regulated). Pursuant to this statutory
mandate, DOE issued a NOPR which
proposed energy conservation standards
for circulation fans used in residential
central HVAC systems (78 FR 64068
(Oct. 25, 2013)). DOE added that it did
not interpret its authority as including
regulating the duct work itself. DOE
recognized that component-level
regulations could have system-level
impacts. Accordingly, DOE conducted
its NOPR analyses and selected the
standard levels proposed in the NOPR
in such a way that meets the statutory
requirements set forth by EPCA without
ignoring system effects, which
otherwise might compromise the
thermal performance of the HVAC
products that incorporate furnace fans.
For example, the final test procedure
codified in DOE’s regulations at 10 CFR
part 430, subpart B, appendix AA
specifies that the furnace fan be tested
as factory-installed in the HVAC
product, thereby enabling the rating
metric, FER, to account for system
effects on airflow delivery and,
ultimately, energy performance. In
addition, the product class structure
proposed in the NOPR allowed for
differentiation of products with designs
that achieve higher thermal efficiency
but may have lower fan performance,
such as condensing furnaces. 78 FR
64068, 64082 (Oct. 25, 2013).
In the January 3, 2014 test procedure
final rule, DOE broadened its definition
of ‘‘furnace fan’’ to mean ‘‘an
electrically-powered device used in a
consumer product for the purpose of
circulating air through ductwork.’’ 79
FR 500, 521.
In response to the NOPR, DOE did not
receive comments from interested
parties regarding the definition of
‘‘furnace fan’’ established by the test
procedure final rule. Consequently, in
this standards final rule, DOE is
maintaining the definition for ‘‘furnace
fan,’’ codified at 10 CFR 430.2.
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However, DOE did receive comments on
its definitions for certain product types
that include furnace fans. DOE
summarizes and responds to these
comments later in this section of the
notice.
The scope of the preliminary analysis
included furnace fans used in furnaces,
modular blowers, and hydronic air
handlers. Even though DOE has
interpreted its authority as
encompassing any electrically-powered
device used in residential HVAC
products to circulate air through duct
work, the preliminary analysis scope
excluded single-package central air
conditioners (CAC) and heat pumps
(HP) and split-system CAC/HP blowercoil units. At the time of the preliminary
analysis, DOE determined that it may
consider these and other such products
in a future rulemaking as data and
information to develop credible
analyses becomes available.
In response to the preliminary
analysis, efficiency advocates expressed
concern at DOE’s exclusion of packaged
and split-system CAC products because
advocates believe current standards for
these products do not maximize the
technologically feasible and
economically justified energy savings
for the circulation fans integrated in
these products. ASAP and Adjuvant
stated that the metric used for CAC
products does not accurately represent
field conditions and requested that they
be added to the scope. 78 FR 64068,
64080 (Oct. 25, 2013).
In contrast, many manufacturers
submitted comments in response to the
preliminary analysis that they believe
that the scope of coverage presented in
the preliminary analysis exceeds the
statutory authority granted to DOE
because the statutory language for this
rulemaking is found in 42 U.S.C 6295(f)
under the title ‘‘Standards for furnaces
and boilers.’’ Consequently,
manufacturers stated that DOE should
not include any non-furnace products
such as central air conditioners, heat
pumps, or condensing unit-blower-coil
combinations. Manufacturers also
claimed that the electricity used to
circulate air through duct work is
already adequately accounted for in
existing energy efficiency metrics for
CAC and HP products that use
circulation fans. 78 FR 64068, 64080–81
(Oct. 25, 2013).
In the October 25, 2013 furnace fan
energy conservation standard NOPR,
DOE noted that, although the title of this
statutory section refers to ‘‘furnaces and
boilers,’’ the applicable provision at 42
U.S.C. 6295(f)(4)(D) was written using
notably broader language than the other
provisions within the same section. 78
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FR 64068, 64081. Specifically, that
statutory provision directs DOE to
‘‘consider and prescribe energy
conservation standards or energy use
standards for electricity used for
purposes of circulating air through duct
work.’’ Id. Such language could be
interpreted as encompassing
electrically-powered devices used in
any residential HVAC product to
circulate air through duct work, not just
furnaces, and DOE has received
numerous comments on both sides of
this issue. In the standards NOPR,
however, DOE only proposed energy
conservation standards for those
circulation fans that are used in
residential furnaces and modular
blowers (see discussion below). As a
result, DOE did not address public
comments that pertain to fans in other
types of HVAC products (other than to
clarify instances where there was
uncertainty as to whether a given
product fits within the scope of the
current rulemaking). The following list
describes the furnace fans which DOE
proposed to address in the standards
NOPR.
• Products addressed in this
rulemaking: Furnace fans used in
weatherized and non-weatherized gas
furnaces, oil furnaces, electric furnaces,
and modular blowers.
• Products not addressed in this
rulemaking: Furnace fans used in other
products, such as split-system CAC and
heat pump indoor units, through-thewall indoor units, small-duct, highvelocity (SDHV) indoor units, energy
recovery ventilators (ERVs), heat
recovery ventilators (HRVs), draft
inducer fans, exhaust fans, or hydronic
air handlers.
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Id.
In the October 25, 2013 NOPR, DOE
also maintained its proposal to account
for the electrical consumption of
furnace fans while performing all active
mode functions (i.e., heating, cooling,
and constant circulation) because
furnace fans are used not just for
circulating air through duct work during
heating operation, but also for
circulating air during cooling and
constant-circulation operation. In DOE’s
view, in order to obtain a complete
assessment of overall performance and a
metric that reflects the product’s
electrical energy consumption during a
representative average use cycle, the
metric must account for electrical
consumption in a set of airflow-control
settings that spans all active mode
functions. This would ensure a more
accurate accounting of the benefits of
improved furnace fans. Id.
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China WTO commented that DOE’s
definition for ‘‘furnace fan’’ and the
proposed scope show that residential
furnace fans primarily perform the
heating function. For this reason, China
WTO recommended that DOE exclude
fan performance for cooling operation to
avoid unnecessary test procedure
burden. (China WTO, No. 92 at pp. 1–
2).
For the reasons stated above, the
energy conservation standards
established by this notice account for
the electrical consumption of furnace
fans while performing all active mode
functions (i.e., heating, cooling, and
constant circulation). The commenter
did not dispute the fact that fans will
operate in cooling or constantcirculation mode, often for non-trivial
periods of time. Because the electrical
energy consumption of the fan may vary
substantially depending on its mode of
operation, DOE has concluded that
testing fan operation in all these modes
is necessary to reflect the product’s
energy consumption during a
representative use cycle and that such
testing would not be unduly
burdensome to conduct.
Unico submitted comments regarding
concerns with DOE’s test procedure and
proposed standard levels as they apply
to SDHV systems. Unico explains that
DOE proposed to exclude SDHV
products from the rulemaking but
included modular blowers and electric
furnaces, resulting in a potential
conflict. Unico added that most of their
SDHV air handlers are modular in
construction. Unico also offers an addon electric furnace to provide secondary
or backup heat, but very few systems are
installed as an electric furnace. As a
result, Unico expressed uncertainty
whether this rule applies to SDHV
modular blowers and SDHV electric
furnaces. Unico provided data showing
that SDHV blowers operate at different
conditions compared to the products
proposed to be covered and cannot meet
the proposed FER levels. Ultimately,
Unico expressed concerns that this rule
could potentially eliminate many SDHV
products from the market if they are
subject to DOE’s proposed standards.
(Unico, No. 93 at pp.1–4)
In response to the comment, DOE
clarifies that the furnace fan test
procedure and the energy conservation
standards established by this final rule
do not apply to SDHV products,
including SDHV modular blowers and
electric furnaces. DOE recognizes that
these products operate at different
conditions which significantly impact
their fan performance, as compared to
the products addressed in this
rulemaking. While DOE’s regulations at
PO 00000
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10 CFR 430.2 include a definition for
‘‘small duct high velocity systems,’’ it
does not include a definition for small
duct high velocity modular blowers or
SDHV electric furnaces. Absent
clarification, DOE realizes that
confusion may result regarding which
products are and are not covered by
today’s standards. Accordingly, DOE is
adopting the following definition of
‘‘small-duct high-velocity (SDHV)
modular blower,’’ which has been
drafted to be consistent with the
existing definition of ‘‘SDHV system’’ at
10 CFR 430.2:
Small-duct high-velocity (SDHV)
modular blower means a product that:
• Meets the definition of ‘‘modular
blower,’’ as set forth in 10 CFR part 430,
subpart B, appendix AA;
• Is designed for, and produces, at
least 1.2 inches of external static
pressure when operated at the certified
air volume rate of 220–350 CFM per
rated ton of cooling in the highest
default cooling airflow-controls setting;
and
• When applied in the field, uses
high velocity room outlets generally
greater than 1,000 fpm that have less
than 6.0 square inches of free area.
Similarly, DOE is adopting a
definition for ‘‘small-duct high-velocity
(SDHV) electric furnace’’ to read as
follows:
Small-duct high-velocity (SDHV)
electric furnace means a product that:
• Meets the definition of ‘‘electric
furnace,’’ as set forth in 10 CFR 430.2;
• Is designed for, and produces, at
least 1.2 inches of external static
pressure when operated at the certified
air volume rate of 220–350 CFM per
rated ton of cooling in the highest
default cooling airflow-control setting;
and
• When applied in the field, uses
high velocity room outlets generally
greater than 1,000 fpm that have less
than 6.0 square inches of free area.
DOE has concluded that these
amendments should eliminate any
confusion associated with DOE not
addressing SDHV modular blowers and
SDHV electric furnaces in the present
rulemaking. Unico also submitted other
SDHV-related concerns, but DOE need
not discuss those issues further because
SDHV products are not addressed in
this rulemaking.
AHRI, Morrison, Goodman, Johnson
Controls, and Mortex stated that
modular blowers should be excluded
from the scope of this rulemaking.
(AHRI, No. 98 at pp. 1, 2; Morrison, No.
108 at p. 1; Goodman, No. 102 at p. 5;
Johnson Controls, No. 95 at p. 2; and
Mortex, NOPR Public Meeting
Transcript, No. 91 at pp. 78–79). AHRI,
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Morrison, and Johnson Controls
continue to advance an interpretation of
42 USC 6295(f)(4)(D) as being only
applicable to furnaces, and these
commenters argued that absent a
legislative change, DOE has exceeded its
statutory authority in terms of the
NOPR’s proposed coverage of modular
blowers. (AHRI, No. 98 at pp. 1–2;
Morrison, No. 108 at p. 1; and Johnson
Controls, No, 95 at p. 2). AHRI and
Johnson Controls added that some
modular blowers in today’s marketplace
are not designed to operate with electric
resistance heat kits, rendering the final
test procedure insufficient for these
products. (AHRI, No. 98 at pp. 1, 2; and
Johnson Controls, No. 95 at p. 3).
ASAP, et al., on the other hand,
expressed support for the inclusion of
modular blowers in the scope of
coverage. ASAP, et al. stated that they
understand that the strip heat used with
electric furnaces is often installed in the
field, which means that an ‘‘electric
furnace’’ is often sold by the
manufacturer as a ‘‘modular blower.’’
ASAP, et al. cite DOE’s finding that nonweatherized and mobile home electric
furnace/modular blower furnace fans
represent 10 percent of all furnace fan
sales. According to ASAP, et al.,
excluding modular blowers from the
scope of coverage would not only
reduce energy savings from this
rulemaking, but would also create a
loophole—i.e., manufacturers would
have an incentive to sell electric
furnaces as modular blowers (without
strip heat installed) in order to avoid
compliance with the furnace fan energy
conservation standards. (ASAP, et al.,
No. 105 at pp. 1, 2)
As stated above, DOE maintains its
interpretation that the relevant statutory
language at 42 U.S.C. 6295(f)(4)(D) is
broader in its applicability than just
furnaces, and consequently, it provides
DOE authority to cover modular blowers
in this rulemaking. These same
arguments were already addressed in
some detail in the NOPR (see 78 FR
64068, 64081 (Oct. 25, 2013)). DOE also
disagrees with the contention of AHRI
and Johnson Controls that the final test
procedure is not sufficient to address all
modular blowers. All modular blower
models of which DOE is aware can be
operated in conjunction with an electric
resistance heat kit, and commenters did
not identify any models of modular
blowers that cannot. Even assuming
arguendo that modular blowers do exist
that are not designed to operate with an
electric resistance heat kit, DOE expects
that number of such models would be
de minimis and that manufacturers
producing modular blowers that cannot
be operated in conjunction with an
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electric resistance heat kit would apply
for a waiver from the test procedure.
DOE provides more details regarding
this issue in the January 3, 2014 test
procedure final rule. 79 FR 504.
In its comments, Johnson Controls
stated that DOE’s use of the phrase
‘‘primary heat source’’ is too ambiguous,
especially when certain products might
be modified in the field. According to
Johnson Controls, DOE’s
characterizations of air handlers and
modular blowers when an air handler or
modular blower is the primary heating
source is still confusing and brings
uncertainty to the NOPR market
assessment. Johnson Controls
commented that none of the residential
air handlers, modular blowers, or
residential single-package finished good
models built by Johnson Controls
includes factory-installed electric heat
kits. Therefore, according to the
commenter, electric heat kits installed
in these products cannot be considered
to be the primary source for heat in their
applications, and so none of these
products should be included in this
rulemaking. Johnson Controls added
that while field-installed electric heat
kits are available and used frequently,
the use of field kits is outside of the air
handler or modular blower
manufacturer’s control, unlike gas
furnaces where the application is
known to usually be the primary heating
source in the vast number of situations.
(Johnson Controls, No. 95 at p. 2) NEEA,
Mortex, and Daikin agreed that the
contractor determines whether a CAC/
HP blower-coil unit with electric
resistance heat is the principal source of
heating for a residence, rendering any
such determination speculative for other
entities. (NEEA, NOPR Public Meeting
Transcript, No. 91 at pp. 64–65; Mortex,
NOPR Public Meeting Transcript, No. 91
at pp. 78–79; and Daikin, NOPR Public
Meeting Transcript, No. 91 at pp. 75–76)
Modular blowers are not a source of
heat per DOE’s definition of ‘‘modular
blower’’ as provided in 10 CFR part 430,
subpart B, appendix AA. Consequently,
the ‘‘principal heating source’’ qualifier
(per the definition of ‘‘furnace’’ at 10
CFR 430.2) does not apply to modular
blowers, so this part of the ‘‘furnace’’
definition has the effect of excluding
modular blowers from that definition.
However, the ‘‘furnace’’ definition is not
the only factor in deciding whether
modular blowers are covered in this
rulemaking, contrary to what Johnson
Controls suggests. If electric resistance
heat is added to a modular blower
product, that product no longer meets
DOE’s definition of a ‘‘modular blower.’’
Instead, DOE considers the modified
product an electric furnace, absent other
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38147
design changes. Regardless of whether
the electric resistance heat is factoryinstalled, both product variations are
covered in the final test procedure and
this energy conservation standard.
DOE recognizes that interested parties
may have trouble determining whether
a CAC/HP blower-coil unit with electric
resistance heating is considered an
electric furnace and thereby covered by
the energy conservation standards
established by this final rule. Strictly
following the DOE definition for
‘‘electric furnace’’ (which references the
DOE definition of ‘‘furnace’’) as set forth
at 10 CFR 430.2, coverage in this final
rule of a CAC/HP blower-coil with
electrical resistance heating depends on
whether the electric resistance heating
is the ‘‘principal heating source for the
residence.’’ As Johnson Controls points
out, this is not as easily determined as
for gas and oil furnaces. DOE expects
that in the significant majority of CAC/
HP blower-coil models that have electric
resistance heat, the electric resistance
heat is supplemental in nature and not
the principal heating source for the
residence. For this reason, DOE has
decided that the energy conservation
standards established by this rule will
not cover CAC/HP blower-coil units,
regardless of whether they include
electric resistance heat.
Lennox argued that including
weatherized commercial products in
this rulemaking is unrealistic and
improper. Specifically, Lennox
expressed concerns that DOE
mischaracterizes single-package
weatherized products as ‘‘residential’’
when these products are offered with a
single-phase power source. The
commenter stated that these products
are often used in commercial
applications, explaining that singlephase weatherized products are often
designed to have higher duct static
pressure capability than a traditional
residential furnace. Lennox commented
that they have single-phase belt-drive
products that are capable of operating
up to 2 inches water column external
static pressure to meet commercial duct
static requirements. According to
Lennox, BPM motors (including both
constant-torque and constant-airflow
BPM motors) typically used in
residential products cannot achieve the
high static pressures required in these
commercial installations. Therefore,
Lennox recommended that DOE should
exclude all products marked not for
residential use from standards coverage.
(Lennox, No. 100 at p. 4).
DOE recognizes that industry may
differentiate between residential
products and commercial equipment
differently than DOE. The standards
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Federal Register / Vol. 79, No. 128 / Thursday, July 3, 2014 / Rules and Regulations
established by this final rule do not
cover all single-phase, single-package
HVAC products, only single-phase
weatherized furnaces (i.e., single-phase,
single-package HVAC products that
include a ‘‘furnace’’ as defined at 10
CFR 430.2). Lennox did not identify,
and after additional research, DOE is not
aware of any weatherized gas furnace
models that operate at the static
pressures mentioned by the commenter.
DOE expects that the operating
conditions mentioned by Lennox are
typical of single-package heat pump
equipment, which is not covered by this
rule. DOE expects the number of models
covered by this rule that DOE defines as
residential but are designed and
operated in commercial applications to
be de minimis. Any manufacturer which
can substantiate its case that it would
suffer serious hardship, gross inequity,
and an unfair distribution of burdens if
required to comply with the furnace fan
standards may seek exception relief
from DOE’s Office of Hearings and
Appeals (OHA).17
ACEEE commented that if
manufacturers offered air handlers as a
separate product, without the coil, the
modified product would not be
inherently different than a modular
blower. ACEEE stated that DOE should
cover CAC/HP blower-coil units
following the same logic that DOE used
to justify covering modular blowers (i.e.,
because of their similarities to electric
furnaces). ACEEE also commented that
the DOE definition for ‘‘modular
blower’’ is confusing because, in their
experience, all (or almost all)
conventional indoor blower units—
whether furnaces, HP, or CAC—use a
separate assembly (or field-fabricated
‘plenum’) to house the coil used as the
evaporator (CAC) or evaporator and
condenser (HP). (ACEEE, No. 94 at pp.
1–2, 4).
DOE disagrees with ACEEE’s
assessment that a CAC/HP blower-coil
unit with the coil removed and an
electric furnace are equally comparable
to a modular blower. For example,
modular blowers are typically designed
to accommodate the addition of electric
resistance heating kits (after which DOE
would consider them as electric
furnaces) without modifying the
product envelope. Modular blower
envelope dimensions are similar, and in
many cases identical, to electric furnace
dimensions as a result. In addition, the
final test procedure requires an electric
resistance heat kit to be installed in
17 For information about obtaining exception
relief, see 10 CFR part 1003 (available at https://
www.ecfr.gov/cgi-bin/text-idx?SID=d95bf6ed9cd8
49253fab734656f80c2e&node=10:4.0.3.5.3
&rgn=div5).
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17:09 Jul 02, 2014
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modular blowers to produce a
temperature rise allowing for
calculation of airflow for the rating
metric, FER. The test configurations for
electric furnaces and modular blowers
are almost identical as a result. In turn,
the FER values for an electric furnace
and modular blower with no other
design difference other than the
presence of an electric resistance heat
kit are expected to be approximately
equivalent. On the other hand, the coils
typically included in CAC/HP blowercoil units are larger than heat resistance
kits. Consequently, blower-coil unit
envelope dimensions are different than
modular blower dimensions, which
impacts fan performance. CAC/HP
blower-coil unit design, as it relates to
fan performance, cannot be compared to
modular blower design for this reason.
The final test procedure does not
include methods for deriving an FER
value for CAC/HP blower-coil units.
Furthermore, the coil and envelope
dimension differences mentioned would
preclude the circulation fan
performance of a CAC/HP blower-coil
unit from being deemed equivalent to an
otherwise similarly-designed modular
blower. In addition, modular blowers
and electric furnaces are product
configurations installed in the field.
DOE doubts that a CAC/HP blower-coil
unit with the coil removed would be
offered by manufacturers or purchased
and installed in the field. Regarding the
criticism of its definition of ‘‘modular
blower,’’ DOE recognizes that the
definition for ‘‘modular blower’’ as set
forth at 10 CFR part 430, subpart B,
appendix AA may be confusing because
it does not explicitly state that a
modular blower does not include an
indoor refrigerant coil, only that it does
not provide heating or cooling. An
‘‘indoor unit,’’ on the other hand, is
defined at 10 CFR 430.2 as containing
a ‘‘coil.’’ This notice modifies the
definition of ‘‘modular blower’’ to
explicitly exclude products that contain
an indoor refrigerant coil in order to
eliminate ambiguity between the two
definitions.
ACEEE, Earthjustice, and CA IOU
stated that DOE’s decision to exclude
products such as CAC/HP and hydronic
air handlers is inappropriate and in
conflict with DOE’s interpretation of the
statutory language. These interested
parties also commented that DOE does
not provide a justification for its
decision to exclude products for which
DOE claims to have authority to set
energy conservation standards. (ACEEE,
No. 94 at pp. 1–2, 4; and CA IOU, No.
106 at pp. 1, 2) According to
Earthjustice, DOE’s decision to exclude
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Sfmt 4700
products for which it claims authority to
cover represents a failure to carry out
EPCA’s command to adopt ‘‘standards
for electricity used for purposes of
circulating air through ductwork’’ and
does not comply with the statute’s
requirement that standards ‘‘shall be
designed to achieve the maximum
improvement in energy efficiency’’ that
is ‘‘technologically feasible and
economically justified.’’ (42 U.S.C.
6295(o)(2)(A). Earthjustice adds that
EPCA authorizes DOE not to prescribe
an amended or new standard for a type
or class of covered product in three
situations: (1) The standard will
eliminate certain product features from
the market; (2) the standard will not
result in significant conservation of
energy or is not technologically feasible
or economically justified; or (3) for
certain products, test procedures have
not been established. (42 U.S.C.
6295(o)(3) and (4)). Earthjustice states
that DOE has failed to show that the
products it is not addressing in this rule
meet those criteria. (Earthjustice, No.
101 at p. 1).
ASAP, et al. encouraged DOE to adopt
standards and/or test procedure changes
to drive improved efficiency of furnace
fans that are part of single-package and
blower-coil central air conditioners and
heat pumps in the future. According to
ASAP, et al., CA IOU and ACEEE, the
operating conditions and metrics used
in the DOE test procedures for CAC/HP
(i.e., SEER and HSPF) are insufficient
for representing furnace fan
performance in the field for those
products. (ASAP, et al., No. 105 at pp.
2, 3; CA IOU, No. 106 at pp. 1, 2; and
ACEEE, No. 94 at pp. 1–2, 4). Further,
ASAP, et al. are concerned that heat
pump indoor units will increasingly be
installed and operated as electric
furnaces (without an outdoor unit) to
avoid both the DOE standard for CAC/
HP and the standards established by this
rule. ASAP, et al. added that consumers
will have greater incentive to install
heat pump indoor units to operate as
electric furnaces if a heat pump indoor
unit with a PSC motor is less expensive
than an electric furnace/modular blower
with a constant-torque BPM motor.
(ASAP, et al., No. 105 at pp. 2, 3)
Earthjustice also identified CAC/HP
blower-coil units installed without an
outdoor unit and operated as an electric
furnace as a potential loophole.
(Earthjustice, No. 101 at p. 1) While
ASAP, et al., stated that they recognize
that it may be too late to include furnace
fans that are part of single-package and
blower-coil central air conditioners and
heat pumps in the scope of coverage in
the current rulemaking, they encourage
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DOE to address furnace fan efficiency in
these products in the future through one
of two options: (1) Amend the test
procedures for central air conditioners
and heat pumps to incorporate more
realistic external static pressure values;
or (2) include furnace fans that are part
of single-package and blower-coil
central air conditioners and heat pumps
in a future rulemaking for furnace fans.
ASAP, et al., submitted that if DOE
pursued the second option, changing
the external static pressure values in the
central air conditioner and heat pump
test procedures would be less critical,
because fan efficiency would be
addressed through standards for furnace
fans. (ASAP, et al., No. 105 at pp. 2, 3)
CA IOU also expressed support for a
separate, expedited rulemaking to set
energy conservation standards for
products not addressed in this rule. CA
IOU claims that such a rule would
ensure that the entire market for furnace
fans is regulated, thereby avoiding the
negative market impacts due to the
prevalence of unregulated products. (CA
IOU, No. 106 at pp. 1, 2). NEEA and
NPCC also expressed disappointment
that DOE is choosing to cover only twothirds of furnace fan products by
excluding indoor blower/cool units
used with split system heat pump and
air conditioning systems and hydronic
air handlers, which leaves substantial
energy savings on the table. (NEEA and
NPCC, No. 96 at p. 3). ACEEE estimated
that approximately two quads of
potential cumulative energy savings are
left uncaptured by DOE’s decision to
exclude CAC/HP blower-coil units,
which ACEEE claims could jeopardize
achievement of the Administration’s
goal of 3 billion tons of CO2 avoided.
(ACEEE, No. 94 at p. 1–2, 4). CA IOU
cited these potential energy savings as
another reason that a separate,
expedited rulemaking is warranted. (CA
IOU, No. 106 at pp. 1, 2). Laclede,
APGA, and AGA also recommended
that DOE expand the scope of this rule
to include products such as split-system
central air conditioners, heat pump air
handlers, through-the-wall air handlers,
and small-duct high-velocity air
handlers that compete with the types of
natural gas furnaces covered by this
rules. Each cited concerns that DOE’s
decision to exclude fans used in these
products could lead to fuel switching.
(Laclede, No. 89 at p. 2; APGA, No. 90
at p. 2; and AGA, No. 110 at p. 2).
Laclede believes the Department failed
to adequately explain why fans in heat
pumps are excluded and to clearly
demonstrate how this exclusion serves
the best interests of the American
public.
EEI, on the other hand, supports
DOE’s exclusion of CAC/HP blowercoils and hydronic air handlers from
this rulemaking. EEI commented that
the energy used by the fans operating in
the cooling mode is part of the
calculation of SEER, EER, and HSPF.
EEI explains that manufacturers have
already made design decisions that
reduce the energy usage of such fans for
these systems to meet the higher air
conditioner and heat pump energy
conservation standards (based on SEER
and HSPF) that took effect in 1992 and
2006, and will take effect in 2015. EEI
stated that including these fans in this
rule would be a form of ‘‘double
regulation’’ of the same product. (EEI,
No. 87 at p. 3) Southern Company
agreed that CAC/HP fan energy is
already covered by the SEER and HSPF
rating. (Southern Company, NOPR
Public Meeting, No. 43 at p. 70).
38149
As explained previously, DOE has
noted the relatively broad scope of the
language of 42 U.S.C. 6295(f)(4)(D),
which provides DOE authority to
regulate ‘‘electricity used for purposes
of circulating air through duct work.’’ At
the present time, however, DOE is only
adopting energy conservation standards
for those circulation fans that are used
in residential furnaces and modular
blowers. The DOE test procedure for
furnace fans is not currently equipped
to address fans contained in central air
conditioners, heat pumps, or other
products, as would be required for the
adoption of standards under 42 U.S.C.
6295(o)(3). Consequently, DOE is not
considering standard setting for other
products beyond the current scope of
the rulemaking at this time.
2. Product Classes
DOE identified nine key product
classes in the preliminary analysis, each
of which was assigned its own
candidate energy conservation standard
and baseline FER. DOE identified
twelve additional product classes that
represent significantly fewer shipments
and significantly less overall energy use.
DOE grouped each non-key product
class with a key product class to which
it is closely related in applicationspecific design and internal structure
(i.e., the primary criteria used to
differentiate between product classes).
DOE assigned the analytical results of
each key product class to the non-key
product classes with which it is grouped
because DOE expected the energy use
and incremental manufacturer
production costs (MPCs) of improving
efficiency to be similar within each
grouping. Table IV.1 lists the 21
preliminary analysis product classes.
TABLE IV.1—PRELIMINARY ANALYSIS PRODUCT CLASSES
Key product class
Additional product classes
Non-Weatherized, Non-Condensing Gas Furnace Fan (NWG–NC).
Non-weatherized, Condensing Gas Furnace Fan (NWG–C).
Weatherized Non-Condensing Gas Furnace Fan (WG–NC) ...................
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Non-weatherized, Non-Condensing Oil Furnace Fan (NWO–NC) ..........
Weatherized, Non-Condensing Oil Furnace Fan (WO–NC).
Weatherized Electric Furnace/Modular Blower Fan (WEF/WMB).
Mobile Home Weatherized Gas Furnace Fan (MH–WG).
Mobile Home Weatherized Oil Furnace Fan (MH–WO).
Mobile Home Weatherized Electric Furnace/Modular Blower Fan (MH–
WEF/WMB).
Non-Weatherized, Condensing Oil Furnace Fan (NWO–C).
Mobile Home Non-Weatherized Oil Furnace Fan (MH–NWO).
Non-weatherized Electric Furnace/Modular Blower Fan (NWEF/NWMB).
Heat/Cool Hydronic Air Handler Fan (HAH–HC) ..................................... Heat-Only Hydronic Air Handler Fan (HAH–H).
Hydronic Air Handler Fan with Coil (HAH–C).
Mobile Home Heat/Cool Hydronic Air Handler Fan (MH–HAH–HC).
Mobile Home Heat-Only Hydronic Air Handler Fan (MH–HAH–H).
Mobile Home Hydronic Air Handler Fan with Coil (MH–HAH–C).
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan
(MH–NWG–NC).
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TABLE IV.1—PRELIMINARY ANALYSIS PRODUCT CLASSES—Continued
Key product class
Additional product classes
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan (MH–
NWG–C).
Mobile Home Electric Furnace/Modular Blower Fan (MH–EF/MB).
Manufacturers agreed that the
selected key product classes are an
accurate representation of the market.
Some manufacturers disagreed with
DOE’s approach to specify additional
product classes within a key product
class, stating that shipment data
indicates that the additional product
classes are too small to be covered.
In the NOPR, DOE agreed with
manufacturers’ assertion that the
additional non-key product classes
represent products with few and in
many cases, no shipments. 78 FR 64082.
Individual discussions with
manufacturers for the MIA confirmed
this assertion. Additionally, review of
the AHRI appliance directory revealed
that only two of the additional non-key
product classes have active models
listed: (1) Mobile home weatherized gas
furnace fans (MH–WG) and (2) mobile
home non-weatherized oil furnace fans
(MH–NWO). The number of active basic
models for MH–WG and MH–NWO are
4 and 16, respectively. For this reason,
DOE proposed in the NOPR to eliminate
the additional non-key product classes
except for MH–WG and MH–NWO. Due
to the limited number of basic models
for MH–WG and MH–NWO, DOE did
not have data to directly analyze and
establish standards for these additional
product classes. As a result, DOE
proposed to reserve space to establish
standards for MH–WG and MH–NWO
furnace fans in the future as sufficient
data become available. DOE also
proposed to exclude hydronic air
handlers from consideration in this
rulemaking, thereby further reducing
the number of product classes addressed
in the NOPR to 10. 78 FR 64082. Table
IV.2 includes a list of the revised set of
product classes for residential furnace
fans used in the NOPR.
DOE did not receive comment or
additional information on the proposed
product classes, thus, DOE is not
making changes to the product classes
in this Final Rule. Table IV.2 includes
a list of the product classes for
residential furnace fans used in the
Final Rule.
TABLE IV.2—PRODUCT CLASSES FOR RESIDENTIAL FURNACE FANS
Product class
Non-Weatherized, Non-Condensing Gas Furnace Fan (NWG–NC)
Non-Weatherized, Condensing Gas Furnace Fan (NWG–C)
Weatherized Non-Condensing Gas Furnace Fan (WG–NC)
Non-Weatherized, Non-Condensing Oil Furnace Fan (NWO–NC)
Non-Weatherized Electric Furnace/Modular Blower Fan (NWEF/NWMB)
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan (MH–NWG–NC)
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan (MH–NWG–C)
Mobile Home Electric Furnace/Modular Blower Fan (MH–EF/MB)
Mobile Home Weatherized Gas Furnace Fan (MH–WG)
Mobile Home Non-Weatherized Oil Furnace Fan (MH–NWO)
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3. Technology Options
In the preliminary analysis, DOE
considered seven technology options
that would be expected to improve the
energy efficiency of furnace fans: (1) Fan
housing and airflow path design
modifications; (2) high-efficiency fan
motors (in some cases paired with
multi-stage or modulating heating
controls); (3) inverter-driven permanentsplit capacitor (PSC) fan motors; (4)
backward-inclined impellers; (5)
constant-airflow brushless permanent
magnet (BPM) motor control relays; (6)
toroidal transformers; and (7) switching
mode power supplies. In the NOPR,
DOE revised its proposed scope of
coverage to no longer address hydronic
air handlers, the only furnace fan
product class for which standby mode
and off mode energy consumption is not
already fully accounted for in the DOE
energy conservation standards
rulemakings for residential furnaces and
residential CAC and HPs. 76 FR 37408
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(June 27, 2011); 76 FR 67037 (Oct. 31,
2011). Consequently, the standby mode
and off mode technology options
(options 5 through 7 in the list above)
are no longer applicable. In addition,
DOE found that multi-staging and
modulating heating controls can also
improve FER, so DOE evaluated multistaging and modulating heating controls
as a separate technology option for the
NOPR. 78 FR 64083.
DOE did not receive comment or
additional information regarding the
evaluated technology options, so DOE
did not make any changes to the list of
technology options identified in the
NOPR. The resultant list of technology
options identified to be evaluated in the
screening analysis before consideration
in the engineering analysis for the Final
Rule include: (1) Fan housing and
airflow path design modifications; (2)
inverter-driven PSC fan motors; (3)
high-efficiency fan motors; (4) multistaging and modulating heating
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controls; and (5) backward-inclined
impellers. Each identified technology
option is discussed below and in more
detail in chapter 3 of the Final Rule
TSD.
Fan Housing and Airflow Path Design
Improvements
The preliminary analysis identified
fan housing and airflow path design
modifications as potential technology
options for improving the energy
efficiency of furnace fans. Optimizing
the shape of the inlet cone 18 of the fan
housing, minimizing gaps between the
impeller and fan housing inlet, and
optimizing cut-off location and
manufacturing tolerances were
identified as enhancements to a fan
18 The inlet cone is the opening of the furnace fan
housing through which return air enters the
housing. The inlet cone is typically curved inward,
forming a cone-like shape around the perimeter of
the opening, to provide a smooth surface to direct
air from outside the housing to inside the housing
and into the impeller.
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housing that could improve efficiency.
Separately, modification of elements in
the airflow path, such as the heat
exchanger, could reduce internal static
pressure and as a result, reduce energy
consumption. Manufacturer input was
requested to determine the use and
practicability of these potential
technology options.
Interested parties expressed support
for DOE’s consideration of the
aerodynamics of furnace fan cabinets in
its initial analysis of technology options.
In particular, ASAP cited a 2003 GE
study 19 that quantified energy savings
produced by modifying fan housing as
justification for its inclusion as an
option. ACEEE, et al. also cited a
Lawrence Berkeley National Laboratory
(LBNL) study 20 that linked changes in
efficiency to modifying the clearance
between fan housing and an air handler
cabinet wall. Ingersoll Rand stated that
there are proprietary fan housing
designs on the market that already
improve mechanical efficiency by 10–20
percent at a cost much lower than the
cost to implement high-efficiency
motors or make changes to the impeller
and its tolerances. 78 FR 64083.
DOE is aware of the studies cited by
ASAP and ACEEE, as well as the
proprietary housing design mentioned
by Ingersoll Rand. For the NOPR, DOE
decided to include fan housing design
modifications as a technology to be
evaluated further in the screening
analysis because of these indications
that each could improve fan efficiency.
78 FR 64083.
Many interested parties requested that
DOE keep airflow path design as a
technology option. Manufacturers stated
that improving airflow path design, like
modifying fan housing, is highly costeffective when compared to other
enhancements. Similar to the fan
housing design modifications, DOE
decided to include airflow path design
as a technology option to be evaluated
further in the screening analysis as a
result of these claims of potential fan
efficiency improvement. 78 FR 64083.
DOE believes including airflow path
design is appropriate because of its
potential to impact fan efficiency.
Airflow path design will impact the
rating metric, FER, because the DOE test
procedure requires the furnace fan to be
tested as it is factory-installed in the
HVAC product.
19 Wiegman, Herman, Final Report for the
Variable Speed Integrated Intelligent HVAC Blower
(2003) (Available at: https://www.osti.gov/bridge/
servlets/purl/835010-GyvYDi/native/835010.pdf).
20 Walker, I.S, State-of-the-art in Residential and
Small Commercial Air Handler Performance (2005)
LBNL 57330 (Available at: https://epb.lbl.gov/
publications/pdf/lbnl-57330plus.pdf).
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DOE did not receive comment or
additional information on fan housing
about including airflow path design
improvements as a technology option,
thus, DOE is including these as
technologies to be evaluated further in
the screening analysis. Chapter 3 of the
Final Rule TSD provides more technical
detail regarding fan housing and airflow
path design modifications and how
these measures could reduce furnace fan
energy consumption.
Inverter Controls for PSC Motors
In the preliminary analysis, DOE
identified inverter-driven PSC motors as
a technology option. DOE is aware of a
series of non-weatherized gas furnaces
with inverter-driven PSC furnace fan
motors that was once commercially
available. DOE has determined that
inverter controls provide efficiency
improvement by offering additional
intermediate airflow-control settings
and a wider range of airflow-control
settings (i.e., lower turndown ratio) than
conventional PSC controls. The
additional airflow-control settings and
range enable the furnace fan to better
match demand. Publically-available
performance data for the series of
furnaces using inverter-driven PSCs
demonstrate that the use of this
technology results in reduced FER
values compared to baseline PSC
furnace fans. Consequently, DOE
considered inverter-driven PSCs as a
technologically feasible option for
reducing furnace fan energy
consumption.
Manufacturers were opposed to listing
inverter-driven PSCs as a viable
technology option. Manufacturers
commented that there are alternate,
more cost-effective solutions to reduce
energy consumption for air-moving
systems, such as airflow path design or
ECM (referred to herein by DOE as a
‘‘constant-airflow BPM motor’’)
technology. 78 FR 64084.
For the NOPR analysis, DOE
recognized manufacturers’ concerns
with the cost-effectiveness of inverterdriven PSC fan motors. However, DOE
decided to include inverter-driven PSC
motors as a technology option to be
evaluated further in the screening
analysis due to their potential to reduce
furnace fan energy consumption. 78 FR
64084.
DOE did not receive comment or
additional information on including
inverter controls for PSC motors as a
technology option, thus, DOE is
including this technology option in the
Final Rule. DOE evaluates in the
engineering analysis the costeffectiveness of all energy-saving
technology options that are not screened
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out. Chapter 3 of the Final Rule TSD
provides a more detailed discussion of
inverter-driven PSC furnace fan motors.
High-Efficiency Motors
In the preliminary analysis, DOE
identified four motor types that are
typically used in furnace fan assemblies:
(1) PSC motors; (2) PSC motors that
have more than 3 airflow-control
settings and sometimes improved
materials (hereinafter referred to as
‘‘improved PSC’’ motors); (3) constanttorque BPM motors (often referred to as
‘‘X13 motors’’); and (4) constant-airflow
BPM motors (often referred to as
‘‘ECMs’’).21 DOE finds that furnace fans
using high-efficiency motor technology
options operate more efficiently than
furnace fans using baseline PSC motors
by:
• Functioning more efficiently at a
given operating condition;
• Maintaining efficiency throughout
the expected operating range; and
• Achieving a lower turndown ratio 22
(i.e., ratio of airflow in lowest setting to
airflow in highest setting).
Ingersoll Rand commented that a PSC
motor will use less energy at higher
static pressures, while an ECM increases
energy use as static pressure rises.
Ingersoll Rand stated that as a result,
understanding the impact of switching
to an ECM at higher static pressures may
confuse the consumer. (Ingersoll Rand,
PA Public Meeting Transcript, No. 43 at
p. 67)
For the NOPR analysis, DOE stated
that it is aware that consumers may be
confused when BPM motors (referred to
as ECMs by Ingersoll Rand above)
consume more energy than PSC motors
at higher static pressures, because
consumers expect BPM motors to
consume less energy than PSC motors
under the same operating conditions. In
general, input power to the fan motor
increases as static pressure increases to
provide a given airflow (i.e., the fan
motor has to work harder in the face of
increased resistance to provide a desired
amount of air).23 DOE agreed with
Ingersoll Rand that as static pressure
increases, input power to a PSC-driven
furnace fan will decrease, which is
21 ‘‘ECM’’ and ‘‘X13’’ refer to the constant-airflow
and constant torque (respectively) BPM offerings of
a specific motor manufacturer. Throughout this
notice, DOE will refer to these technologies using
generic terms, which are introduced in the list
above. However, DOE’s summaries of interestedparty submitted comments include the terminology
used by the interested party when referring to motor
technologies.
22 A lower turndown ratio can significantly
improve furnace fan efficiency because fan input
power has a cubic relationship with airflow.
23 See chapter 3 of the TSD for more details
regarding fan operation.
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seemingly contradictory to the principle
described above. DOE found that input
power to a PSC-driven furnace fan
decreases because the airflow provided
by the fan decreases as static pressure
rises (i.e., the fan does not have to work
as hard in the face of increased
resistance because the fan is not
providing as much air). 78 FR 64084.
Input power to a constant-airflow BPM
motor-driven furnace fan, on the other
hand, will increase as static pressure
rises because the BPM motor-driven fan
is designed to maintain the desired level
As detailed in the NOPR, interested
parties recognized the benefits provided
by constant-torque and constant-airflow
BPM motors. Interested parties also
agreed that the BPM motor variations
(i.e., constant-torque and constantairflow) and inverter-driven PSC motors
generally have lower turndown ratios
than a three-speed PSC motor. 78 FR
64084. Table IV.3 contains the
turndown ratio estimates supplied
publicly by interested parties.
Manufacturers generally provided
similar feedback during interviews.
of airflow. Recognizing that this
behavior could complicate comparing
the relative performance of these motor
technologies, DOE’s rating metric, FER,
is normalized by airflow to result in
ratings that are in units of watts/cfm.
DOE believed that a comparison using a
watts/cfm metric will mitigate
confusion by accurately reflecting that
even though a constant-airflow BPM
motor is consuming more power at
higher statics, it is also providing more
airflow, which is useful to the
consumer.
TABLE IV.3—INTERESTED PARTY ESTIMATED FAN MOTOR TURNDOWN RATIOS
PSC
Interested party
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NMC (NMC, No. 60 at p. 1) .............................................................................
Goodman (Goodman, No. 50 at p. 2) .............................................................
Rheem (Rheem, No. 54 at p. 6) ......................................................................
Overall, comments regarding highefficiency motor turndown ratio
validated DOE’s expectation that lower
turndowns are associated with
improved PSCs, inverter-driven PSCs,
and BPM motor variations. These
motors consume significantly less
energy over a typical residential furnace
fan operating range. DOE disagreed with
Lennox that including constant
circulation as part of FER would
‘‘artificially’’ inflate the performance of
BPM motors compared to PSC motors,
because DOE concluded that there is
non-trivial use of this mode by
consumers. 78 FR 64085. As part of the
test procedure rulemaking, DOE
estimated that on average, consumers
operate furnace fans in constantcirculation mode 400 hours annually.
This estimate is used to weight fan
constant-circulation electrical energy
consumption in FER. Excluding this
mode from the rating metric would
underestimate the potential efficiency
improvements of technology options,
such as BPM motors, that could reduce
fan electrical consumption while
performing this function. A detailed
discussion of DOE’s estimate for
national average constant-circulation
furnace fan operating hours can be
found in the test procedure NOPR. 77
FR 28674, 28682 (May 15, 2012). DOE
did not revise these estimates in the test
procedure Final Rule published on
January 3, 2014. 79 FR 499.
DOE did not receive comment or
additional information on including
high-efficiency motors as a technology
option, thus, DOE is including this
technology option in the Final Rule.
DOE evaluates in the engineering
analysis the cost-effectiveness of all
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Wave chopper
controller PSC
0.45
0.70–0.75
0.60
0.36
........................
........................
energy-saving technology options that
are not screened out. Chapter 3 of the
Final Rule TSD provides a more
detailed discussion of high-efficiency
furnace fan motors.
Multi-Stage or Modulating Heating
Controls
In the preliminary analysis (77 FR
40530 (July 10, 2012)), DOE identified
two-stage and modulating heating
controls (hereinafter collectively
referred to as ‘‘multi-stage’’ controls) as
a method of reducing residential furnace
fan energy consumption. Multi-stage
furnaces typically operate at lower heat
input rates and, in turn, a lower airflowcontrol setting for extended periods of
time compared to single-stage furnaces
to heat a residence.24 Due to the cubic
relationship between fan input power
and airflow, operating at the reduced
airflow-control setting reduces overall
fan electrical energy consumption for
heating despite the extended hours. In
the preliminary analysis, DOE analyzed
multi-staging controls paired with use of
a constant-airflow BPM fan motor as one
technology option, because DOE found
the two to be almost exclusively used
together in commercially-available
products.
Interested parties encouraged DOE to
consider X13-level motors applied with
multi-stage furnace controls as a
technology option. 78 FR 64085. During
interviews, manufacturers commented
24 A further discussion of multi-stage heating
controls is found in chapter 3 of the preliminary
analysis TSD, which can be found at the following
web address: https://www.regulations.gov/
#!documentDetail;D=EERE-2010-BT-STD-00110037.
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Constanttorque ECM
0.45
0.40–0.50
0.30
Constantairflow ECM
0.20
0.25–0.35
0.20
that multi-stage heating controls can be
and are used regardless of motor type.
Based on comments from
manufacturers, DOE recognized that
multi-stage controls can be paired with
other motor types, not just constantairflow BPM motors. DOE agreed with
interested parties that implementing
multi-stage heating controls
independent of motor type could result
in residential furnace fan efficiency
improvements. Consequently, DOE
decided to de-couple multi-staging
controls from the constant-airflow BPM
motor technology option. Accordingly,
DOE evaluated multi-staging controls as
a separate technology option for the
NOPR. 78 FR 64085.
DOE did not receive comment or
additional information on multi-staging
controls as a technology option, thus,
DOE is including this technology option
in the Final Rule.
Backward-Inclined Impellers
DOE determined in the preliminary
analysis that using backward-inclined
impellers could lead to possible
residential furnace fan energy savings.
Although limited commercial data
regarding backward-inclined impeller
performance were available, DOE cited
research by General Electric (GE) that
showed large improvements in
efficiency were achievable under certain
operating conditions.25
Interested parties disagreed with the
DOE’s findings, stating that literature
indicates there are varying degrees of
performance improvement when
25 Wiegman, Herman, Final Report for the
Variable Speed Integrated Intelligent HVAC Blower
(2003) (Available at: https://www.osti.gov/bridge/
servlets/purl/835010-GyvYDi/native/835010.pdf).
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backward-inclined impellers are used in
place of forward-curved impellers. 78
FR 64085. Ebm-papst, a company that
provides custom air-movement
products, offered a diverging opinion
from most manufacturers regarding the
energy-saving potential of backwardinclined impellers. That company
retrofitted several HVAC products with
furnace fan assemblies that incorporated
backward-inclined impellers without
increasing cabinet size and tested them.
Depending on the application and the
external static pressure load (typically
0.5 in. w.c. to 1 in. w.c.), ebm-papst
found that the backward-inclined
impeller achieved input power
reductions from 15–30 percent. (ebmpapst Inc., No. 52 at p. 1).
DOE recognized that backwardinclined impellers may not be more
efficient than forward-curved impellers
under all operating conditions and that
there may be considerable constraints to
implementation. However, the GE
prototype and ebm-papst prototype both
demonstrate that significant energy
consumption reduction is achievable at
some points within the range of
residential furnace fan operation. For
this reason, DOE included backwardinclined impellers as a technology
option in the NOPR. 78 FR 64086.
DOE did not receive additional
comment or information on including
backward-inclined impellers as a
technology option. Thus, DOE included
backward-inclined impellers as a
technology to be evaluated further in the
screening analysis for the Final Rule.
B. Screening Analysis
DOE uses the following four screening
criteria to determine which technology
options are suitable for further
consideration in an energy conservation
standards rulemaking:
1. Technological feasibility.
Technologies that are not incorporated
in commercial products or in working
prototypes will not be considered
further.
2. Practicability to manufacture,
install, and service. If it is determined
that mass production and reliable
installation and servicing of a
technology in commercial products
could not be achieved on the scale
necessary to serve the relevant market at
the time of the compliance date of the
standard, then that technology will not
be considered further.
3. Impacts on product utility or
product availability. If it is determined
that a technology would have significant
adverse impact on the utility of the
product to significant subgroups of
consumers or would result in the
unavailability of any covered product
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type with performance characteristics
(including reliability), features, sizes,
capacities, and volumes that are
substantially the same as products
generally available in the United States
at the time, it will not be considered
further.
4. Adverse impacts on health or
safety. If it is determined that a
technology would have significant
adverse impacts on health or safety, it
will not be considered further.
(10 CFR part 430, subpart C, appendix
A, 4(a)(4) and 5(b))
In sum, if DOE determines that a
technology, or a combination of
technologies, fails to meet one or more
of the above four criteria, it will be
screened out from further consideration
in the engineering analysis. The reasons
for eliminating any technology are
discussed below.
The subsequent sections include
comments from interested parties
pertinent to the screening criteria,
DOE’s evaluation of each technology
option against the screening analysis
criteria, and whether DOE determined
that a technology option should be
excluded (‘‘screened out’’) based on the
screening criteria.
discussion with manufacturers, DOE
was not able to identify a case in which
fan housing or airflow path design
modifications could lead to potential
fan energy savings without increasing
the size of the HVAC product or
compromising thermal performance or
safety. DOE is aware of the impacts on
thermal efficiency and furnace fan
performance of the additional heat
exchanger in condensing furnaces. As
discussed in section III.B, DOE
accounted for these impacts in its
criteria for differentiating product
classes. In addition, DOE concurs with
manufacturers’ observations that an
increase in envelope size would
adversely impact practicability to
manufacture and install, as well as
product utility. Accordingly, DOE
decided to screen out fan housing and
airflow path design modifications in the
NOPR. 78 FR 64086.
DOE did not receive additional
comment or information regarding fan
housing and airflow path design
modifications in response to the NOPR.
Thus, DOE determined to screen out fan
housing and airflow path design
modifications in the Final Rule.
1. Screened-Out Technologies
Through a review of each technology,
DOE found that all of the other
identified technologies met all four
screening criteria to be examined further
in DOE’s analysis. 78 FR 64087. In
summary, DOE did not screen out the
following technology options: (1)
Inverter-driven PSC fan motors; (2)
high-efficiency fan motors; (3) multistage heating controls; and (4)
backward-inclined impellers. DOE
understands that all of these technology
options are technologically feasible,
given that the evaluated technologies
are being used (or have been used) in
commercially-available products or
working prototypes. These technologies
all incorporate materials and
components that are commercially
available in today’s supply markets for
the residential furnace fans that are the
subject of this Final Rule. Therefore,
DOE believes all of the efficiency levels
evaluated in this notice are
technologically feasible. For additional
details, please see chapter 4 of the Final
Rule TSD.
Interested parties, however, voiced
concerns regarding these screening
criteria as they apply to BPM fan motors
and backward-inclined impellers in
previous phases of this rulemaking.
DOE summarizes and addresses these
concerns in the sections immediately
below. DOE did not receive public
comments relevant to the screening
DOE screened out fan housing and
airflow path design improvements in
the preliminary analysis. DOE had little
quantitative data to correlate specific
fan housing alterations with efficiency
improvements. Additionally, DOE
anticipated that any improvements to
airflow path design that would result in
fan efficiency improvement would
require an increase in furnace fan
cabinet size or negatively impact heat
exchanger performance, thereby
compromising the practicability to
manufacture or reducing utility to
consumers.
In response to the preliminary
analysis, interested parties stated many
concerns associated with modifying
airflow path designs to reduce
residential furnace fan electrical energy
consumption, namely, that airflow path
design modifications would likely
require increasing HVAC product size.
Manufacturers explained that increasing
HVAC products size would have
adverse impacts on practicability to
install and consumer utility, because the
furnace fan market is predominantly a
replacement market. 78 FR 64086.
For the NOPR, DOE did not receive or
find additional quantitative data that
shows a measurable increase in fan
efficiency as a result of a specific fan
housing or airflow path design
modification. Even after individual
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analysis criteria for the other remaining
technology options.
High-Efficiency Motors
In response to the preliminary
analysis, manufacturers stated that there
are a limited number of ECM motor
suppliers to furnace fan manufacturers,
and that it is a proprietary technology.
Manufacturers also stated that no
alternative ECM exists at the scale of
Regal Beloit ECMs and that limiting PSC
applicability would reduce product
flexibility.
Motor manufacturers disagreed with
residential furnace fan manufacturers,
claiming that there is more than just a
single motor manufacturer offering ECM
technology. Motor manufacturers also
supported DOE’s assumption that after
implementation of furnace fan
efficiency standards, brushless
permanent magnet motor technologies
will become increasingly available over
time. DOE discovered during interviews
with manufacturers that there are
multiple suppliers of BPM motors. DOE
also found further evidence that some
manufacturers purchase BPM motors
from multiple suppliers. EEI stated that
the expiration of Regal Beloit ECM
patents around 2020 may increase the
availability of this motor type while
decreasing cost. (EEI, PA Public Meeting
Transcript, No. 43 at p. 127)
In the preliminary analysis, DOE
requested comment as to whether
manufacturers could alternatively
develop BPM motor controls in-house
when using high-efficiency motors from
other, non-Regal Beloit, suppliers. Most
furnace fan manufacturers claimed that
development of in-house controls for
BPM motors is not an option. 78 FR
64087.
While DOE recognizes that Regal
Beloit possesses a number of patents in
the BPM motor space, other motor
manufacturers (e.g., Broad Ocean, ebmpapbst, and NMC) also offer BPM
models. Additionally, DOE is aware that
in years past, residential furnace fans
paired with constant-airflow BPM
motors accounted for 30 percent of the
market. While DOE estimates that
constant-airflow BPM motors represent
only 10–15 percent of the current
furnace fan market, the manufacturing
capability to meet BPM motor demand
exists. Thus, DOE continues to expect
that BPM motor technology is currently
available from more than one source
and will become increasingly available
to residential furnace fan manufacturers.
78 FR 64087.
Also in response to the preliminary
analysis, some fan manufacturers
expressed concern that high-efficiency
motor reliance on rare earth metals
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would impact supply. However, DOE is
aware of high-efficiency motors that do
not contain rare earth materials. DOE is
also confident, after discussions with
manufacturers, that if BPM motors are
adopted as a means to meet a future
residential furnace fan energy
conservation standard, manufacturers
would have a number of cost- and
performance-competitive suppliers from
which to choose who have available, or
could rapidly develop, control systems
independently of the motor
manufacturer. 78 FR 64087.
DOE did not receive additional
comment or information in response to
the NOPR about high-efficiency motors
related to the screening criteria. Thus
DOE included high-efficiency motors as
a technology option in the engineering
analysis.
Backward-Inclined Impellers
In response to the preliminary
analysis, furnace fan manufacturers
stated that backward-inclined impellers
must have larger diameter and operate
at higher speed than forward-curve
impellors in order to attain equivalent
performance (i.e., flow and pressure
rise). However, ebm-papst stated that
they retrofitted existing equipment with
backward-inclined impellers, which
only required making minor changes to
the airflow path within the equipment.
78 FR 64088.
Manufacturers were also concerned
with the potential impacts that
backward-inclined impellers could have
on heat exchanger temperatures. Some
commenters also argued that backwardinclined impellers may affect furnace
fan utility, because the noise produced
by this impeller type may limit product
application. Utilities claimed that a
backward-inclined impeller, in
combination with increased fan motor
speeds to achieve higher efficiency,
leads to amplified noise levels. 78 FR
64088.
For the NOPR, DOE found that there
are multiple approaches to
implementing backward-inclined
impellers to reduce furnace fan energy
consumption. DOE recognized that one
approach is to use a backward-inclined
impeller that is larger than a standard
forward-curved impeller, which may
lead to larger HVAC products. Another
approach is to pair the backwardinclined impeller with a motor that
operates at increased RPM. Ebm-papst
tests show a significant potential to
reduce fan electrical energy
consumption for a backward-inclined
impeller assembly that uses existing
motor technology at higher RPMs and is
implemented in existing HVAC
products (i.e., no increase in product
PO 00000
Frm 00026
Fmt 4701
Sfmt 4700
size required). Ebm-papst does not
believe that achieving higher RPMs with
existing motor technology is an obstacle
for implementing this technology. DOE
believed that this prototype represented
a backward-inclined implementation
approach that could achieve fan energy
savings while avoiding the negative
impacts listed by manufacturers.
Consequently, DOE decided not to
screen out the backward-inclined
impeller technology option in the
NOPR. 78 FR 64088.
DOE did not receive additional
comment or information about
backward-inclined impellers related to
the screening criteria. Thus, DOE
decided not to screen out backwardinclined impellers in the Final Rule.
C. Engineering Analysis
In the engineering analysis
(corresponding to chapter 5 of the Final
Rule TSD), DOE establishes the
relationship between the manufacturer
selling price (MSP) and improved
residential furnace fan efficiency. This
relationship serves as the basis for costbenefit calculations for individual
consumers, manufacturers, and the
Nation. DOE typically structures the
engineering analysis using one of three
approaches: (1) Design option; (2)
efficiency level; or (3) reverse
engineering (or cost-assessment). The
design-option approach involves adding
the estimated cost and efficiency of
various efficiency-improving design
changes to the baseline to model
different levels of efficiency. The
efficiency-level approach uses estimates
of cost and efficiency at discrete levels
of efficiency from publicly-available
information, and information gathered
in manufacturer interviews that is
supplemented and verified through
technology reviews. The reverse
engineering approach involves testing
products for efficiency and determining
cost from a detailed bill of materials
derived from reverse engineering
representative products. The efficiency
values range from that of a least-efficient
furnace fan sold today (i.e., the baseline)
to the maximum technologically feasible
efficiency level. For each efficiency
level examined, DOE determines the
MSP; this relationship is referred to as
a cost-efficiency curve.
1. Efficiency Levels
In this rulemaking, DOE used an
efficiency-level approach in conjunction
with a design-option approach to
identify incremental improvements in
efficiency for each product class. An
efficiency-level approach enabled DOE
to identify incremental improvements in
efficiency for efficiency-improving
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technologies that furnace fan
manufacturers already incorporate in
commercially-available models. A
design-option approach enabled DOE to
model incremental improvements in
efficiency for technologies that are not
commercially available in residential
furnace fan applications. In combination
with these approaches, DOE used a costassessment approach to determine the
manufacturing production cost (MPC) at
each efficiency level identified for
analysis. This methodology estimates
the incremental cost of increasing
product efficiency. When analyzing the
cost of each efficiency level, the MPC is
not for the entire HVAC product,
because furnace fans are a component of
the HVAC product in which they are
integrated. The MPC includes costs only
for the components of the HVAC
product that impact FER.
Baseline
During the preliminary analysis, DOE
selected baseline units typical of the
least-efficient furnace fans used in
commercially-available, residential
HVAC models that have a large number
of annual shipments. This sets the
starting point for analyzing potential
technologies that provide energy
efficiency improvements. Additional
details on the selection of baseline units
may be found in chapter 5 of the Final
Rule TSD. DOE compared the FER at
higher energy efficiency levels to the
FER of the baseline unit and compared
baseline MPCs to the MPCs at higher
efficiency levels.
DOE reviewed FER values that it
calculated using test data and
performance information from publiclyavailable product literature to determine
baseline FER ratings. Table IV.4
presents the baseline FER values
identified in the preliminary analysis
for each product class.
TABLE IV.4—PRELIMINARY ANALYSIS BASELINE FER
FER
(W/1,000 cfm)
Product class
Non-Weatherized, Non-Condensing Gas Furnace Fan .................................................................................................
Non-Weatherized, Condensing Gas Furnace Fan .........................................................................................................
Weatherized, Non-Condensing Gas Furnace Fan .........................................................................................................
Non-Weatherized, Non-Condensing Oil Furnace Fan ...................................................................................................
Electric Furnace/Modular Blower Fan ............................................................................................................................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan ...........................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ..................................................................................
Mobile Home Electric Furnace/Modular Blower Fan ......................................................................................................
In response to the preliminary
analysis, manufacturers asserted that the
baseline FER values presented were not
representative of the furnace fans in the
least-efficient residential HVAC models
offered for sale today. Some
manufacturers also requested that DOE
alter FER to better reflect unit capacity.
Specifically, some manufacturers stated
that residential furnace fans having a
larger capacity also have higher FERs
and recommended that DOE adjust
baseline FER values to include the
largest-capacity fan within a product
class. 78 FR 64089.
In the NOPR, DOE evaluated the
feedback it received and used the data
provided by interested parties to
generate new FER values and to revise
its baseline, intermediate efficiency
levels, and max-tech FER estimates.
DOE’s revisions included FER results
for furnace fan models that span the
capacity range of residential products.
After reviewing all of the available FER
values based on new data, DOE
concluded that FER can best be
represented as a linear function of
airflow capacity (i.e., a first constant
added to airflow multiplied by a second
380
393
333
333
312
295
319
243
constant). The slope of the linear fit
characterizes the change in FER for each
unit of airflow capacity increase, and
the y-intercept represents where the
FER line intersects the y-axis (where
airflow capacity is theoretically zero).
For the NOPR, DOE proposed to use
such linear functions to represent FER
for the different efficiency levels of the
different product classes. 78 FR 64089.
Table IV.5 shows the revised FER
baseline efficiency levels estimates that
DOE used for the NOPR.
TABLE IV.5—NOPR BASELINE FER ESTIMATES
FER*
(W/1,000 cfm)
Product class
mstockstill on DSK4VPTVN1PROD with RULES2
Non-Weatherized, Non-Condensing Gas Furnace Fan .................................................................................................
Non-Weatherized, Condensing Gas Furnace Fan .........................................................................................................
Weatherized Non-Condensing Gas Furnace Fan ..........................................................................................................
Non-Weatherized, Non-Condensing Oil Furnace Fan ...................................................................................................
Electric Furnace/Modular Blower Fan ............................................................................................................................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan ...........................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ..................................................................................
Mobile Home Electric Furnace/Modular Blower Fan ......................................................................................................
Mobile Home Weatherized Gas Furnace Fan ................................................................................................................
Mobile Home Non-Weatherized Oil Furnace Fan ..........................................................................................................
FER = 0.057
FER = 0.057
FER = 0.057
FER = 0.057
FER = 0.057
FER = 0.057
FER = 0.057
FER = 0.057
Reserved.
Reserved.
×
×
×
×
×
×
×
×
QMax
QMax
QMax
QMax
QMax
QMax
QMax
QMax
+
+
+
+
+
+
+
+
362.
395.
271.
336.
331.
271.
293.
211.
*QMax is the airflow, in cfm, at the maximum airflow-control setting measured using the proposed DOE test procedure at the time of the ECS
NOPR publication. 78 FR 19606, 19627 (April 2, 2013).
Manufacturers stated that the baseline
FER values presented in the NOPR need
to be re-evaluated to determine the
appropriate baseline. Because the test
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procedure was not finalized at the time
of the ECS NOPR publication, Lennox
believes that assumptions were made by
DOE to determine the baseline from
PO 00000
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other sources, leading to overstated
energy savings and misleading
conclusions. (Lennox, No. 100 at p. 3)
Goodman believes that the NOPR
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baseline values are too high. Goodman
initially commented that baseline values
were too low for the preliminary
analysis. Based on the product testing
per the April 2013 test procedure
SNOPR, Goodman feels the increased
values for baseline FER are too high,
and should be closer (but still higher
than) the original TSD estimated values.
(Goodman, No. 102 at p. 8) Morrison,
NEEA, and NPPC also commented that
because there was no finalized test
procedure at the time the ECS NOPR
was published, DOE should not be using
test data from public literature to
generate FER values. (Morrison, No. 91
at p. 124; NEEA, NPCC, No. 96 at p. 2)
Ingersoll-Rand echoed Lennox’s and
Morrison’s comments, stating that it is
difficult to get furnace fan power data
from public literature, and that DOE’s
baseline FER values are over-estimated.
(Ingersoll-Rand, No. 91 at pp. 110–111)
Rheem and Lennox questioned whether
the efficiency levels are based off of FER
or the average annual auxiliary
electrical energy consumption (Eae).
(Rheem, No. 83 at p. 4; Lennox, No. 100
at p. 3) Lennox and Ingersoll-Rand also
commented specifically about the
baseline FER for weatherized gas
furnaces, citing a dramatic difference in
DOE’s baseline performance level as
compared to their product offerings.
Additionally, when the performance
improvement factors are applied to
DOE’s baseline, the result is a very
aggressive mandated increase in
performance. (Lennox, No. 100 at p. 3;
Ingersoll-Rand, No. 107 at p. 4) AHRI
also commented on the FER for
weatherized gas furnaces, stating that
the FER values for weatherized gas
furnace fans and non-weatherized
condensing gas furnace fans should be
the same because the test procedure is
the same for both products, except for
a difference in ESP. AHRI explained the
difference in ESP accounts for the
cooling coil within the weatherized gas
furnace, therefore, in effect, the furnace
fan assemblies for weatherized and nonweatherized gas furnaces are subject to
the same ESP. (AHRI, No. 91 at pp. 127–
129) Goodman agreed with AHRI that
weatherized gas furnace fans should
have the save efficiency levels as nonweatherized gas, non-condensing
furnace fans. (Goodman, No. 102 at p. 3)
DOE did not use Eae as an input for
the engineering analysis. All efficiency
levels considered by DOE throughout
this rulemaking, including the baseline,
are based on FER data, not Eae. DOE
used Eae as a proxy for FER to evaluate
market-wide energy performance of
furnace fans in the market and
technology assessment only. Further
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description of this characterization is
found in chapter 3 of the Final Rule
TSD. DOE disagrees with Lennox,
Morrison, NEEA, and NPPC that FER
values that DOE generated prior to the
final test procedure or based on public
literature should not be considered in
this Final Rule. DOE outlines in detail
in section III.A the reasons that FER
data from previous stages of the
rulemaking and public literature are
relevant. Section III.A also explains how
DOE’s changes to the test procedure
between the test procedure SNOPR and
final rule should not result in significant
differences in FER values for many
covered products. Thus, DOE disagrees
with Ingersoll Rand, Lennox, Goodman,
and Morrison’s claims that, in the
absence of a final test procedure or
because of changes in the final test
procedure, DOE used unreliable
information to calculate FER and model
efficiency levels for the NOPR.
Regardless, DOE agrees with interested
parties that DOE should re-update its
NOPR baseline equations based on new
data. DOE received some baseline FER
data from interested parties in response
to the NOPR. As discussed in section
III.A, DOE also conducted testing prior
to and during the development of the
test procedure final rule that generated
a broad enough set of results to enable
DOE to derive FER values that are
consistent with the requirements of the
final test procedure. DOE used this new
baseline FER data to revise its baseline
equations.
DOE investigated interested party
claims that DOE’s proposed baseline
equation for weatherized gas furnace
fans did not match manufacturer
performance estimates. DOE did not
receive additional baseline FER data for
weatherized gas furnace fans. However,
DOE did derive additional FER values
from data from specification sheets and
testing of weatherized gas furnaces at
higher efficiency levels (i.e.,
weatherized gas furnaces that use
constant-torque and constant-airflow
BPM motors). DOE was able to collect
more reliable FER data for more efficient
weatherized gas furnace fans than for
baseline weatherized gas furnace fans.
Consequently, DOE estimated the
weatherized gas furnace fan baseline
FER by multiplying the market and
capacity weighted FER value for
weatherized gas furnace fans with
constant-airflow BPM motor and multistaging by the expected percent increase
in FER (i.e., the inverse of the expected
percent reduction in FER for constantairflow BPM and multi-staging). DOE
then developed a conversion factor from
the non-weatherized, non-condensing
PO 00000
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Sfmt 4700
gas furnace fan baseline FER to generate
a y-intercept for the weatherized noncondensing gas furnace fan baseline FER
equation. This approach significantly
increased DOE’s estimated baseline FER
for weatherized non-condensing gas
furnace fans to a level consistent with
the revised baseline for nonweatherized, condensing gas furnace
fans. Even though they are not identical,
DOE concludes that the approach
described is appropriate based on
interested party feedback. The airflow
path design of weatherized noncondensing gas and non-weatherized,
condensing gas furnaces are very
different, which impacts furnace fan
performance, accounting for the slightly
different FER equations.
DOE also received comments from
interested parties regarding the slopes in
the NOPR FER equations. Rheem and
Lennox commented that the slope
characterizing the relationship between
FER and airflow capacity is too flat,
adding that higher-capacity models are
space constrained, and their FER values
do not meet the proposed FER levels in
the NOPR. (Rheem, No. 83 at p. 8;
Lennox, No. 100 at p. 6) Ingersoll-Rand
commented that for condensing
furnaces and furnaces using improved
PSC motors and multi-staging controls,
FER tends to decrease as capacity
increases, creating a negative slope.
(Ingersoll-Rand, No. 91 at pp. 110–111;
Ingersoll-Rand, No. 107 at pp. 3–4)
Ingersoll-Rand also commented that
even though FER values for furnace fans
with PSC motors follow a linear trend,
FER values for furnace fans that use
BPM motor technologies do not because
they react differently to changes in static
pressure (Ingersoll-Rand, No. 107 at p.
5) ACEEE, Goodman, and Mortex
questioned whether a linear slope is the
best way to characterize the relationship
between FER and airflow capacity.
AHRI and Goodman added that there is
a cubic relationship between fan input
power and airflow, thus, a non-linear
slope may be more appropriate. (ACEEE,
No. 94 at p. 3; Goodman, No. 102 at p.
13; Mortex, No. 104 at p. 3; AHRI, No.
98 at p. 3)
In response to interested party
comments, DOE recalculated FER versus
airflow capacity slopes using new data
from baseline series for both nonweatherized, non-condensing gas
furnace fans and non-weatherized,
condensing gas furnace fans. DOE found
that the average baseline slope increased
dramatically from 0.057 to 0.081. DOE
is aware that some instances of furnace
series models will not match DOE’s
slope analysis results. The data, that
DOE has, shows a positive slope when
characterizing the relationship between
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FER and airflow capacity. Furthermore,
DOE did not determine that a linear fit
was the best fit statistically. DOE
believes a linear fit is the best
representation of furnace fan
performance given the level of data
available. DOE finds that linear fits
result in a distribution of efficiency
levels that match the distribution of
furnace fan performance by technology
option used. Additionally, a cubic
trend-line does not account for changes
in furnace envelope size, heat exchanger
size, furnace fan outlet size, and other
factors the affect furnace fan
performance. Using a cubic trend-line
would only be appropriate if these other
factors were held constant. DOE finds
that input power to a PSC-driven
furnace fan decreases because the
airflow provided by the fan decreases as
static pressure rises (i.e., the fan does
not have to work as hard in the face of
increased resistance because the fan is
not providing as much air). Input power
to a constant-airflow BPM motor-driven
furnace fan, on the other hand, will
increase as static pressure rises because
the BPM motor-driven fan is designed to
maintain the desired level of airflow.
Recognizing that this behavior could
complicate comparing the relative
performance of these motor
technologies, DOE’s rating metric, FER,
is normalized by airflow to result in
ratings that are in units of watts/cfm.
Table IV.5 shows the revised FER
baseline efficiency levels estimates that
DOE used for the Final Rule.
TABLE IV.6—FINAL RULE BASELINE FER ESTIMATES
FER *
(W/1,000 cfm)
Product class
Non-Weatherized, Non-Condensing Gas Furnace Fan .................................................................................................
Non-Weatherized, Condensing Gas Furnace Fan .........................................................................................................
Weatherized Non-Condensing Gas Furnace Fan ..........................................................................................................
Non-Weatherized, Non-Condensing Oil Furnace Fan ...................................................................................................
Electric Furnace/Modular Blower Fan ............................................................................................................................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan ...........................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ..................................................................................
Mobile Home Electric Furnace/Modular Blower Fan ......................................................................................................
Mobile Home Weatherized Gas Furnace Fan ................................................................................................................
Mobile Home Non-Weatherized Oil Furnace Fan ..........................................................................................................
FER = 0.081
FER = 0.081
FER = 0.081
FER = 0.081
FER = 0.081
FER = 0.081
FER = 0.081
FER = 0.081
Reserved.
Reserved.
×
×
×
×
×
×
×
×
QMax
QMax
QMax
QMax
QMax
QMax
QMax
QMax
+
+
+
+
+
+
+
+
335.
358.
365.
433.
304.
252.
273.
186.
* QMax is the airflow, in cfm, at the maximum airflow-control setting measured using the final DOE test procedure. 79 FR 499, 524 (January 3,
2014).
Percent Reduction in FER
For the preliminary analysis, DOE
determined average FER reductions for
each efficiency level for a subset of key
product classes and applied these
reductions to all product classes. DOE
found from manufacturer feedback and
its review of publically-available
product literature that manufacturers
use similar furnace fan components and
follow a similar technology path to
improving efficiency across all product
classes. DOE does not expect the
percent reduction in FER associated
with each design option, whether
commercially available or prototype, to
differ across product classes as a result.
Table IV.7 includes DOE’s preliminary
analysis estimates for the percent
reduction in FER from baseline for each
efficiency level.
TABLE IV.7—PRELIMINARY ANALYSIS ESTIMATES FOR PERCENT REDUCTION IN FER FROM BASELINE FOR EACH
EFFICIENCY LEVEL
Efficiency level
(EL)
1
2
3
4
5
................................................
................................................
................................................
................................................
................................................
Percent
reduction in
FER from
baseline
Design option
Improved PSC ..............................................................................................................................
Inverter-Driven PSC .....................................................................................................................
Constant-Torque BPM Motor .......................................................................................................
Constant-Airflow BPM Motor + Multi-Staging ..............................................................................
Premium Constant-Airflow BPM Motor + Multi-Staging + Backward-Inclined Impeller ...............
2
10
45
59
* 63
mstockstill on DSK4VPTVN1PROD with RULES2
* DOE estimates that implementing a backward-inclined impeller at EL 5 results in a 10% reduction in FER from EL 4. This is equivalent to a
reduction of 4% percent of the baseline FER. The total percent reduction in FER from baseline for EL 5 includes the 59% reduction from EL 4
and the 4% net reduction of the backward-inclined impeller for a total percent reduction of 63% from baseline.
Interested parties questioned DOE’s
estimates for the FER reduction for highefficiency motors. Specifically,
interested parties noted that DOE
underestimated the efficiency gain of
improved PSC motors over standard
PSC motors, and overestimated the
efficiency improvement of BPM motor
technology options. 78 FR 64090.
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For the NOPR, DOE reviewed its
estimates of percent reduction in FER
from baseline for each efficiency level
based on interested party feedback. In
addition to the comments summarized
above, interested parties also provided
FER values for higher-efficiency
products in manufacturer interviews.
DOE used these data to revise its
percent reduction estimates. Table IV.8
PO 00000
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Sfmt 4700
shows DOE’s revised estimates for the
percent reduction in FER for each
efficiency level that DOE used in the
NOPR. For a given product class, DOE
applied the percent reductions below to
both the slope and y-intercept of the
baseline FER equation to generate FER
equations to represent each efficiency
level above baseline.
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TABLE IV.8—NOPR ESTIMATES FOR PERCENT REDUCTION IN FER FROM BASELINE FOR EACH EFFICIENCY LEVEL
Efficiency level
(EL)
1
2
3
4
5
6
................................................
................................................
................................................
................................................
................................................
................................................
Percent
reduction
in FER from
baseline
Design option
Improved PSC ..............................................................................................................................
Inverter-Driven PSC .....................................................................................................................
Constant-Torque BPM Motor .......................................................................................................
Constant-Torque BPM Motor and Multi-Staging ..........................................................................
Constant-Airflow BPM Motor and Multi-Staging ..........................................................................
Premium Constant-Airflow BPM Motor and Multi-Staging + Backward-Inclined Impeller ...........
10
25
42
50
53
* 57
mstockstill on DSK4VPTVN1PROD with RULES2
* DOE estimates that implementing a backward-inclined impeller at EL 6 results in a 10% reduction in FER from EL 5. This is equivalent to a
4% percent reduction in FER from baseline. The total percent reduction in FER from baseline for EL 6 includes the 53% reduction from EL 5 and
the 4% net reduction from the backward-inclined impeller for a total percent reduction of 57% from baseline.
Note that EL 4 in the table above was
a newly proposed efficiency level in the
NOPR. As discussed in section IV.A.3,
DOE analyzed multi-staging as a
separate technology option. For the
NOPR, DOE also evaluated a separate
efficiency level representing applying
multi-staging to a furnace fan with a
constant-torque BPM motor. 78 FR
64091.
In response to the NOPR, AHRI asked
if DOE considered pairing PSC motors
with multi-stage furnace controls in its
analysis. (AHRI, No. 91 at p. 310) While
DOE did gather data for and investigated
PSC-driven furnace fans in multi-stage
products, DOE did not include this
combination as an efficiency level for
the Final Rule. In the engineering
analysis, DOE assesses technology
options in order of cost-effectiveness.
DOE finds that constant-torque BPM
motors are more cost-effective than PSC
motors with multi-staging. While the
cost of multi-staging for each motor type
is approximately the same, multi-staging
results in significantly less energy
savings when used with a PSC motor.
DOE expects this is the result of a
limited turndown ratio as discussed in
section III.A.4.
Interested parties commented on the
NOPR percent reductions in FER from
the baseline and resulting efficiency
level equations. Nidec stated that the
percent reductions do not reflect
furnace fan performance improvements
when using higher-efficiency PSC
motors. (Nidec, No. 91 at p. 147) Many
manufacturers stated that the proposed
efficiency levels are not consistent with
product performance using the varying
design options. Rheem, Allied Air,
Daikin, Lennox, and Ingersoll-Rand
stated that only their multi-staging
furnace lines that use constant-airflow
BPM motors would meet the proposed
standard level. (Rheem, No, 83 at pp. 1–
2; Allied Air, No. 91 at p. 105; Daikin,
No. 91 at p. 105; Lennox, No. 100 at p.
5; Ingersoll-Rand, No. 91 at pp. 102–
103) Goodman and AHRI submitted
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similar comments stating that there are
existing products that use the design
options specified within TSL 5 that will
not even meet the proposed energy
conservation standards. (AHRI, No. 98
at p. 3; and Goodman, No 102 at pp. 4
and 7) In a joint comment submitted by
Appliance Standards Awareness Project
(ASAP), Alliance to Save Energy (ASE),
National Consumer Law Center (NCLC),
and National Resources Defense Council
(NRDC) and in a separate comment
submitted by California Investor-Owned
Utilities (CA IOUs), interested parties
recommended that DOE conduct
additional testing of furnace fans with
constant-torque BPM motors with multistaging controls to verify the accuracy of
the proposed FER standard level
equations, and to ensure that the
majority of products containing
constant-torque BPM motors with multistaging controls meet the standard.
(ASAP, et al., No. 105 at p. 2; CA IOU,
No. 106 at p. 3)
DOE carefully considered the
feedback received from interested
parties on the percent reductions in FER
from baseline that the Department
proposed in the NOPR. DOE shares
manufacturers’ concerns that their
products are not meeting the levels
proposed in the NOPR despite those
models using the technologies (or more
efficient technologies) on which those
levels are based. DOE used data
provided by interested parties,
conducted additional testing using the
final DOE test procedure, and gathered
data from additional product
specification sheets to generate new FER
values. DOE used this new FER data to
revise its estimates of percent reduction
in FER from baseline for each efficiency
level. In response to Nidec, DOE did
analyze an efficiency level associated
with improved PSC motors. However,
DOE did not receive and could not
gather any new FER data with which to
revise its estimated percent reduction in
FER from baseline for this technology.
Using the revised estimates of percent
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reduction in FER from baseline, DOE
revised its FER equations. Then, for the
product classes with the highest
shipments, DOE assessed how many
models for which DOE has an FER value
met the revised EL 4. DOE finds that
over 90% of the non-weatherized, noncondensing gas, non-weatherized,
condensing gas and weatherized noncondensing gas furnace fans for which
DOE has FER values that use constanttorque BPM motors and multi-staging
meet the revised EL 4. DOE finds that
many models in those product classes
for which DOE has FER data that use
constant-torque BPM motors without
multi-staging would also meet the
revised EL 4. DOE feels that the
percentage of models that meet the
revised EL 4 show that the Final Rule
efficiency levels are reflective of the
performance of the technologies on
which they are based.
Ingersoll Rand stated that percent
reduction in FER from the baseline
should not be constant across all
capacities for products using constanttorque BPM motor technologies.
Specifically, Ingersoll-Rand noted that
efficiency improvements with this
technology decrease with increasing
furnace capacity, and that at high
airflow capacities, there is little or no
difference in FER values between
furnace fans using improved PSC
motors and those using constant-torque
BPM motors. (Ingersoll-Rand, No. 107 at
p. 5) Additionally, Ingersoll-Rand stated
that wider cabinets for furnaces with
more cooling capacity but the same
heating input will have lower FERs.
(Ingersoll-Rand, NOPR Public Meeting
Transcript, No. 91 at p. 94) IngersollRand and Mortex disagree with DOE
using the same slope for FER equations
for both mobile home furnaces as well
as non-mobile home furnaces. These
parties cite that there are space
constraints associated with mobile
home applications, and that it is more
difficult to meet the proposed standard
at higher capacities because the cabinet
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size must remain the same. (IngersollRand, No. 91 at pp. 116–117; Mortex,
No. 91 at pp. 129–131)
DOE recognizes that percent
reduction in FER from baseline for a
given technology option varies with
capacity. DOE’s estimates of percent
reduction in FER from baseline are
based on market-weighted averages of
FER values from across the entire range
of furnace fan airflow capacities to
account for this variation. As discussed
above, DOE finds that constant percent
reductions in FER from baseline result
in a distribution of efficiency levels that
match the distribution of furnace fan
performance by technology option used
across the entire range of furnace fan
airflow capacities. Thus, DOE believes
that a constant percent reduction in FER
from baseline across all airflow
capacities is appropriate. DOE is also
aware that in some instances FER may
decrease for furnaces with higher
cooling capacities but the same heating
input. DOE’s analysis includes FER data
for furnace fans that have differing
heating capacity to cooling capacity
ratios. DOE recognizes that these ratios
indicate design differences that impact
fan performance. However, a significant
majority of the models for which DOE
has FER data are meeting the ELs
associated with the technologies that
they use. Of the few models that do not,
DOE observes no pattern related to the
ratio of heating capacity to cooling
capacity. DOE recognizes that mobile
home products are more spaceconstrained than the other products
covered by this standard. DOE did not
receive mobile home FER data in
response to the NOPR. Despite DOE
using the same slope for mobile home
product classes to characterize the
relationship between FER and airflow
capacity for all product classes, the
resulting ELs for mobile home furnace
fans are less stringent than those for
non-mobile home furnaces at higher
capacities. EL 4 for MH–NWG–NC and
NWG–NC both have slopes of 44 FER
per 1000 cfm, for example. Thus, for an
increase in airflow capacity of 1000 cfm,
EL 4 allows for an increase of 44 in FER
for both classes. At 1,200 cfm, EL 4 is
represented by and FER of 235 for
NWG–NC and 190 for MH–NWG–NC.
38159
An increase of 44 in FER would
represent an increase in FER of
approximately 18 percent for the NWG–
NC furnace fan, but an increase in FER
of approximately 23% for the MH–
NWG–NC furnace fan. Consequently,
the allowable increase in FER as
capacity increases is more lenient for
mobile home furnaces. DOE believes
this leniency is appropriate considering
the more rigid space constraints mobile
home furnaces must meet. DOE
recognizes that the same variation in
stringency occurs as a result of DOE’s
method for establishing baseline FER
equations using conversion factors as
described in more detail in chapter 5 of
the Final Rule TSD. However, the
difference in FER values between
mobile home and non-mobile home
furnace fans is much greater than the
difference between FER values amongst
non-mobile home furnace fans. The
variation in stringency for non-mobile
home products is minimal as a result.
Table IV.9 shows DOE’s revised
estimates for the percent reduction in
FER for each efficiency level that DOE
used in the Final Rule analyses.
TABLE IV.9—FINAL RULE ESTIMATES FOR PERCENT REDUCTION IN FER FROM BASELINE FOR EACH EFFICIENCY LEVEL
Efficiency level
(EL)
1
2
3
4
5
6
................................................
................................................
................................................
................................................
................................................
................................................
Percent
reduction
in FER from
baseline
Design option
Improved PSC ..............................................................................................................................
Inverter-Driven PSC .....................................................................................................................
Constant-Torque BPM Motor .......................................................................................................
Constant-Torque BPM Motor and Multi-Staging ..........................................................................
Constant-Airflow BPM Motor and Multi-Staging ..........................................................................
Premium Constant-Airflow BPM Motor and Multi-Staging + Backward-Inclined Impeller ...........
12
25
41
46
51
* 56
* DOE estimates that implementing a backward-inclined impeller at EL 6 results in a 10% reduction in FER from EL 5. This is equivalent to a
5% percent reduction in FER from baseline. The total percent reduction in FER from baseline for EL 6 includes the 51% reduction from EL 5 and
the 5% net reduction from the backward-inclined impeller for a total percent reduction of 56% from baseline.
Ingersoll Rand provided a significant
amount of FER data in its written
comment to support its statements.
(Ingersoll Rand, No. 107 at pp. 3, 12–16)
DOE appreciates this information and
included these FER values in its
revision of the engineering analysis to
account for the furnace fan performance
behaviors described by Ingersoll Rand.
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2. Manufacturer Production Cost (MPC)
In the preliminary analysis, DOE
estimated the manufacturer production
cost associated with each efficiency
level to characterize the cost-efficiency
relationship of improving furnace fan
performance. The MPC estimates are not
for the entire HVAC product because
furnace fans are a component of the
HVAC product in which they are
integrated. The MPC estimates includes
costs only for the components of the
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HVAC product that impact FER, which
DOE considered to be the:
•
•
•
•
•
•
Fan motor and integrated controls;
Primary control board (PCB);
Multi-staging components;
Impeller;
Fan housing; and
Components used to direct or guide
airflow.
DOE separated the proposed product
classes into high-volume and lowvolume product classes and generated
high-volume and low-volume MPC
estimates to account for the increased
purchasing power of high-volume
manufacturers.26
26 High-volume and low-volume product classes
are discussed further in chapter 5 of the Final Rule
TSD.
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Production Volume Impacts on MPC
In response to the preliminary
analysis, manufacturers commented that
they use different manufacturing
processes for high and low-volume
products. In the NOPR analysis, DOE
found that 94 percent of the MPC for
furnace fans is attributed to materials
(included purchased parts like fan
motors), which are not impacted by
process differences. DOE’s estimates
also already accounted for process
differences between manufacturers for
high-volume and low-volume products.
The products that DOE evaluated to
support calculation of MPC included
furnace fans from various
manufacturers, including both highvolume and low-volume models.
Observed process differences are
reflected in the bills of materials for
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those products. DOE believed that its
approach to distinguish between highvolume and low-volume product classes
accounts for the expected difference in
MPC between high-volume and lowvolume product classes. 78 FR 64091.
DOE did not receive comment or
additional information on production
volume impacts on MPC, thus, DOE is
taking the same approach to distinguish
between high-volume and low-volume
product classes in the Final Rule.
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Inverter-Driven PSC Costs
In the preliminary analysis, DOE
estimated that the MPC of inverter
control for a PSC motor is $10–$12,
depending on production volume.
Interested parties commented that DOE
was underestimating the cost of adding
an inverter to a PSC motor, and
questioned if DOE’s cost estimate was
for wave chopper technology and not
inverters. In the NOPR, DOE stated that
the preliminary analysis estimate for the
MPC of an inverter-driven PSC was
indeed based on a wave chopper drive.
DOE found that more sophisticated and
costly inverters are required to achieve
the efficiencies reflected in DOE’s
analysis. Consequently, DOE adjusted
its cost estimate for PSC inverter
technology. DOE gathered more
information about the cost of inverters
that are suited for improving furnace fan
efficiency. In addition to receiving cost
estimates during manufacturer
interviews, DOE also reviewed its cost
estimates for inverter drives used in
other residential applications, such as
clothes washers. DOE found that $30 for
high-volume products and $42.29 for
low-volume products are better
estimates of the MPC for inverters used
to drive PSC furnace fan motors.
Accordingly, DOE updated those values
for the NOPR. 78 FR 64091–64092.
DOE did not receive comment or
additional information on cost estimates
for inverter-driven PSC motors, thus,
DOE is not making changes to the MPC
estimates for inverters used to drive PSC
furnace fan motors in the Final Rule.
Furnace Fan Motor MPC
In response to the preliminary
analysis, manufacturers stated that DOE
underestimated the incremental MPC to
implement high-efficiency motors in
HVAC products, other than oil furnaces.
Most manufacturers stated that the cost
increase to switch from PSCs to moreefficient motor technologies was at least
twice that of the DOE’s estimate. Based
upon the input received from interested
parties, DOE adjusted its motor cost
estimates in the NOPR analysis. In
general, DOE increased its estimates by
approximately 10 to 15 percent, which
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is consistent with the feedback DOE
received. 78 FR 64092.
Goodman stated that DOE
significantly underestimated the costs of
the increasing levels of fan motor cost.
(Goodman, No. 102 at p. 9) Lennox
stated that DOE underestimated the total
cost of furnace fans with BPM motor
technology by 10 to 30 percent,
therefore, the incremental costs are
underestimated by 20 to 120 percent.
(Lennox, No. 100 at p. 6) Conversely,
ACEEE commented that DOE has a wellestablished record of over-estimating the
cost of complying with standards, thus,
DOE’s cost estimates should be
discounted to further improve the
economics of advanced technology
options. (ACEEE, No. 94 at p. 3) Rheem
questioned if the DOE motor cost
estimates included power factor
correction filters for BPM motors, as
those can cost $10 to $20. (Rheem, No.
91 at p. 165)
DOE recognizes that BPM motor use
contributes to concerns regarding total
harmonic distortion. However, the use
of power factor correction filters for
BPM motor technologies is currently not
required under federal regulations. The
DOE cost estimates reflect what is
currently available on the market, thus,
the added cost of filters for BPM motor
technologies is not included in DOE’s
MPC estimates for BPM motors. DOE
believes the motor MPC estimates
presented in the NOPR are
representative of current motor costs.
Thus, DOE is keeping the same furnace
fan motor cost estimates presented in
the NOPR for the Final Rule analysis.
Details regarding DOE’s MPC estimates
are provided in chapter 5 of the Final
Rule TSD.
Motor Control Costs
In the preliminary analysis, DOE
estimated that the MPC of the primary
control board (PCB) increases with each
conversion to a more-efficient motor
type (i.e., from PSC to constant-torque
BPM motor and from constant-torque to
constant-airflow BPM motor).
Manufacturers confirmed that higherefficiency motors and modulating
motors require more sophisticated and
costly controls. DOE also received
feedback regarding the cost of the PCBs
associated with each motor type during
manufacturer interviews. In general,
manufacturers commented that the
PCBs used with constant-torque BPM
motors are more costly. However, other
manufacturer interview participants
stated that the MPC of the PCB used
with these motors should be equivalent
or even less expensive than the PCBs
used with PSC motors. 78 FR 64092.
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In the NOPR, DOE agreed with
interested parties that the MPC of the
PCB needed for a constant-airflow BPM
motor is higher than for the PCB paired
with a PSC motor. DOE estimated that
the MPC of a PCB paired with a
constant-airflow BPM motor is roughly
twice as much as for a PCB paired with
a constant-torque BPM motor or PSC.
DOE also agreed with the interested
parties that stated that the MPC for a
PCB paired with a constant-torque BPM
motor is equivalent to that of a PCB
needed for a PSC motor. DOE revised its
analysis to reflect this assumption in the
NOPR as a result.
DOE did not receive comment or
additional information on motor control
costs, thus, DOE is not making changes
to this in the Final Rule.
Backward-Inclined Impeller MPC
Interested parties commented that
DOE’s preliminary analysis estimate for
the incremental MPC associated with
implementing a backward-inclined
impeller, in combination with a
premium constant-airflow BPM motor
and multi-staging, is too low.
Manufacturers also commented that
tighter tolerances and increased
impeller diameter lead to increased
material costs, as well as increased costs
associated with motor mount structure
and reverse forming fabrication
processes.
During the NOPR, DOE reviewed its
manufacturer production cost estimates
for the backward-inclined impeller
technology option based on interested
party comments. During manufacturer
interviews, some manufacturers
reiterated or echoed that DOE’s
estimated MPC for backward-inclined
impellers is too low, but they did not
provide quantification of the total MPC
of backward-inclined impellers or the
incremental MPC associated with the
changes needed to implement them.
Other manufacturers did quantify the
MPC of backward-inclined impeller
solutions and their estimates were
consistent with DOE’s preliminary
analysis estimate. Consequently, DOE
did not modify its preliminary analysis
estimated MPC for backward-inclined
impellers in the NOPR. 78 FR 64092.
In response to the NOPR, Mortex
questioned whether the price
differential between backward-inclined
impellers manufactured at high volume
and those manufactured at low volume
should be greater than DOE’s estimate of
32 cents. (Mortex, No. 91 at p. 163)
DOE reviewed its manufacturer
production cost estimates for the
backward-inclined impeller technology
option based on interested party
comments. DOE did not receive any
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quantification of the total MPC of
backward-inclined impellers or the
incremental MPC associated with the
changes needed to implement them.
Consequently, DOE did not modify its
NOPR estimated MPC for backwardinclined impellers in the Final Rule.
Regardless, DOE finds that EL 6, which
represents use of a backward-inclined
impeller, is not economically justified.
Modifying the MPC estimate for this
technology would not impact the
standard set by this Final Rule as a
result.
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Other Components
In response to the MPCs presented in
the NOPR, Goodman commented that
there are likely additional components
for the furnace that may need to be
added if significant changes to the
blower system are implemented. For
example, improving air moving
efficiency may require an increase in
cabinet size, or the addition of internal
baffling to direct airflow over the heat
exchanger. None of these additional
components or modifications were
accounted for in the furnace fan MPC.
(Goodman, No. 102 at p. 13)
As discussed in section III.B.1 and
chapter 4 of the Final Rule TSD, DOE
did not include housing design
modifications in the engineering
analysis. Thus, DOE did not develop
cost estimates for housing design
modifications. DOE recognizes that the
airflow path design of the HVAC
product in which the furnace fan is
integrated impacts efficiency. DOE
anticipates that modifying the size of
the cabinet and the geometry of the heat
exchanger(s) would be the primary
considerations for improving airflow
path design. Alterations to the design
and configuration of internal
components, such as the heat
exchanger, could impact the thermal
performance of the HVAC product,
potentially reducing or eliminating
product availability for certain
applications. While DOE did not
consider airflow path design as a
technology option, as described in
section III.B.1, DOE did account for the
components used to direct or guide
airflow in the MPC estimates.
D. Markups Analysis
DOE uses manufacturer-to-consumer
markups to convert the manufacturer
selling price estimates from the
engineering analysis to consumer prices,
which are then used in the LCC and PBP
analysis and in the manufacturer impact
analysis. Before developing markups,
DOE defines key market participants
and identifies distribution channels.
Generally, the furnace distribution
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chain (which is relevant to the
residential furnace fan distribution
chain) includes distributors, dealers,
general contractors, mechanical
contractors, installers, and builders. For
the markups analysis, DOE combined
mechanical contractors, dealers, and
installers in a single category labeled
‘‘mechanical contractors,’’ because these
terms are used interchangeably by the
industry. Because builders serve the
same function in the HVAC market as
general contractors, DOE included
builders in the ‘‘general contractors’’
category.
DOE used the same distribution
channels for furnace fans as it used for
furnaces in the recent energy
conservation standards rulemaking for
those products. DOE believes that this is
an appropriate approach, because the
vast majority of the furnace fans covered
in this rulemaking is a component of a
furnace. Manufactured housing furnace
fans in new construction have a separate
distribution channel in which the
furnace and fan go directly from the
furnace manufacturer to the producer of
mobile homes. DOE has concluded that
there is insufficient evidence of a
replacement market for furnace fans to
establish a separate distribution channel
on that basis.
DOE develops baseline and
incremental markups to transform the
manufacturer selling price into a
consumer product price. DOE uses the
baseline markups, which cover all of a
distributor’s or contractor’s costs, to
determine the sales price of baseline
models. Incremental markups are
separate coefficients that DOE applies to
reflect the incremental cost of higherefficiency models.
Ingersoll Rand stated that the
incremental markup percentages do not
represent real life practices and are too
low. It commented that once the new
rule goes into effect, the more expensive
furnaces will become the baseline and
will need to be marked up appropriately
for manufacturers, distributors, and
dealers to remain viable. (Ingersoll
Rand, No. 107 at p. 8) However, the
commenter provided no data to support
its expectation of how the actors
respond in terms of pricing when
confronted with more-stringent energy
conservation standards.
DOE acknowledges that detailed
information on actual distributor and
contractor practices would be helpful in
evaluating their markups on furnaces. In
the absence of such information, DOE
has concluded that its approach, which
is consistent with expected business
behavior in competitive markets, is
reasonable to apply. If the cost of goods
sold increases due to efficiency
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38161
standards, DOE continues to assume
that markups would decline slightly,
leaving profit unchanged, and, thus, it
uses lower markups on the incremental
costs of higher-efficiency products.
Goodman stated that lower markups
on incremental costs of higherefficiency products is an invalid
practice because manufacturers will
attempt to have higher margin dollars to
offset overall lower volumes. (Goodman,
No. 102 at p. 9) For the LCC and NIA
analyses, DOE does not use a lower
markup on the incremental
manufacturer selling price of higherefficiency products. Instead, it assumes
that manufacturers are able to maintain
existing average markups in response to
new standards. The MIA considers
different markup scenarios for
manufacturers (see section IV.J.2.b).
E. Energy Use Analysis
The purpose of the energy use
analysis is to determine the annual
energy consumption of residential
furnace fans in representative U.S.
homes and to assess the energy savings
potential of increased furnace fan
efficiency. In general, DOE estimated
the annual energy consumption of
furnace fans at specified energy
efficiency levels across a range of
climate zones. The annual energy
consumption includes the electricity
use by the fan, as well as the change in
natural gas, liquid petroleum gas (LPG),
electricity, or oil use for heat production
as result of the change in the amount of
useful heat provided to the conditioned
space as a result of the furnace fan. The
annual energy consumption of furnace
fans is used in subsequent analyses,
including the LCC and PBP analysis and
the national impact analysis.
DOE used the existing DOE test
procedures for furnaces and air
conditioners to estimate heating and
cooling mode operating hours for the
furnace fan. The power consumption of
the furnace fan is determined using the
individual sample housing unit
operating conditions (the pressure and
airflow) at which a particular furnace
fan will operate when performing
heating, cooling, and constantcirculation functions. The methodology
and the data are fully described in
chapter 7 of the final rule TSD.
DOE used the Energy Information
Administration’s (EIA) Residential
Energy Consumption Survey (RECS) 27
to establish a sample of households
using furnace fans for each furnace fan
27 Energy Information Administration, 2009
Residential Energy Consumption Survey (Available
at: https://www.eia.gov/consumption/residential/
data/2009/index.cfm?view=consumption).
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product class. RECS data provide
information on the age of furnaces with
furnace fans, as well as heating and
cooling energy use in each household.
The survey also includes household
characteristics such as the physical
characteristics of housing units,
household demographics, information
about other heating and cooling
products, fuels used, energy
consumption and expenditures, and
other relevant data. DOE uses the
household samples not only to
determine furnace fan annual energy
consumption, but also as the basis for
conducting the LCC and PBP analysis.
DOE used RECS 2009 28 heating and
cooling energy use data to determine
heating and cooling operating hours.
DOE used data from RECS 2009,
American Housing Survey (AHS)
2011,29 and the Census Bureau 30 to
project household weights in 2019,
which is the anticipated compliance
date of any new energy efficiency
standard for residential furnace fans.
These adjustments account for housing
market changes since 2009, as well as
for projected product and demographic
changes.
The power consumption (and overall
efficiency) of a furnace fan depends on
the speed at which the motor operates,
the external static pressure difference
across the fan, and the airflow through
the fan. To calculate furnace fan
electricity consumption, DOE
determined the operating conditions
(the pressure and airflow) at which a
particular furnace fan will operate in
each RECS housing unit when
performing heating, cooling, and
constant-circulation functions. For the
final rule, DOE adjusted the furnace fan
energy use estimated from RECS 2009
data to account for projected changes in
heating and cooling loads due to climate
change (as projected by EIA in AEO
2013).
DOE gathered field data from
available studies and research reports to
determine an appropriate distribution of
external static pressure (ESP) values.
DOE compiled over 1,300 field ESP
measurements from several studies that
included furnace fans in single-family
and mobile homes in different regions of
the country. The average ESP value in
the cooling operating mode from these
studies results in an average 0.65 in.
w.c. for single-family households and
0.30 in. w.c. for mobile homes.
28 See https://www.eia.gov/consumption/
residential/data/2009/.
29 See https://www.census.gov/housing/ahs/data/
national.html.
30 See https://www.census.gov/popest/.
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Rheem stated that substitution of a
BPM motor can increase the
conditioned air that is leaked to the
atmosphere. (Rheem, No. 83 at p. 13)
However, the commenter provided no
data to support its view on increased air
leakage associated with BPM motors.
DOE agrees that if a BPM motor
maintains flow in a high-resistance duct
system that has leakage, it may lead to
higher duct leakage compared to a PSC
motor. However, in cases where the
heating load can be met with low air
flow, the BPM motor may have lower air
leakage. Given that the magnitude of
these effects is uncertain and may offset,
DOE did not include it in its analysis.
DOE notes that the constant-torque BPM
motor, which meets the standards in
today’s final rule, may not maintain the
flow in leaky and overly-restrictive
ducts, and, thus, would be expected to
have similar losses as a PSC motor.
NEEA stated that their field
measurements of ESP for the past 40
years are consistent with DOE’s
analysis. (NEEA, No. 91 at p. 222)
Daikin stated that, from experience over
the past 30 plus years, mobile homes
have higher external static pressure than
the typical site-built home in the
preponderance of cases. (Daikin, No. 91
at p. 222)
The data that DOE has seen (described
in appendix 7B of the final rule TSD) do
not indicate that mobile homes have
higher external static pressure.
Furthermore, the HUD static pressure
criteria for mobile homes 31 are
supportive of DOE’s assumptions
regarding ESP. Consequently, DOE has
maintained its approach regarding ESP
for this final rule.
DOE determined furnace fan
operating hours in heating mode by
calculating the furnace burner operating
hours and adjusting them for delay
times between burner and fan operation.
Burner operating hours are a function of
annual house heating load, furnace
efficiency, and furnace input capacity.
For the NOPR, to estimate use of
constant circulation in the sample
homes, DOE evaluated the available
studies, which include a 2010 survey in
Minnesota 32 and a 2003 Wisconsin field
monitoring of residential furnaces.33
DOE did not use these data directly,
however, because it believes they are
not representative of consumer practices
31 HUD for Mobile Home with comfort cooling
certificate ¥0.3 inches WC at cooling airflow
setting [Title 24 of the HUD code PART 3280—
Mobile Home Construction and Safety Standards,
Part 3280.715(a)(3)(ll)].
32 Provided in CEE, No. 22 at pp. 1–2.
33 Pigg, S., ‘‘Electricity Use by New Furnaces: A
Wisconsin Field Study’’ (October 2003) (Available
at https://www.ecw.org/sites/default/files/230-1.pdf)
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for the U.S. as a whole. In these
northern States, many homes have low
air infiltration, and there is a high
awareness of indoor air quality issues,
which could lead to significant use of
constant circulation. To develop
appropriate assumptions for other
regions, DOE modified the data from
these States using information from
manufacturer product literature (which
suggests very little use in humid
climates) and consideration of climate
conditions in other regions. For the
NOPR, DOE used the same assumptions
for use of constant circulation as were
used in the proposed DOE test
procedure for furnace fans. 77 FR 28674
(May 15, 2012). The average value that
emerges is approximately 400 hours per
year. The shares of homes using the
various constant-circulation modes are
presented in Table IV.10.
NEEA and NPCC commented that
DOE’s estimate of 400 hours per year of
continuous-circulation mode may be
overly conservative, and they disagree
with stakeholders who suggest that 400
hours per year is too high. (NEEA,
NPCC, No. 32 at p. 5)
For the final rule, DOE examined a
newly-released proprietary survey that
broadly evaluates the use of continuous
circulation across the U.S.34 This survey
shows a higher number of continuouscirculation hours than DOE used for the
NOPR. DOE has concerns about the
representativeness of the data, however,
because the survey only included
homeowners who had been involved in
the purchase of central HVAC
equipment in the past two years. The
practices of these consumers may not
accurately portray the use of continuous
circulation across the entire stock of
homes with central HVAC equipment.
Given the uncertainty regarding the
survey data, DOE decided that it would
not be appropriate to change the
continuous-circulation hours for the
final rule.
Southern Company stated that if DOE
is assuming a greater percentage of
variable speed fans in the future, the
need for constant circulation will be
reduced. (Southern Company, No. 91 at
p. 233) DOE accounted for the reduced
hours of operation during constantcirculation mode when variable speed
motors are applied (see appendix 7–C).
Variable speed fans tend to increase the
operating hours in heating and cooling
modes, which would result in a smaller
fraction of time in continuous-fan mode.
34 Decision Analysts, 2013 American Home
Comfort Study (2013) (Available at: https://
www.decisionanalyst.com/Syndicated/
HomeComfort.dai).
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DOE also performed a sensitivity
analysis to estimate the effect on the
LCC results if it assumed half as much
use of constant circulation. These
38163
results are discussed in section V.B.1 of
this document.
TABLE IV.10—CONSTANT-CIRCULATION TEST PROCEDURE ASSUMPTIONS USED FOR FURNACE FANS STANDARDS
ANALYSIS
Assumed
average
number of
hours
Constant-circulation fan use
Estimated
share of
homes in north
and south-hot
dry regions
(percent)
Estimated
share of
homes in
south-hot
humid region
(percent)
0
7290
1097
541
365
84
7
2
2
5
97
1
0.4
0.4
1
Total ......................................................................................................................................
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No constant fan ...........................................................................................................................
Year-round ...................................................................................................................................
During heating season .................................................................................................................
During cooling season .................................................................................................................
Other (some constant fan) ...........................................................................................................
........................
100
100
Morrison stated that not all the energy
used in circulation is wasted heat
because the energy consumed for
circulation during the heating season is
useful energy. Morrison recommended
that for a more accurate analysis of
energy use in circulation mode, DOE
should split heating and cooling hours.
(Morrison, No. 108 at p. 2) DOE adjusted
its analysis so that heat generated by
constant-circulation fan operation
reduces furnace heating energy use in
the heating season, and in the cooling
season, it adds to the operating hours of
the air conditioner.
In the NOPR, DOE recognized that the
energy savings in cooling mode from
higher-efficiency furnace fans used in
some higher-efficiency CAC and heat
pumps was already accounted for in the
analysis related to the energy
conservation standards for those
products. To avoid double-counting, the
analysis for furnace fans did not include
furnace fan electricity savings that were
counted in DOE’s rulemaking for CAC
and heat pump products.35
Several stakeholders stated that DOE
may be double-counting energy savings
in cooling mode in this rulemaking by
accounting for the central air
conditioner blower output used for
calculating SEER. (JCI, No. 95 at pp. 4–
5; Morrison, No. 108 at p. 2; AHRI, No.
98 at p.6; Goodman, No. 102 at p. 5) EEI
stated that a large share of the estimated
furnace fan energy savings are a result
of the air conditioner and heat pump
energy efficiency standards, so some or
all of these estimated energy savings
should be removed from the furnace fan
analyses. (EEI, No. 87 at p. 5)
35 U.S. Department of Energy—Energy Efficiency
& Renewable Energy, Final Rule Technical Support
Document: Energy Efficiency Standards for
Consumer Products: Central Air Conditioners, Heat
Pumps, and Furnaces (2011) (Available at: https://
www.regulations.gov/#!documentDetail;D=EERE2011-BT-STD-0011-0012).
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DOE’s rulemaking analysis for CAC
and heat pump products included
savings from those households
purchasing a CAC or heat pump at SEER
15 or above that would need to have a
BPM motor-driven fan in the furnace to
achieve that efficiency level. The basecase efficiency distribution of fans used
in the current analysis includes the
presence of those BPM motor-driven
fans in homes with the higher-efficiency
CAC or heat pumps. Because the energy
savings from the considered fan
efficiency levels are measured relative
to the base-case efficiencies, any savings
reported here for furnace fans are over
and above those counted in the CAC
and heat pump rulemaking.
Morrison stated that any reduction in
energy use by the fan from this
rulemaking would be a de facto
improvement in SEER and an unlawful
change to the current SEER regulations.
It noted that if there is no change to
SEER, then there will be no energy
savings when operated in the cooling
mode. (Morrison, No. 108 at p. 2)
A reduction in energy use by the
furnace fan resulting from this
rulemaking would improve the CAC
operating efficiency (for homes with
both furnace and CAC), but DOE is not
increasing the energy conservation
standard for CAC or requiring a change
to the reported current SEER ratings for
CAC. DOE has clear and explicit
statutory authority to regulate furnace
fans under 42 U.S.C. 6295(f)(4)(D), and
any related improvements to CAC
efficiency would simply be an added
benefit.
Recognizing the possibility of
consumers using higher-efficiency
furnace fans more than baseline furnace
fans, DOE included a rebound effect in
its preliminary analysis. DOE used a
2009 program evaluation report from
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Wisconsin 36 to estimate the extent to
which increased use of constant
circulation under a standard requiring
BPM furnace fans is likely to cancel out
some of the savings from such a fan. The
specific assumptions are described in
chapter 7 of the final rule TSD.
Commenting on the average energy
use estimates reported in the final rule
TSD, EEI stated that the baseline energy
use values seem to be overstated,
because baseline values reported in the
market and technology assessment are
lower than what was used in following
analyses. Consequently, the estimated
energy savings and energy cost savings
are overstated as well, because they are
shown in the NOPR as percentage
savings based on the design options.
(EEI, No. 87 at pp. 4–5) Goodman
believes that the calculated baseline
values, and thus the projected energy
savings, are too high based on product
testing for the April 2013 test procedure
SNOPR. (Goodman, No. 102 at p. 8)
The baseline values reported in the
market and technology assessment are
based on the test procedure. The energy
use analysis is not based on test
procedure conditions, but instead
reflects actual usage in the field, which
is more appropriate for estimating the
impacts of higher furnace fan efficiency
on consumers. Therefore, the estimated
energy savings and energy cost savings
are not overstated.
JCI and AHRI stated that DOE needs
to ensure that it avoids double-counting
energy consumption associated with
standby mode, noting that there is no
standby mode and off mode energy use
associated with furnace fans that would
36 State of Wisconsin, Public Service Commission
of Wisconsin, Focus on Energy Evaluation
Semiannual Report, Final (April 8, 2009) (Available
at: https://focusonenergy.com/sites/default/files/
semiannualreport18monthcontractperiodfinal
revisedoctober192009_evaluationreport.pdf).
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not already be measured by the
established test procedures, because
they are integrated in the electrical
systems of the HVAC products in which
they are used. (JCI, No. 95 at p. 5; AHRI,
No. 98 at p. 6)
The proposed furnace fan energy
rating metric would not account for the
electrical energy consumption in
standby mode and off mode, because
energy consumption in those modes is
already accounted for in the energy
conservation standards for residential
furnaces and residential CAC and HP.
Accordingly, DOE did not include
standby mode and off mode energy use
associated with furnace fans in the
present analysis. Consequently, there
should not be any problems associated
with double-counting of standby mode
and off mode energy consumption.
variables (e.g., energy prices,
installation costs, and repair and
maintenance costs). It uses weighting
factors to account for distributions of
shipments to different building types
and States to generate LCC savings by
efficiency level. Each Monte Carlo
simulation consists of 10,000 LCC and
PBP calculations. The model performs
each calculation using input values that
are either sampled from probability
distributions and household samples or
characterized with single-point values.
The analytical results include a
distribution of points showing the range
of LCC savings and PBPs for a given
efficiency level relative to the base-case
efficiency forecast. The results of DOE’s
LCC and PBP analysis are summarized
in section IV.F and described in detail
in chapter 8 of the final rule TSD.
F. Life-Cycle Cost and Payback Period
Analysis
In determining whether an energy
conservation standard is economically
justified, DOE considers the economic
impact of potential standards on
consumers. The effect of new or
amended energy conservation standards
on individual consumers usually
involves a reduction in operating cost
and an increase in purchase cost. DOE
uses the following two metrics to
measure consumer impacts:
• Life-cycle cost (LCC) is the total
consumer cost of an appliance or
product, generally over the life of the
appliance or product. The LCC
calculation includes total installed cost
(equipment manufacturer selling price,
distribution chain markups, sales tax
and installation cost), operating costs
(energy, repair, and maintenance costs),
equipment lifetime, and discount rate.
Future operating costs are discounted to
the time of purchase and summed over
the lifetime of the product.
• Payback period (PBP) measures the
amount of time it takes consumers to
recover the assumed higher purchase
price of a more energy-efficient product
through reduced operating costs. Inputs
to the payback period calculation
include the installed cost to the
consumer and first-year operating costs.
DOE analyzed the net effect of
potential residential furnace fan
standards on consumers by calculating
the LCC and PBP for each efficiency
level for each sample household. DOE
performed the LCC and PBP analyses
using a spreadsheet model combined
with Crystal Ball (a commerciallyavailable software program used to
conduct stochastic analysis using Monte
Carlo simulation and probability
distributions) to account for uncertainty
and variability among the input
1. Installed Cost
The installed cost at each efficiency
level is based on the product price,
distribution chain markups, sales tax,
and installation cost.
The current product price comes from
the engineering analysis. DOE believes
that price trends for integral horsepower
electric motors are a reasonable proxy
for trends in prices of furnace fans, and
for the NOPR DOE evaluated the
historic real (i.e., adjusted for inflation)
producer price index (PPI) of such
motors. DOE found that this index has
been decreasing except for the last few
years, when it started to increase (see
appendix 10–C of the final rule TSD).
Given the uncertainty about whether the
recent trend will continue or instead
revert to the historical mean, DOE
elected to use constant prices at the
most recent level as the default price
assumption to project future prices of
furnace fans. 78 FR 64068, 64096 (Oct.
25, 2013).
Morrison stated that motor prices
have remained flat in the last decade
because production of motors moved
offshore and foreign competitors entered
the marketplace. It stated that in the
coming decades, motor prices will
increase at the rate of long run prices for
commodities (e.g. copper, steel,
aluminum). (Morrison, No. 108 at p. 2)
Goodman believes that it is incorrect to
use constant prices at the most recent
level of motor cost, which has shown a
recent increasing trend, as the default
price assumption to project future prices
of furnace fans. (Goodman, No. 102 at p.
9)
DOE continues to believe that it is
unclear whether the increasing trend in
motor prices since 2004 will continue in
the future. Part of the recent growth in
prices of commodities used in motors
was due to strong demand from China.
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Current projections envision slower
growth in China, which would likely
dampen commodity prices. Given the
uncertainty, DOE continued to use
constant prices at the most recent level
as the default price assumption for the
final rule. For the NIA, DOE also
conducted sensitivity analysis using
alternative price growth assumptions.
Because furnace fans are installed in
furnaces in the factory, there is
generally no additional installation cost
at the home. However, furnace fans that
employ a constant-airflow BPM design
may require additional installation
costs. DOE assumed that all constantairflow BPM furnace fan installations
will require extra labor at startup to
check and adjust airflow.
Goodman stated that it is acceptable
for relative product cost comparison to
include costs only for the components
of the HVAC product that impact FER
in the manufacturing cost, but it
disagrees with using the cost of only the
furnace fan portion of the furnace in the
LCC, GRIM, and other aspects of the
financial analysis. The real upfront costs
for the consumer will be significantly
higher (likely two to four times more)
than DOE has included in the analysis
using only the furnace fan portion.
(Goodman, No. 102 at p. 9) DOE
believes that the commenter is claiming
that the consumer will face higher costs
when buying a furnace because the
proposed furnace fan standards would
require changes in furnace design. As
discussed in section IV.B.1, DOE
screened out fan housing and airflow
path design modifications from further
analysis. Accordingly, it is unlikely that
significant changes in furnace design
would be required to accommodate
furnace fans that meet today’s
standards. Therefore, DOE concludes
that using the incremental costs of the
furnace fan portion is reasonable.
2. Operating Costs
To estimate the annual energy costs
for operating furnace fans at different
efficiency levels, DOE used the annual
energy use results from the energy use
analysis and projections of residential
energy prices. DOE derived average
monthly energy prices for a number of
geographic areas in the United States
using the latest data from EIA 37 and
monthly energy price factors that it
37 U.S. Department of Energy—Energy
Information Administration, Form EIA–826
Database Monthly Electric Utility Sales and
Revenue Data, 2013. https://www.eia.doe.gov/cneaf/
electricity/page/eia826.html; U.S. Department of
Energy—Energy Information Administration,
Natural Gas Navigator. 2013. https://
tonto.eia.doe.gov/dnav/ng/ng_pri_sum_dcu_nus_
m.htm.
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developed. Electricity and natural gas
prices were adjusted using seasonal
marginal price factors to come up with
monthly marginal electricity and natural
gas prices. DOE assigned an appropriate
price to each household in the sample,
depending on its location.
Laclede stated that using average
utility rates leads to significantly
overstating consumer savings. DOE
should use marginal energy rates in its
consumer energy savings calculations.
(Laclede, No. 86 at p. 4) As described
above, DOE did derive marginal
electricity and natural gas prices based
on recent data. (For a discussion of the
development of marginal energy price
factors, see appendix 8–C of the final
rule TSD). To arrive at marginal prices
in future years, DOE multiplied the
current marginal prices by values in the
Reference case projection of annual
average residential electricity and
natural gas price changes in EIA’s AEO
2013. The price trends projected in the
AEO 2013 Reference case are shown in
chapter 8 of the final rule TSD. For
electricity prices, which are primarily of
interest in this rulemaking, the AEO
2013 projection shows the average
residential price growing from 0.119
$/kWh in 2020 to 0.122 $/kWh in 2030
and 0.131 $/kWh in 2040 (constant
dollars).
To estimate annual maintenance
costs, DOE derived labor hours and
costs for annual maintenance from RS
Means data.38 The frequency with
which the maintenance occurs was
derived from a consumer survey 39 on
the frequency with which owners of
different types of furnaces perform
maintenance.
For the NOPR, DOE used the same
maintenance costs for furnace fans at
different efficiency levels. 78 FR 64096.
Goodman stated that it is invalid to
assume that the maintenance costs for
all efficiency levels are the same
regardless of technology, as higher
technology products will take a higher
skill level of technician, and will
require more costly equipment for
service than baseline products.
(Goodman, No. 102 at p. 9) Allied Air
stated that in shifting from a primarily
single-stage PSC market to multistage
constant torque, the maintenance cost
could be two to three times current
costs. (Allied Air, No. 43 at pp. 252–
253)
38 RS Means Company Inc., Means Facilities
Maintenance & Repair Cost Data. 2012. Kingston,
MA.
39 Decision Analysts, 2008 American Home
Comfort Study: Online Database Tool, 2009.
Arlington, Texas. https://www.decisionanalyst.com/
Syndicated/HomeComfort.dai.
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DOE understands that furnace fans
require very little maintenance, and it
did not find any evidence that there is
any additional maintenance cost
associated with higher efficiency
equipment. It seems likely that the
commenters are including repair costs
under the term ‘‘maintenance.’’ DOE’s
treatment of repair costs is discussed
below.
The most important element of repair
costs for furnace fans is replacement of
the fan motor. For the NOPR, to estimate
rates of fan motor failure, DOE
developed a distribution of fan motor
lifetime (expressed in operating hours)
by motor size using data developed for
DOE’s small electric motors final rule.
75 FR 10874 (March 9, 2010). DOE then
paired these data with the calculated
number of annual operating hours for
each sample furnace, including constant
circulation as appropriate. DOE did not
have a firm basis for quantifying
whether constant-torque BPM motors
and constant-airflow BPM motors have
different failure rates than PSC motors.
Thus, it used the same motor lifetime
for each fan efficiency level in terms of
total operating hours (the lifetime in
terms of years is lower for constanttorque BPM and constant-airflow BPM
motors because they are more frequently
used in multi-stage heating mode). 78
FR 64097.
Rheem stated that DOE did not justify
the assumption that furnace fan motor
lifetimes are equal to furnace lifetimes.
(Rheem, No. 83 at p. 4) DOE modeled
overall furnace fan lifetime based on
furnace lifetimes (see discussion below),
but it used the approach described
above for furnace fan motor lifetime.
Morrison stated that multi-staged
BPM assemblies will have longer
operating times within a given period
(to account for lower fire rates and heat
output) and therefore, all else being
equal, will have a shorter life
expectancy. (Morrison, No. 108 at p. 5)
DOE’s approach is consistent with the
comment; a multi-staged BPM motor has
a shorter lifetime measured in years.
A number of stakeholders stated that
failure rates are higher for BPM motors
than for PSC motors, leading to shorter
lifetime. Rheem stated that the PSC
motor life, which it estimated to be 15
years, is much longer than the BPM
motor life. (Rheem, No. 83 at pp. 2 and
13) Mortex stated that, based on their
experience, BPM lifetime is half that of
PSC motors. (Mortex, No. 104 at p. 2)
Lennox estimated that constant-airflow
BPM motors have failure rates that are
50% higher than PSC motors at 5 and
10 years, and furnaces with constanttorque BPM motors have failure rates
that are 385% higher than PSC motors
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38165
at 5 and 10 years. (Lennox, No. 100 at
p. 8) Ingersoll Rand stated that its data
indicate that BPM motors fail at 2.3
times the rate of PSC motors in the 5 to
10 year time frame. (Ingersoll Rand, No.
107 at pp. 6–7) AHRI stated that the
failure rate for a high efficiency motor
is typically higher than that of a PSC
motor because the electronics added to
a high efficiency motor introduce
additional failure modes associated with
the life of electronic controls in damp,
very cold and very hot conditions. AHRI
has collected data from manufacturers
that show that the failure rates
associated with constant-torque BPM
and constant-airflow BPM technologies
are higher than PSC motors over an
extended time period. (AHRI, No. 98 at
p. 7) Morrison and Ingersoll Rand cited
recent data from an AHRI survey of
manufacturers that indicate failure rates
at 1, 5 and 10 years are 24%, 87% and
165% greater for BPM motors than PSC
ones. (Morrison, No. 108 at p. 5,
Ingersoll Rand, No. 107 at p. 6) JCI
stated that, based on an analysis of JCI’s
residential warranty data, failure rates
associated with constant-torque BPM
and constant-airflow BPM technologies
are significantly higher than those
experienced by standard PSC motors
due to the added electronic controls that
are required as part of the BPM motor
designs, which are more susceptible to
failure due to power fluctuations and
other factors. (JCI, No. 95 at p. 7)
Ingersoll Rand stated that repair of the
electronics is not possible for the
constant-torque BPM motors available
today, so an electronics failure will
result in a complete motor replacement.
(Ingersoll Rand, No. 107 at pp. 7–8)
In contrast, NEEA and NPCC believe
that the NOPR analysis assumptions
may unfairly penalize BPM motors, as
the Department has insufficient data to
properly estimate the frequency and
nature of BPM motor repair. (NEEA,
NPCC, No. 96 at p. 5)
DOE notes that BPM motors had
higher level of failure in the late 1990s
and early 2000s when the electronics
technologies went through major
renovations. The comments from
furnace manufacturers may reflect this
past experience. For example, the cited
data from an AHRI survey of
manufacturers would reflect BPM
technology in the early 2000s. For the
final rule, DOE searched for more
information on the lifetime of BPM and
PSC motors. This information
(discussed in appendix 8–E) suggests
that BPM and PSC motors have similar
lifetimes, as BPM designs have
improved over the years. While BPM
motor designs could have additional
failures due to the additional controls or
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electronics, furnace fan motor
manufacturers claim longer mechanical
life for BPM designs due to better
bearings and less heat generated by
inefficiency. Between now and the
compliance date, future BPM motor
enhancements could further strengthen
product reliability and reduce failures.
In this analysis, DOE assumes higher
failures for BPM designs due to longer
operating hours (because of multi-stage
operating at more hours and more
constant circulation operation of BPM
motors), as well as additional control
failures. For example, DOE estimates
that 43% for BPM constant torque
multi-stage designs experience failure
during the lifetime of the furnace,
compared to 35% of PSC designs.
Recognizing that there exists some
uncertainty regarding the lifetime of
BPM motors, DOE conducted a
sensitivity analysis using alternative
assumptions, as requested in a comment
by Mortex. (Mortex, No. 43 at pp. 264–
265) This analysis is described in
appendix 8–E of the final rule TSD.
For the NOPR, the replacement motor
costs were based on costs developed in
the engineering analysis for each motor
type, and the labor time and unit costs
were based on RS Means data.40 78 FR
64097. DOE included additional labor
hours to repair constant-torque BPM
and constant-airflow BPM motors, as
well as higher equipment cost for the
BPM motors. DOE assumed that when
replacement is necessary, consumers
replace the failed motor with the same
type of motor.
A number of stakeholders stated that
the replacement cost of BPM motors is
higher than the cost DOE used in its
analysis. (Morrison, No. 108 at p. 2;
Goodman, No 102 at p. 8; APGA, No.
110 at p. 3) Mortex stated that DOE
substantially underestimated BPM
replacement costs, which in its
experience are 2–3 times that of a PSC.
(Mortex, No. 104 at p. 2) Ingersoll Rand
stated that replacement costs are
significantly underestimated for
constant-torque BPM and constantairflow BPM motors. It added that the
difference between PSC motor
replacement and constant-torque BPM
motor replacement should be at least
$225, and the PSC to constant-airflow
BPM difference should be at least $295.
(Ingersoll Rand, No. 107 at pp. 7–8) JCI
stated that outside the warranty periods
(typically 10 years for parts), ECM
motors can cost 3 to 5 times the
replacement costs of PSC motors due to
the complexity of those motors and the
40 RS Means Company Inc., RS Means Residential
Cost Data (2012); RS Means Company Inc.,
Facilities Maintenance & Repair Cost Data (2012).
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electronic controls required to use them.
(JCI, No. 95 at p. 6)
The replacement equipment cost of
BPM and PSC motors used in DOE’s
LCC analysis is based on costs derived
in the engineering analysis, which DOE
believes are accurate. It is possible that
the stakeholders believe that the higher
BPM replacement costs are largely due
to extra labor charges by contractors.
DOE determined that for a constant
torque BPM motor any such extra
charges would be minimal. In the
analysis for today’s final rule, on
average the replacement cost is $407 for
a constant torque multi-stage BPM (EL
4) and $356 for the PSC design (EL 0).
Several stakeholders stated that the
replacement cost of an aftermarket
furnace fan is 2–3 times higher than
DOE’s estimated manufacturer
production costs for low-volume
product classes. They added that DOE’s
material cost estimate of $0.00 for
furnace fan replacements is incorrect.
(JCI, No. 95 at p. 6; Morrison, No. 108
at p. 5; AHRI, No. 98 at p. 8; Lennox,
No. 100 at p. 8; Unico, No. 93 at p. 5)
DOE believes that the first comment
above refers to a replacement motor.
DOE applies markups to the motor MPC,
such that the cost to the consumer is
two to three times higher than the MPC.
The material cost is listed as $0.00 in
the cited tables because these tables
refer to labor costs only (as stated in the
table captions).
Ingersoll Rand stated that motors that
fail in-warranty are not free, as standard
product warranties in the HVAC
industry cover parts only, and do not
typically include labor charges, which
the homeowner must pay. (Ingersoll
Rand, No. 107 at p. 7) DOE excluded
labor charges only if the consumer has
a service contract or if the motor fails
the first year (which is rare).
Southern Company stated that DOE
unrealistically considered component
failures as independent events rather
than interdependent ones. It stated that
in actual consumer settings, rather than
a lab, it is likely that a capacitor failure
will not be detected until it results in a
motor failure. (Southern Company, No.
85 at p. 3) Undetected capacitor failure
that leads to motor failure (as may occur
for PSC motors) is reflected in DOE’s
distribution of motor lifetimes.
3. Furnace Fan Lifetime
DOE used the same modeling for
furnace fan lifetime (meaning the life of
the overall equipment not including the
motor) as in the NOPR.78 FR 64097.
Chapter 8 of the final rule TSD describes
the approach. DOE used the same
lifetime for furnace fans at different
efficiency levels because there are no
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data that indicate variation of lifetime
with efficiency. For the NOPR analysis,
DOE assumed that the lifetime for the
fans installed in electric furnaces and
gas furnaces is the same.
Rheem stated that the lifetime of a
residential furnace fan is limited by the
lifetime of the electronic control, and
advanced controls may shorten the
lifetime of the product. (Rheem, No. 83
at pp. 6, 13) JCI stated that the repair
costs for furnace fans are generally the
cost of replacing the motors used, as
there are very few failures of fan
components other than the motor. (JCI,
No. 95 at p. 6)
DOE believes that with current
technology there are few failures of the
electronic control, as stated by JCI. DOE
also expects that the reliability of the
electronic controls is likely to increase
as the technology matures. Nonetheless,
DOE accounts for failure of capacitors
and motor electronic controls in its
repair cost analysis.
APGA stated that 23.6 years lifetime
for gas-fired furnace fans in the LCC
analysis is unrealistic, and DOE should
employ more realistic furnace fan lives
based on documented motor lives.
(APGA, No. 110 at p. 3) It would appear
that APGA misinterpreted DOE’s
approach. Motor failure, which occurs
on average at around 15 years, is
counted as a repair cost. However, DOE
believes that the rest of the furnace fan
would last as long as the furnace itself.
Southern Company stated that
because the analysis shows at least 50%
greater shipments of furnace fans than
furnaces, the data seems to indicate a
shorter lifetime for furnace fans than
furnaces. (Southern Company, No. 85 at
p. 3) DOE did not calculate the
shipments of furnace fans. Since furnace
fans are a component of furnaces, the
shipments in the NIA analysis are
limited to furnace shipments only.
4. Discount Rates
For the NOPR, DOE used distributions
of discount rates based on a variety of
financial data. 78 FR 64097. For
replacement furnaces, the average rate
was 5.0 percent.
Miller stated that, based on a
literature review of consumer discount
rates for energy-using durables, the 3percent and 7-percent discount rates
used in the analysis only represent highincome households; other consumers
may use much higher discount rates.
Consumers with higher discount rates—
including median-income Americans,
low-income Americans, and the
elderly—are much less likely to benefit
from higher efficiency furnace fans.
(Miller, No. 79 at pp. 10–13)
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DOE uses 3-percent and 7-percent
discount rates to measure net consumer
benefits from energy efficiency
standards from a national perspective
(see section IV.H). DOE recognizes that
a wide range of discount rates may be
appropriate for consumers, and thus it
uses distributions of discount rates
when it evaluates consumer impacts in
the LCC analysis. For the final rule, DOE
developed specific distributions of
discount rates for each of six consumer
income groups. Chapter 8 of the final
rule TSD describes the approach. The
estimated impacts of today’s standards
on low-income households are
discussed in section V.B.1.41
5. Compliance Date
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In the NOPR, DOE proposed a 5-year
compliance date for residential furnace
fan standards. 78 FR 64103. A number
of stakeholders encouraged DOE to
adopt a three-year period between the
final rule publication and the
compliance date rather than the five
years proposed in the NOPR. (ACEEE,
No. 94 p. 6; NEEP, No. 109 at p. 2;
Earthjustice, No. 101 at p. 3; CA IOU,
No. 106 at p. 3; Joint Advocates, No. 105
at p. 4; NEEA, NPCC, No. 96 at p. 3)
ACEEE, CA IOU, the Joint Advocates,
and NEEA and NPCC stated that the
technologies assumed to be required to
meet TSL 4 are well-established in the
market and commercially available.
(ACEEE, No. 94 at p. 6; CA IOU, No. 106
at p. 3; Joint Advocates, No. 105 at p.
4; NEEA, NPCC, No. 96 at p. 3) NEEP
stated that three years should provide
adequate time for manufacturers to
adjust product lines. (NEEP, No. 109 at
p. 2) The Joint Advocates stated that
constant-torque BPM motors are
essentially drop-in replacements for
PSC motors, and capital conversion
costs are not required. (Joint Advocates,
No. 105 at p. 4) NEEA and NPCC believe
that three years of lead time should be
sufficient to allow a ramping up of
motor manufacturing capacity and a
gradual shift of air handler
manufacturing lines to incorporate
them. The technology required to meet
the TSL 4 standards requires little more
than expansion of current production
41 The comment refers to high discount rates
based on studies of implicit consumer discount
rates using the purchase of energy-using durables
(such as air conditioners, dishwashers, and
refrigerators) to measure consumer time
preferences. While these studies of implicit
consumer discount rates provide a way of
characterizing consumer behavior, they do not
necessarily measure consumer time preferences.
What appears to be low valuation of future energy
cost savings from higher-efficiency appliances
instead may be partially a result of lack of
information on the magnitude of savings or inability
to evaluate the available information.
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capacity for these models, which mostly
means buying different furnace fan
motors and the associated controls.
(NEEA, NPCC, No. 96 at p. 3)
Earthjustice stated that DOE must
choose a compliance date based on an
assessment that includes a
consideration of factors beyond the
impact on manufacturers. (Earthjustice,
No. 101 at p. 3)
JCI, Morrison, AHRI, Lennox, and
HARDI support the five-year period
between the final rule publication and
the compliance date as proposed in the
NOPR. (JCI, No. 95 at p. 2; Morrison, No.
108 at p. 2; AHRI, No. 98 at p. 2;
Lennox, No. 100 at p. 4; HARDI, No. 103
at p. 2) JCI, AHRI, and Lennox stated
that to comply with the proposed
standard, manufacturers would not only
have to alter the designs and fabrication
processes for the furnace fan assembly
but also modify the broader product
design of the furnaces, air handlers,
modular blowers, and residential single
package units that include those furnace
fans. (JCI, No. 95 at p. 2; AHRI, No. 98
at p. 2; Lennox, No. 100 at pp. 4–5)
AHRI stated that similar products that
require similar actions for compliance
typically have lead times of five years.
(AHRI, No. 98 at p 2) Ingersoll Rand
agrees with AHRI’s comments. (Ingersoll
Rand, No. 107 at p. 11)
DOE continues to believe a 5-year
lead time is appropriate. Since EPCA
does not mandate a specific lead time
for furnace fan standards, DOE
considered the actions required by
manufacturers to comply with today’s
standards. As discussed in the NOPR,
during manufacturer interviews, DOE
found that standards would result in
manufacturers’ extending R&D beyond
the furnace fan assembly to understand
the impacts on the design and
performance of the furnace or modular
blower in which the furnace fan is
integrated. 78 FR 64103. To comply
with the standards, manufacturers may
have to alter not only the designs and
fabrication processes for the furnace fan
assembly, but also for the furnace or
modular blower into which the furnace
fan is integrated. Similar products that
require similar actions for compliance
typically have lead times of five years.
For these reasons, DOE selected a 5-year
lead time, which would place the
compliance date in 2019. For the
purposes of the LCC and PBP analysis,
DOE assumed that all relevant
consumers purchase a furnace fan in
2019.
efficiency level, DOE’s LCC and PBP
analysis considers the projected
distribution (i.e., market shares) of
product efficiencies in the first
compliance year under the base case
(i.e., the case without new or amended
energy conservation standards).
For the NOPR, DOE reviewed the
information provided by the
manufacturers and estimated that the
combined market share of constanttorque BPM fans and constant-airflow
BPM fans will be 35 percent in 2019.
The shares are 13 percent for constanttorque BPM fans and 22 percent for
constant-airflow BPM fans. DOE
estimated separate shares for
replacement and new home
applications.78 FR 64097.
The market shares of efficiency levels
within the constant-torque BPM motor
and constant-airflow BPM motor
categories were derived from AHRI data
on number of models.42 No such data
were available for the PSC fan efficiency
levels, so DOE used the number of
models it tested or could measure using
product literature to estimate that 40
percent of shipments are at the baseline
level and 60 percent are improved PSC
fans. There are currently no models of
PSC with a controls design, so DOE
assumed zero market share for such
units. Id
No comments were received on the
base case efficiency distribution, and
DOE retained the NOPR assumptions for
the final rule. The details of DOE’s
approach are described in chapter 8 of
the final rule TSD.
6. Base-Case Efficiency Distribution
To estimate the share of consumers
that would be affected by an energy
conservation standard at a particular
42 DOE used the AHRI Directory of Certified
Furnace Equipment (Available at: https://
www.ahridirectory.org/ahridirectory/pages/
home.aspx) as well as manufacturer product
literature.
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7. Payback Period
To calculate PBPs for the considered
efficiency levels, DOE uses the same
inputs as for LCC analysis, except that
discount rates are not required.
Goodman stated that not including
repair costs from later years in the PBP
does not provide a realistic picture of
what most consumers will face. It noted
that while repair costs later in the
product life cycle may allow the initial
investment to balance out faster, the
overall life-cycle costs can be very
negatively impacted by such repairs.
(Goodman, No 102 at p. 10)
DOE recognizes that the PBP metric
does not provide a complete assessment
of all costs that consumers may face, but
it has found that the results are of
interest in standards rulemakings. The
LCC analysis does include all costs, and
in part for this reason, DOE expresses
the share of consumers who benefit
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from standards in terms of the change in
LCC.
As discussed in section III.E.2, EPCA
provides that a rebuttable presumption
is established that an energy
conservation standard is economically
justified if the additional cost to the
consumer of a product that meets the
standard is less than three times the
value of the first year’s energy savings
resulting from the standard, as
calculated under the applicable DOE
test procedure. (42 U.S.C.
6295(o)(2)(B)(i)) The calculation of this
so-called rebuttable presumption
payback period uses the same inputs as
the calculation of the regular PBP for
each sample household, but it uses
average values instead of distributions,
and the derivation of energy
consumption and savings only uses the
parameters specified by the proposed
DOE test procedure for furnace fans
rather than the method applied in the
energy use analysis (described in
section IV.E), which considers the
characteristics of each sample
household.
DOE’s LCC and PBP analyses generate
values that calculate the payback period
for consumers of potential energy
conservation standards, which includes,
but is not limited to, the three-year
payback period contemplated under the
rebuttable presumption test discussed
above. However, DOE routinely
conducts a full economic analysis that
considers the full range of impacts,
including those to the consumer,
manufacturer, Nation, and environment,
as required under 42 U.S.C.
6295(o)(2)(B)(i). The results of this
analysis serve as the basis for DOE to
definitively evaluate the economic
justification for a potential standard
level (thereby supporting or rebutting
the results of any preliminary
determination of economic
justification).
G. Shipments Analysis
DOE uses forecasts of product
shipments to calculate the national
impacts of standards on energy use,
NPV, and future manufacturer cash
flows. DOE develops shipment
projections based on historical data and
an analysis of key market drivers for
each product.
The vast majority of furnace fans are
shipped installed in furnaces, so DOE
estimated furnace fan shipments by
projecting furnace shipments in three
market segments: (1) Replacements; (2)
new housing; and (3) new owners in
buildings that did not previously have
a central furnace.
To project furnace replacement
shipments, DOE developed retirement
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functions for furnaces from the lifetime
estimates and applied them to the
existing products in the housing stock.
The existing stock of products is tracked
by vintage and developed from
historical shipments data. The
shipments analysis uses a distribution
of furnace lifetimes to estimate furnace
replacement shipments.
To project shipments to the new
housing market, DOE utilized projected
new housing construction and historic
saturation rates of various furnace and
cooling product types in new housing.
For the final rule, DOE used AEO 2013
for projections of new housing. Furnace
saturation rates in new housing are
provided by the U.S. Census Bureau’s
Characteristics of New Housing.43
DOE also included a small market
segment consisting of households that
become ‘‘new owners’’ of a gas furnace.
This segment consists of households
that have central air conditioning and
non-central heating or central air
conditioning and electric heating and
choose to install a gas furnace.
Lennox stated that the shipment
projections do not appear to be
supported by the record or recent sales
figures, as historical shipments data
from AHRI for gas and oil warm air
furnaces show a downward trend in
shipments. (Lennox, No. 100 at pp. 6–
7) AHRI stated that DOE’s shipment
projections are inaccurate and the
projected numbers significantly skew
the national energy savings estimates.
(AHRI, No. 98 at pp. 4–5)
DOE’s shipments projections are
based on replacement of furnaces
installed over the past few decades and
furnaces installed in future new homes.
Most of the recent downward trend in
shipments is due to lower new
construction in the wake of the financial
crisis. DOE updated historical
shipments with 2013 data, which shows
a growth in gas furnace shipments. DOE
also updated the new construction
forecast based on AEO 2013 projections,
which reflect improving economic
conditions and a future increase of the
new construction market. In addition,
the replacements reflect an updated
furnace retirement function based on
the latest furnace lifetime data. Oil
furnace shipments are projected to
continue to drop in the future.
JCI and AHRI stated that the projected
shipments should account for an echo
effect loss in replacement sales for the
furnaces that were not sold in the years
2008–2012. (JCI, No. 95 at p. 10; AHRI,
No. 98 at pp. 4–5) The projection for
today’s final rule shows a lower level of
43 Available at: https://www.census.gov/
construction/chars/.
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replacement shipments in the 2025–
2030 period, which is a consequence
(i.e., an echo) of the decline in historical
shipments in 2006–2009.
JCI believes that the shipment
projections for furnaces are too
optimistic. It noted that during the years
prior to 2006, demand for large homes
with multiple furnace systems was more
common than it is today. (JCI, No. 95 at
pp. 9–10) Mortex stated that forecasts of
future shipments are unrealistically
high because new homes are smaller
and less likely to have two furnaces.
(Mortex, No. 104 at p. 3) In DOE’s final
rule analysis, DOE assumed that new
homes would not have multiple
furnaces.
It is reasonable to expect that energy
conservation standards for residential
furnace fans that result in higher
furnace prices would have some
dampening effect on sales. Some
consumers might choose to repair their
existing furnace rather than purchase a
new one, or perhaps install an
alternative space heating product. To
estimate the impact on shipments of the
price increase for the considered
efficiency levels, DOE used a relative
price elasticity approach. This approach
also gives some weight to the operating
cost savings from higher-efficiency
products.
Ingersoll Rand stated that the
shipment projections do not account for
a drop off in sales due to higher furnace
prices that will result from using more
expensive components. (Ingersoll Rand,
No. 107 at p. 9) The comment is
incorrect; the relative price elasticity
approach does estimate the impact on
shipments of the price increase for the
considered efficiency levels for the
NOPR and the final rule.
Several stakeholders raised issues
with DOE’s relative price elasticity
approach. They stated that the
household income data and data used to
derive the elasticity are outdated and do
not reflect current trends, and the
household appliances used to derive the
relative price elasticity (refrigerators,
clothes washers and dishwashers) are
inappropriate for this rulemaking. (JCI,
No. 95 at p. 10; Morrison, No. 108 at p.
8; AHRI, No. 98 at pp. 12–13; Goodman,
No. 102 at p. 13) Rheem expressed
similar concerns. (Rheem, No. 83 at p.
12)
In response, DOE notes that there are
very few estimates of consumer demand
elasticity for durable goods. Although
the data that DOE used to estimate
relative price elasticity are not current,
and the analysis focused on products
that differ from furnaces, DOE believes
that consumer behavior with respect to
the impact of higher appliance price on
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demand is not likely to have changed
significantly. One recent paper suggests
that demand elasticity for air
conditioners is inelastic—holding
efficiency constant, a 10% rise in price
leads to a 1.4% decline in sales.44 This
is a lower elasticity than DOE uses in its
analysis. Therefore, DOE believes that it
is reasonable to use the relative price
elasticity approach for today’s final rule.
See chapter 9 in the final rule TSD for
a description of the method.
Mortex stated that a big increase in
the installed cost of a new furnace
under the proposed energy conservation
standards will lead many consumers to
repair rather than replace with a new
furnace. (Mortex, No. 104 at p. 3) In
terms of the overall cost of a new
furnace, the increase attributable to
using a more energy-efficient furnace
fan is relatively small—less than 10
percent—for fans meeting today’s
standards. In any case, the price
elasticity approach described above
captures the potential consumer
response to higher furnace prices, which
often would consist of choosing to
repair an existing furnace rather than
replace it with a new furnace.
AGA urged the Department to include
a robust fuel switching analysis,
including the competing economics of
natural gas furnaces versus both electric
furnaces and heat pumps. (AGA, No.
110 at p. 3) There is a possibility that
for some consumers considering
replacement of a non-condensing gas
furnace, the higher price of a gas furnace
due to today’s standards could lead to
some switching to heat pumps.
However, this switching would only
occur if the CAC is replaced at the same
time as the furnace. Furthermore,
switching to a heat pump would require
additional cost to install backup electric
resistance heating elements. Based on
the above considerations, DOE believes
that any switching to heat pumps due to
today’s standards would be minimal.
The standards would not create any
incentive to switch to electric furnaces
because electric furnaces are subject to
the furnace fan standard and would see
a similar incremental cost as a gas
furnace.
H. National Impact Analysis
The NIA assesses the NES and the
NPV from a national perspective of total
consumer costs and savings expected to
result from new or amended energy
conservation standards at specific
44 David Rapson. Durable Goods and Long-Run
Electricity Demand: Evidence from Air Conditioner
Purchase Behavior. Department of Economics,
University of California, Davis. Available at:
www.econ.ucdavis.edu/faculty/dsrapson/Rapson_
LR_electricity.pdf.
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efficiency levels. DOE determined the
NPV and NES for the potential standard
levels considered for the furnace fan
product classes analyzed. To make the
analysis more accessible and
transparent to all interested parties,
DOE prepared a computer spreadsheet
that uses typical values (as opposed to
probability distributions) as inputs. To
assess the effect of input uncertainty on
NES and NPV results, DOE has
developed its spreadsheet model to
conduct sensitivity analyses by running
scenarios on specific input variables.
Analyzing impacts of potential energy
conservation standards for residential
furnace fans requires comparing
projections of U.S. energy consumption
with new or amended energy
conservation standards against
projections of energy consumption
without the standards. The forecasts
include projections of annual appliance
shipments, the annual energy
consumption of new appliances, and the
purchase price of new appliances.
A key component of DOE’s NIA
analysis is the energy efficiencies
projected over time for the base case
(without new standards) and each of the
standards cases. The projected
efficiencies represent the annual
shipment-weighted energy efficiency of
the products under consideration during
the shipments projection period (i.e.,
from the assumed compliance date of a
new standard to 30 years after
compliance is required).
For the NOPR, DOE reviewed the
information provided by the
manufacturers and modified its estimate
of the long-run trend in market shares
of constant-torque BPM and constantairflow BPM motor furnace fans. The
NOPR analysis assumes a long-run trend
that results in market share of the
constant-torque BPM and constantairflow BPM furnace fans reaching 45
percent in 2048. 78 FR 64099. No
comments were received on this issue
and DOE retained the same approach for
the final rule.
For the NOPR, DOE used a roll-up
scenario for estimating the impacts of
the potential energy conservation
standards for residential furnace fans.
Under the roll-up scenario, DOE
assumes: (1) Products with efficiencies
in the base case that do not meet the
standard level under consideration
would roll up to meet the new standard
level; and (2) products with efficiencies
above the standard level under
consideration would not be affected. Id.
Rheem stated that DOE’s assumption
that the sale of premium products above
the standard level will be unaffected is
unreasonable. (Rheem, No. 83 at p. 3)
DOE acknowledges that the market
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shares of fans with efficiency levels
above a given standard level could
change after compliance with the new
standards is required. Estimating how
manufacturers will respond to new
standards with regard to their marketing
strategy for ‘‘above-standard’’ products
is very difficult, however. Rather than
speculate, DOE believes that it is
preferable to retain a roll-up scenario for
today’s final rule.
For the standards cases, the assumed
efficiency trend after the compliance
year varies depending on the particular
standard. For the case with today’s
standards, the overall BPM motor
market share goes to 100 percent in
2019 and remains at that level. The
shares of the specific BPM motor
designs (i.e., constant-torque BPM,
constant-torque BPM motor + multistage, constant-airflow BPM motor +
multi-stage, and constant-airflow BPM
motor + multi-stage + backwardinclined impeller) remain at the levels
of 2019. The details are provided in
chapter 10 of the final rule TSD.
1. National Energy Savings Analysis
The national energy savings analysis
involves a comparison of national
energy consumption of the considered
products in each potential standards
case (TSL) with consumption in the
base case with no new or amended
energy conservation standards. DOE
calculated the national energy
consumption by multiplying the
number of units (stock) of each product
(by vintage or age) by the unit energy
consumption (also by vintage). Vintage
represents the age of the product. DOE
calculated annual NES based on the
difference in national energy
consumption for the base case (without
new efficiency standards) and for each
higher efficiency standard. DOE
estimated energy consumption and
savings based on site energy and
converted the electricity consumption
and savings to primary energy.
Cumulative energy savings are the sum
of the NES for each year over the
timeframe of the analysis.
DOE calculates primary energy
savings (power plant consumption) from
site electricity savings by applying a
factor to account for losses associated
with the generation, transmission, and
distribution of electricity. For the
NOPR, DOE derived marginal site-topower plant factors based on the version
of the National Energy Modeling System
(NEMS) that corresponds to AEO 2012.
78 FR 64099. The factors change over
time in response to projected changes in
the types of power plants projected to
provide electricity to the country.
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Commenting on DOE’s approach,
AGA stated that it is highly unlikely and
unrealistic that all of the projected
changes in types of power plant used to
generate electricity in this country will
occur between 2019 and 2021 and that
essentially no change will occur from
2031 through 2048. AGA stated that
realistic trend lines to 2048 including a
linear forecast of declining site-to-power
plant energy use should be provided.
(AGA, No. 110 at p. 3)
For the final rule, DOE derived siteto-power plant factors based on the
version of NEMS that corresponds to
AEO 2013. As shown in Figure 10.3.1 in
the final rule TSD, the factor (expressed
as primary energy per site kWh)
declines through 2030 as more efficient
power plants gain share in power
generation. After 2035, there is an
increase due to lower projected share of
highly-efficient combined-cycle power
plants. DOE acknowledges that
projections after 2035 are uncertain, but
it believes that NEMS provides a
reasonable projection.
DOE has historically presented NES
in terms of primary energy savings. In
response to the recommendations of a
committee on ‘‘Point-of-Use and FullFuel-Cycle Measurement Approaches to
Energy Efficiency Standards’’ appointed
by the National Academy of Science,
DOE announced its intention to use fullfuel-cycle (FFC) measures of energy use
and greenhouse gas and other emissions
in the national impact analyses and
emissions analyses included in future
energy conservation standards
rulemakings. 76 FR 51281 (August 18,
2011). After evaluating the approaches
discussed in the August 18, 2011 notice,
DOE published a statement of amended
policy in the Federal Register in which
DOE explained its determination that
NEMS is the most appropriate tool for
its FFC analysis and its intention to use
NEMS for that purpose. 77 FR 49701
(August 17, 2012). The approach used
for today’s final rule is described in
appendix 10–C of the final rule TSD.
JCI and AHRI stated that, for cooling
mode, the NIA spreadsheet model does
not indicate how DOE used the average
annual electricity use values from the
energy use analysis to determine
national energy savings. (JCI, No. 95 at
pp. 4–5; AHRI, No. 98 at p. 6) In the NIA
spreadsheet, the LCC Inputs worksheet
shows how the average annual
electricity use values are used over the
analysis period.
Several stakeholders questioned the
accuracy of the doubling in FFC energy
savings from TSL 3 to TSL 4 from an
incremental efficiency level
improvement of 8 percent for five of the
product classes from adding the multi-
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staging option. (JCI, No. 95 at p 4; EEI,
No. 91 at pp. 307, 309; Morrison, No.
108 at p. 4; AHRI, No. 98 at pp. 4–5;
Lennox, No. 100 at p. 2; Ingersoll Rand,
No. 107 at p. 9) Similarly, AHRI stated
that if the effect of multi-staging was
indeed prominent enough to nearly
double the estimated FFC energy
savings between TSLs 3 and 4, DOE
should have evaluated this effect for
PSC motors as well. (AHRI, No. 98 at p.
5) Morrison stated that for nonweatherized gas furnace fans, it is
inconsistent that TSL 4 could produce
a very large increase in FFC energy
savings over TSL 3 while TSL 2 and 3
have the same national energy savings;
compared to the difference in energy
use between TSL 2 and TSL 3, TSL 4
has a much lower incremental average
electricity savings and higher additional
fuel use compared to TSL 3. (Morrison,
No. 108 at p. 4)
For the final rule, DOE incorporated
new test data on the fan efficiency levels
that were included in TSL 3 (constant
torque BPM motors) and TSL 4
(constant torque BPM motors (multistage)). These data contributed to a
decrease in efficiency for TSL 4 (see
section IV.C.1) With this change, the
increase in savings from TSL 3 to TSL
4 is now smaller than in the NOPR. The
NIA results are presented in section
V.B.3.
Several stakeholders stated that it is
implausible that the furnace fan
standard will save about as much energy
as the 2006 13 SEER rulemaking (76 FR
7185) or the 2013/2015 90% AFUE
furnace and 14 SEER rulemaking (76 FR
37412). (AHRI, No. 98 at p. 6; Ingersoll
Rand, No. 107 at p. 9; Lennox, No. 100
at p. 2; Goodman, No. 102 at p. 6)
Ingersoll Rand stated that the energy
savings from the proposed rule claim to
be greater than savings from the 13
SEER rule, but the energy savings of a
furnace switching from a PSC motor to
a constant torque BPM is nearly an
order of magnitude less than the energy
use of the furnace or heat pump.
(Ingersoll Rand, No. 107 at p. 9)
DOE reviewed the methodology used
to assess the energy savings estimated
for the proposed standards, as discussed
in previous parts of this notice, and
believes that the energy savings
estimated for the considered TSLs are
reasonable. Comparison with other rules
must be done with caution, as the
savings in those rules depends on both
the stringency of the standards and the
base case that was chosen in the
analysis. The fact that the energy
savings of a furnace switching from a
PSC motor to a constant torque BPM is
much less than the energy use of the
furnace or heat pump is not relevant to
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the energy savings associated with
standards for furnaces or heat pumps.
2. Net Present Value Analysis
The inputs for determining NPV are:
(1) Total annual installed cost; (2) total
annual savings in operating costs; (3) a
discount factor to calculate the present
value of costs and savings; (4) present
value of costs; and (5) present value of
savings. DOE calculated net savings
each year as the difference between the
base case and each standards case in
terms of total savings in operating costs
versus total increases in installed costs.
DOE calculated savings over the lifetime
of products shipped in the forecast
period. DOE calculated NPV as the
difference between the present value of
operating cost savings and the present
value of total installed costs. DOE used
a discount factor based on real discount
rates of 3 and 7 percent to discount
future costs and savings to present
values.
For the NPV analysis, DOE calculates
increases in total installed costs as the
difference in total installed cost between
the base case and standards case (i.e.,
once the standards take effect).
DOE assumed no change in
residential furnace fan prices over the
2019–2048 period. In addition, DOE
conducted a sensitivity analysis using
alternative price trends, specifically one
in which prices decline over time, and
another in which prices rise. These
price trends are described in appendix
10–C of the final rule TSD.
DOE expresses savings in operating
costs as decreases associated with the
lower energy consumption of products
bought in the standards case compared
to the base efficiency case. Total savings
in operating costs are the product of
savings per unit and the number of units
of each vintage that survive in a given
year.
DOE estimates the NPV of consumer
benefits using both a 3-percent and a 7percent real discount rate. DOE uses
these discount rates in accordance with
guidance provided by the Office of
Management and Budget (OMB) to
Federal agencies on the development of
regulatory analysis.45 The NPV results
for the residential furnace fan TSLs are
presented in section V.B.3 of this
document.
I. Consumer Subgroup Analysis
A consumer subgroup comprises a
subset of the population that may be
affected disproportionately by new or
revised energy conservation standards
(e.g., low-income consumers, seniors).
45 OMB Circular A–4 (Sept. 17, 2003), section E,
‘‘Identifying and Measuring Benefits and Costs.’’
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The purpose of a consumer subgroup
analysis is to determine the extent of
any such disproportional impacts.
For today’s final rule, DOE evaluated
impacts of potential standards on two
subgroups: (1) Senior-only households
and (2) low-income households. DOE
identified these households in the RECS
sample and used the LCC spreadsheet
model to estimate the impacts of the
considered efficiency levels on these
subgroups. The consumer subgroup
results for the residential furnace fan
TSLs are presented in section V.B.1 of
this document.
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J. Manufacturer Impact Analysis
1. Overview
DOE performed an MIA to estimate
the financial impact of new energy
conservation standards on
manufacturers of residential furnace
fans and to calculate the potential
impact of such standards on
employment and manufacturing
capacity. The MIA has both quantitative
and qualitative aspects. The quantitative
part of the MIA primarily relies on the
Government Regulatory Impact Model
(GRIM), an industry cash-flow model
with inputs specific to this rulemaking.
The key GRIM inputs are data on the
industry cost structure, product costs,
shipments, and assumptions about
markups and conversion expenditures.
The key output is the industry net
present value (INPV). Different sets of
assumptions (markup scenarios) will
produce different results. The
qualitative part of the MIA addresses
factors such as product characteristics,
impacts on particular subgroups of
firms, and important market and
product trends. The complete MIA is
outlined in chapter 12 of the final rule
TSD.
For this rulemaking, DOE considers
the ‘‘furnace fan industry’’ to consist of
manufacturers who assemble furnace
fans as a component of the HVAC
products addressed in this rulemaking.
DOE conducted the MIA for this
rulemaking in three phases. In Phase 1
of the MIA, DOE prepared a profile of
the residential furnace fans industry
that includes a top-down cost analysis
of manufacturers used to derive
preliminary financial inputs for the
GRIM (e.g., sales, general, and
administration (SG&A) expenses;
research and development (R&D)
expenses; and tax rates). DOE used
public sources of information, including
company SEC 10–K filings,46 corporate
annual reports, the U.S. Census
46 U.S. Securities and Exchange Commission,
Annual 10–K Reports (Various Years) (Available at:
https://sec.gov).
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Bureau’s Economic Census,47 and
Hoover’s reports.48
In Phase 2 of the MIA, DOE prepared
an industry cash-flow analysis to
quantify the potential impacts of a new
energy conservation standard. In
general, energy conservation standards
can affect manufacturer cash flow in
three distinct ways: (1) Create a need for
increased investment; (2) raise
production costs per unit; and (3) alter
revenue due to higher per-unit prices
and possible changes in sales volumes.
In Phase 3 of the MIA, DOE
conducted structured, detailed
interviews with a representative crosssection of manufacturers. During these
interviews, DOE discussed engineering,
manufacturing, procurement, and
financial topics to validate assumptions
used in the GRIM and to identify key
issues or concerns. Section IV.J.4 of the
NOPR contains a description of the key
issues manufacturers raised during the
interviews. 78 FR 64068, 64104–05 (Oct.
25, 2013).
Additionally, in Phase 3, DOE
evaluated subgroups of manufacturers
that may be disproportionately
impacted by new standards or that may
not be accurately represented by the
average cost assumptions used to
develop the industry cash-flow analysis.
For example, small manufacturers,
niche players, or manufacturers
exhibiting a cost structure that largely
differs from the industry average could
be more negatively affected. DOE
identified one subgroup (i.e., small
manufacturers) for a separate impact
analysis.
DOE applied the small business size
standards published by the Small
Business Administration (SBA) to
determine whether a company is
considered a small business. 65 FR
30836, 30848 (May 15, 2000), as
amended at 65 FR 53533, 53544 (Sept.
5, 2000) and codified at 13 CFR part
121. To be categorized as a small
business under North American
Industry Classification System (NAICS)
code 333415, ‘‘Air-Conditioning and
Warm Air Heating Equipment and
Commercial and Industrial Refrigeration
Equipment Manufacturing,’’ a
residential furnace fan manufacturer
and its affiliates may employ a
maximum of 750 employees. The 750employee threshold includes all
employees in a business’s parent
Census Bureau, Annual Survey of
Manufacturers: General Statistics: Statistics for
Industry Groups and Industries (Available at:
https://factfinder2.census.gov/faces/nav/jsf/pages/
searchresults.xhtml?refresh=t).
48 Hoovers Inc. Company Profiles (Various
Companies) (Available at: https://
www.hoovers.com).
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38171
company and any other subsidiaries.
Based on this classification, DOE
identified 15 residential furnace fan
manufacturers that qualify as small
businesses. The residential furnace fan
small manufacturer subgroup is
discussed in chapter 12 of the final rule
TSD and in section V.B.2.d of this
document.
2. Government Regulatory Impact Model
DOE uses the GRIM to quantify the
changes in cash flow due to new
standards that result in a higher or
lower industry value. The GRIM
analysis uses a standard, annual cashflow analysis that incorporates
manufacturer costs, markups,
shipments, and industry financial
information as inputs. The GRIM model
changes in costs, distribution of
shipments, investments, and
manufacturer margins that could result
from new energy conservation
standards. The GRIM spreadsheet uses
the inputs to arrive at a series of annual
cash flows, beginning in 2014 and
continuing to 2048. DOE calculated
INPVs by summing the stream of annual
discounted cash flows during this
period. For residential furnace fan
manufacturers, DOE used a real
discount rate of 7.8 percent, which was
derived from industry financials and
then modified according to feedback
received during manufacturer
interviews.
The GRIM calculates cash flows using
standard accounting principles and
compares changes in INPV between a
base case and each standards case. The
difference in INPV between the base
case and a standards case represents the
financial impact of the new energy
conservation standard on
manufacturers. As discussed previously,
DOE collected this information on the
critical GRIM inputs from a number of
sources, including publicly-available
data and interviews with a number of
manufacturers (described in the next
section). The GRIM results are shown in
section V.B.2.a. Additional details about
the GRIM, the discount rate, and other
financial parameters can be found in
chapter 12 of the final rule TSD.
a. Government Regulatory Impact Model
Key Inputs
Manufacturer Production Costs
Manufacturing a higher-efficiency
product is typically more expensive
than manufacturing a baseline product
due to the use of more complex
components, which are typically more
costly than baseline components. The
changes in the MPCs of the analyzed
products can affect the revenues, gross
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margins, and cash flow of the industry,
making these product cost data key
GRIM inputs for DOE’s analysis.
In the MIA, DOE used the MPCs for
each considered efficiency level
calculated in the engineering analysis,
as described in section IV.C and further
detailed in chapter 5 of the final rule
TSD. In addition, DOE used information
from its teardown analysis, described in
chapter 5 of the TSD, to disaggregate the
MPCs into material, labor, and overhead
costs. To calculate the MPCs for
equipment above the baseline, DOE
added the incremental material, labor,
and overhead costs from the engineering
cost-efficiency curves to the baseline
MPCs. These cost breakdowns and
product markups were validated and
revised with manufacturers during
manufacturer interviews.
Shipments Forecast
The GRIM estimates manufacturer
revenues based on total unit shipment
forecasts and the distribution of these
values by efficiency level. Changes in
sales volumes and efficiency mix over
time can significantly affect
manufacturer finances. For this analysis,
the GRIM uses the NIA’s annual
shipment forecasts derived from the
shipments analysis from 2014 (the base
year) to 2048 (the end year of the
analysis period). See chapter 9 of the
final rule TSD for additional details.
mstockstill on DSK4VPTVN1PROD with RULES2
Product and Capital Conversion Costs
New energy conservation standards
would cause manufacturers to incur
one-time conversion costs to bring their
production facilities and product
designs into compliance. DOE evaluated
the level of conversion-related
expenditures that would be needed to
comply with each considered efficiency
level in each product class. For the MIA,
DOE classified these conversion costs
into two major groups: (1) Product
conversion costs; and (2) capital
conversion costs. Product conversion
costs are one-time investments in
research, development, testing,
marketing, and other non-capitalized
costs necessary to make product designs
comply with the new energy
conservation standard. Capital
conversion costs are one-time
investments in property, plant, and
equipment necessary to adapt or change
existing production facilities such that
new product designs can be fabricated
and assembled.
To evaluate the level of capital
conversion expenditures manufacturers
would likely incur to comply with new
energy conservation standards, DOE
used manufacturer interviews to gather
data on the anticipated level of capital
investment that would be required at
each efficiency level. DOE validated
manufacturer comments through
estimates of capital expenditure
requirements derived from the product
teardown analysis and engineering
analysis described in chapter 5 of the
TSD.
DOE assessed the product conversion
costs at each considered efficiency level
by integrating data from quantitative
and qualitative sources. DOE considered
market-share-weighted feedback
regarding the potential costs of each
efficiency level from multiple
manufacturers to determine conversion
costs such as R&D expenditures and
certification costs. Manufacturer data
were aggregated to better reflect the
industry as a whole and to protect
confidential information.
In general, DOE assumes that all
conversion-related investments occur
between the year of publication of the
final rule and the year by which
manufacturers must comply with the
new standard. The investment figures
used in the GRIM can be found in
section IV.J.2 of this notice. For
additional information on the estimated
product and capital conversion costs,
see chapter 12 of the final rule TSD.
b. Government Regulatory Impact Model
Scenarios
Shipment Scenarios
In the NIA, DOE modeled shipments
with a roll-up scenario to represent
possible standards-case efficiency
distributions for the years beginning
2019 (the year that compliance with
new standards would be required)
through 2048 (the end of the analysis
period). The roll-up scenario represents
the case in which all shipments in the
base case that do not meet the new
standard would roll up to meet the new
standard level, with the efficiency of
products already at the new standard
level remaining unchanged. Consumers
in the base case who purchase products
above the standard level are not affected
as they are assumed to continue to
purchase the same product in the
standards case. See chapter 9 of the final
rule TSD for more information.
Markup Scenarios
As discussed above, MSPs include
direct manufacturing production costs
(i.e., labor, materials, and overhead
estimated in DOE’s MPCs) and all nonproduction costs (i.e., SG&A, R&D, and
interest), along with profit. To calculate
the MSPs in the GRIM, DOE applied
non-production cost markups to the
MPCs estimated in the engineering
analysis for each product class and
efficiency level. Modifying these
markups in the standards case yields
different sets of impacts on
manufacturers. For the MIA, DOE
modeled two standards-case markup
scenarios to represent the uncertainty
regarding the potential impacts on
prices and profitability for
manufacturers following the
implementation of new energy
conservation standards: (1) A
preservation of gross margin percentage
markup scenario; and (2) a preservation
of per unit operating profit markup
scenario. These scenarios lead to
different markups values that, when
applied to the inputted MPCs, result in
varying revenue and cash flow impacts.
Under the preservation of gross
margin percentage scenario, DOE
applied a single uniform ‘‘gross margin
percentage’’ markup across all efficiency
levels, which assumes that
manufacturers would be able to
maintain the same amount of profit as
a percentage of revenues at all efficiency
levels within a product class. As
production costs increase with
efficiency, this scenario implies that the
absolute dollar markup will increase as
well. Based on publicly-available
financial information for manufacturers
of residential furnace fans and
comments from manufacturer
interviews, DOE assumed the nonproduction cost markup—which
includes SG&A expenses, R&D
expenses, interest, and profit—to be the
following for each residential furnace
fan product class:
TABLE IV.11—MANUFACTURER MARKUP BY RESIDENTIAL FURNACE FAN PRODUCT CLASS
Product class
Markup
Non-Weatherized, Non-Condensing Gas Furnace Fan (NWG–NC) .......................................................................................................
Non-Weatherized, Condensing Gas Furnace Fan (NWG–C) .................................................................................................................
Weatherized, Non-condensing Gas Furnace Fan (WG–NC) ..................................................................................................................
Non-Weatherized, Non-condensing Oil Furnace Fan (NWO–NC) ..........................................................................................................
Electric Furnace/Modular Blower Fan (EF/MB) .......................................................................................................................................
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38173
TABLE IV.11—MANUFACTURER MARKUP BY RESIDENTIAL FURNACE FAN PRODUCT CLASS—Continued
Product class
Markup
Mobile Home Non-Weatherized, Non-condensing Gas Furnace Fan (MH–NWG–NC) .........................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan (MH–NWG–C) ...................................................................................
Mobile Home Electric Furnace/Modular Blower Fan (MH–EF/MB) ........................................................................................................
Because this markup scenario
assumes that manufacturers would be
able to maintain their gross margin
percentage markups as production costs
increase in response to a new energy
conservation standard, it represents a
high bound to industry profitability.
In the preservation of per unit
operating profit scenario, manufacturer
markups are set so that operating profit
one year after the compliance date of the
new energy conservation standard is the
same as in the base case on a per unit
basis. Under this scenario, as the costs
of production increase under a
standards case, manufacturers are
generally required to reduce their
markups to a level that maintains basecase operating profit per unit. The
implicit assumption behind this markup
scenario is that the industry can only
maintain its operating profit in absolute
dollars per unit after compliance with
the new standard is required. Therefore,
operating margin in percentage terms is
squeezed (reduced) between the base
case and standards case. DOE adjusted
the manufacturer markups in the GRIM
at each TSL to yield approximately the
same earnings before interest and taxes
in the standards case as in the base case.
This markup scenario represents a low
bound to industry profitability under a
new energy conservation standard.
3. Discussion of Comments
During the NOPR public meeting,
interested parties commented on the
assumptions and results of the NOPR
analysis TSD. Oral and written
comments addressed several topics,
including conversion costs, cumulative
regulatory burdens, scope of MIA
coverage, markups analysis,
employment impacts, consumer utility
impacts, and impacts on small
businesses.
a. Conversion Costs
Several manufacturers expressed
concern regarding the DOE’s estimates
of the capital and product conversion
costs, including costs relating to testing
and certification.
Regarding capital conversion costs
associated with a furnace fans standard,
Goodman commented that DOE’s
estimate of zero capital conversion costs
at TSL 4 does not properly reflect
feedback from manufacturer interviews.
(Goodman, No. 102 at p. 10) AHRI
stated that the technology option
associated with TSL 4 would necessitate
changes in manufacturers’ assembly and
subassembly production lines,
including the modification and/or
elimination of current fan housings,
heat exchanger types, and furnace
1.25
1.25
1.15
cabinet sizes, at a cost of $103 million
for the industry. (AHRI, No. 98 at p. 10)
Johnson Controls commented that
compliance with the proposed standard
would likely require them to make a
capital investment ranging from $2.8
million to $4 million. (JCI, No. 95 at p.
2)
In the engineering analysis, most of
the technology options being considered
require only a change in the type of
motor used. At the NOPR stage, DOE
tentatively concluded that TSLs 1
through 5 would not require
manufacturers to incur capital
expenditures for new tooling or
equipment. However, in response to the
above-mentioned public comments
received during the NOPR period, DOE
has revised its methodology for
estimating capital conversion costs at all
TSLs for the final rule. DOE
incorporated all capital conversion cost
values submitted by manufacturers
during the course of MIA interviews and
used a product listing weighted-average
of feedback (based on basic model
listings in the AHRI directory) to
determine conversion costs for the
industry. As a result, capital conversion
costs were revised upward at all TSLs,
as shown in Table IV.12.
TABLE IV.12—FINAL RULE CAPITAL CONVERSION COSTS (CCC)
TSL 1
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Total Industry CCCs ($ millions) ..............................................................
DOE notes that the conversion costs
submitted by AHRI and Johnson
Controls are generally consistent with
DOE’s estimates of conversion costs at
TSL 6 in the final rule. However,
without a more detailed breakdown of
the conversion costs by TSL from those
stakeholders, it was not feasible for DOE
to determine the discrepancies in
capital conversion cost values or to
incorporate their feedback into the
GRIM model.
With regards to product conversion
costs, including costs associated with
compliance, certification, and
enforcement (CC&E), both Trane and
Johnson Controls provided their own
estimates in support of the notion that
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TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
8.8
11.1
11.8
15.1
15.7
134.7
there will be significant testing burden
associated with standards compliance.
(Trane, No. 107 at pp. 2, 6, and JCI, No.
95 at p. 8) Goodman also stated that
investments in additional testing
equipment may be required in order to
keep pace with current and future
testing requirements. (Goodman, No.
102 at p. 11) AHRI and multiple
manufacturers commented that the
performance standard associated with
TSL 4 would require total industry
product conversion costs of $6.2
million. (AHRI, No. 98 at p. 10)
DOE acknowledges manufacturers’
concerns regarding product conversion
cost estimates, including those relating
to testing and certification. Similar to
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the capital conversion cost analysis,
DOE refined its final rule modeling of
product conversion costs to better
reflect information received during
manufacturer interviews. DOE used a
product listing weighted-average (based
on basic model listings in the AHRI
directory) to extrapolate individual
manufacturer feedback to an industry
value for each efficiency level and for
each product class. Additionally, for the
final rule, DOE explicitly incorporated
certification costs into the product
conversion cost estimates used in the
GRIM. These certification costs occur in
the base case and apply in the standards
cases. DOE modeled testing and
certification costs under the assumption
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that larger manufacturers have would
conduct all FER testing in-house, while
small manufacturers would outsource
all certification testing. DOE assumed a
cost of $175 per test per basic model for
large manufacturers (derived from the
summary of testing and certification
cost calculations and overall product
conversion costs. Conversion costs are
discussed in detail in section V.B.2.a of
today’s document and in chapter 12 of
the final rule TSD.
test procedure estimate of a maximum
of 4 hours per test) (79 FR 500 (Jan. 3,
2014)) and a cost of $2,000 per test per
basic model for small manufacturers (77
FR 28674 (May 15, 2012)). See Table
IV.13 and Table IV.14 below for a
TABLE IV.13—TESTING AND CERTIFICATION COSTS
Value
General assumptions:
[a] Number of FER tests required per Basic Model .........................................................................................................................
[b] Total Industry Number of Basic Models 1 ...................................................................................................................................
[c] Number of Basic Models for Large Manufacturers .....................................................................................................................
[d] Number of Basic Models for Small Manufacturers .....................................................................................................................
Large manufacturer assumptions:
[e] Labor rate ($/hr) 2 ........................................................................................................................................................................
[f] Time required per test (hours) 3 ...................................................................................................................................................
Small manufacturer assumptions:
[g] Cost per FER test (outsource) ($) 4 = .........................................................................................................................................
[h] FER costs per model for Large Manufacturer ($) = [a]*[e]*[f] ....................................................................................................
[i] FER costs per model for Small Manufacturer ($) = [a]*[g] ..........................................................................................................
Total Industry FER costs ($ millions) = [h]*[c] + [i]*[d] .....................................................................................................................
Total Industry FER costs rescaled to account for EF/MB and MH–EF/MB product classes ($ millions) 5 .....................................
2
2,254
1,943
311
43.73
4
$2,000
$350
$4,000
$1.9
$2.2
1 AHRI
Directory: Residential Furnaces.
of Labor Statistics, 2012 mean hourly wage for all engineers.
3 2012–05–15 Test Procedures for Residential Furnace Fans; Notice of proposed rulemaking, section IV, part B.
4 2012–05–15 Test Procedures for Residential Furnace Fans; Notice of proposed rulemaking, section IV, part B.
5 The AHRI residential furnaces database does not contain electric furnaces/modular blowers. In order to account for CC&E costs relates to
these products (standard and MH), DOE rescaled the $1.9 value by 12%, which is the estimated proportion of shipments for these two categories combined. $2.2 is the value used in the GRIM.
2 Bureau
TABLE IV.14—PRODUCT CONVERSION COSTS
Baseline
Total Number of Basic Models 1 ............................
Average Testing and Certification Costs + R&D
Costs per Basic Model ($) .................................
Total Industry PCCs ($ millions) ............................
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1 AHRI
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
2,254
..................
..................
..................
..................
..................
..................
853
2.2
8,449
18.8
10,577
23.6
11,356
25.3
11,434
25.5
12,157
27.1
13,182
29.4
Directory: Residential Furnaces.
b. Cumulative Regulatory Burden
Interested parties expressed concern
over the cumulative regulatory burden
that would result from a residential
furnace fan energy conservation
standard. AHRI, Morrison, and Lennox
commented that DOE did not account
for the cumulative impacts of additional
DOE regulations, including energy
conservation standards or potential
standards for commercial and industrial
fans and blowers, commercial package
air conditioners and heat pumps, and
commercial warm air furnaces. The
three stakeholders also asserted that
DOE did not address testing burdens
associated with the recently finalized
test procedures for two-stage and
modulating condensing furnaces and
boilers, and potential updates to test
procedures for residential furnaces and
boilers. (AHRI, No. 98 at p. 8–9;
Morrison, No. 108 at p. 6; Lennox, No.
100 at p. 8) Rheem argued that DOE
failed to address cumulative burdens
relating to regulations for water heaters,
boilers, pool heaters, and commercial
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refrigeration equipment. (Rheem, No. 83
at p. 14)
DOE notes that the energy
conservation standard rulemakings for
commercial and industrial fans and
blowers, commercial package air
conditioners and heat pumps,
commercial warm air furnaces, water
heaters, residential boilers, commercial
boilers, and pool heaters are all
regulation currently in progress. No
standards have been proposed, and no
final regulations have been issued for
these rulemakings. It is DOE’s policy not
to include the impacts of regulatory
proposals until the analyses are
complete and the standards are
finalized. Until such rulemaking is
complete, it is unclear what, if any,
requirements will be adopted for the
products in question. Consequently, it
would be speculative to try to include
incomplete regulatory actions in an
assessment of cumulative regulatory
burden. With regard to the test
procedure final rule for residential
furnaces and boilers published on July
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10, 2013, the changes have a compliance
date of January 6, 2014. 78 FR 41265.
Because the regulation goes into effect
before 2016, it is outside of the 3-year
window set for consideration in the
cumulative regulatory burden analysis.
With regard to the commercial
refrigeration equipment (CRE) energy
conservation standard rulemaking, at
the time of the residential furnace fan
rulemaking NOPR publication, the final
rule for CRE standards had not yet been
published. The final rule for CRE
standards was published on March 28,
2014 and is now included in the final
rule cumulative regulatory burden
review in section V.B.2.e. 79 FR 17725.
Johnson Controls commented that
DOE should consider the cumulative
impacts of State or local weatherization
programs that may be restrictive on
HVAC equipment selections, as well as
building code standards at State,
national, and international levels. In
addition, JCI believes DOE should
include the impact of commercial
product energy efficiency standards,
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alternate refrigeration requirements, and
modifications to existing or the
generation of new building performance
standards, such as ASHRAE standards.
(JCI, No. 95 at p. 7).
DOE considers cumulative regulatory
burden pursuant to the directions in the
Process Rule (10 CFR part 430, subpart
C, appendix A). DOE notes that States
and localities are generally preempted
from requiring HVAC standards beyond
the Federal minimum through building
codes or other regulatory requirements.
Once finalized, Federal commercial
energy efficiency standards, alternative
refrigeration requirements, and
ASHRAE 90.1 standards that go into
effect within 3 years of the effective date
of today’s standard are considered in the
cumulative regulatory burden analysis.
AHRI and Morrison commented that
DOE failed to provide quantitative
estimates of the incremental burden
imposed by the additional DOE
standards impacting furnace fan
manufacturers. As a result, both parties
do not feel that such impacts were
adequately reflected in the GRIM.
(AHRI, No. 98 at p. 9, and Morrison, No.
108 at p. 7).
In the final rule cumulative regulatory
burden section, DOE has provided an
explicit review of the conversion costs
associated with DOE energy
conservation standards that impact the
manufacturers covered under the
residential furnace fan rulemaking. For
more information, please see section
V.B.2.e of this document.
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c. Scope of MIA Coverage
AHRI and Rheem commented that
impacts on motor manufacturers should
be included in the manufacturing
impact analysis. (AHRI, No. 43 at p. 151,
and Rheem, No. 83 at p. 6)
DOE’s manufacturer impact analysis
focuses on the manufacturers that have
the direct burden of complying with the
energy conservation standard. In this
rulemaking, the manufacturer of the
residential furnace has the burden of
certifying and labeling the furnace fan
performance. Motors manufacturers are
a component supplier but do not have
a direct compliance burden associated
with this rule.
d. Markups Analysis
AHRI provided comments relating to
both markup scenarios used in the
GRIM. With regards to the preservation
of gross margin percentage markup
scenario, AHRI commented that it is
unreasonable for DOE to assume that, as
manufacturer production costs increase
in response to an energy conservation
standard, manufacturers would be able
to maintain the same gross margin
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percentage markup as the base case.
(AHRI, No. 98 at p. 10) AHRI continued
by commenting that the preservation of
operating profit scenario is also
inaccurate since it implies that
manufacturer markups are set so that
operating profit one year after the
compliance date of the new energy
conservation standards is the same as in
the base case. AHRI believes that the
one year time period is an extremely
optimistic assumption and that a fiveyear time period would be a more
realistic average for the industry. (AHRI,
No. 98 at p. 10)
DOE intends for the preservation of
gross margin percentage and
preservation of per-unit operating profit
markup scenarios to represent the upper
and lower bounds for the performance
of the industry as a result of new
standards. The preservation of gross
margin percentage scenario assumes
that manufacturers are able to pass on
all increases in MPC that result from
standards to their first customers.
Additionally, the scenario assumes
manufacturers are able to maintain the
existing markup on the incremental
manufacturer production costs that
result from the standard, thereby
allowing manufacturers to recover
portions of their conversion cost
investments. The preservation of perunit operating profit scenario assumes
that manufacturers are not able to
generate greater operating profit per unit
sold in the standards case. Additionally,
the scenario assumes that manufacturers
are not able to recover any of their
conversion cost investments. By
applying these two scenarios, DOE
models examine the range of potential
industry impacts that reflect
manufacturers’ varying ability to pass
costs on to customers and recover
conversion costs. The scenario
described by AHRI appears to relate to
manufacturers’ ability to recover
conversion costs, which is likely not
possible by one year following the
standard year. However, the
preservation of operating profit per-unit
markup scenario assumes only that
manufacturers will maintain the same
annual operating profit as in the base
case in the year after the standards go
into effect. DOE believes that
manufacturers’ annual operating profit
will be relatively constant in the years
following the standard, and,
accordingly, the choice between a oneyear and five-year time horizon for this
scenario is arbitrary.
e. Employment Impacts
AHRI and EEI commented that it is
unrealistic to assume there would be no
reductions in domestic production
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employment at TSLs 1 through 5. This
is because labor costs will increase with
higher design options, and,
subsequently, manufacturers will try to
compensate by reducing labor. (AHRI,
No. 98 at p. 10 and EEI, No. 43 at p. 349)
Additionally, AHRI commented that
subsection 12.7.1 in the NOPR TSD
accounts for line-supervisors as
production workers who contribute
towards the manufacture of furnace
fans, but should also account for
engineers and managers in supervisory
roles who may not be involved in the
day-to-day assembly line operations.
(AHRI, No. 98 at p. 11)
At the NOPR stage, DOE’s
employment analysis only provided an
upper bound to employment changes.
These upper bound impacts were
directly correlated to changes in
shipments and changes in per-unit labor
inputs. For the final rule, DOE uses the
same employment model to determine
the upper bound of employment
impacts. At the lower bound, DOE
models the scenario in which all
production moves to lower production
cost countries. In reference to AHRI’s
second comment, DOE does account for
non-production workers in the GRIM
and presents these results along with
revised estimates of domestic
production employment in chapter 12 of
the final rule TSD.
f. Consumer Utility
Morrison commented in support of
DOE’s previously-stated concern
relating to the use of multiple rating
systems on a given product. Morrison
emphasized that this would indeed lead
to consumer confusion. (Morrison, No.
108 at p. 2)
DOE understands manufacturer
concern relating to multiple ratings.
However, DOE is required by legislation
to set a separate standard and an
associated metric for the covered
product, furnace fans.
g. Small Businesses
In reference to the Regulatory
Flexibility Analysis contained in the
NOPR, Mortex expressed concern that
DOE significantly underestimated
capital and product conversion costs.
According to Mortex, even at the
underestimated level, the calculated
impact to small businesses (conversion
costs of 5.1 percent of annual revenues)
would be highly detrimental. (Mortex,
No. 104 at pp. 2–3)
DOE has revised its analysis of
conversion costs for the final rule. The
increase in conversion costs is reflected
in the Final Regulatory Flexibility
Analysis (FRFA), in section VI.B of this
notice. To help portray the magnitude of
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the conversion costs relative to the size
of the average small business, the
conversion costs (which are invested
over a five-year period) are compared to
the financial metric of a single year’s
operation.
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K. Emissions Analysis
In the emissions analysis, DOE
estimated the reduction in power sector
emissions of carbon dioxide (CO2),
nitrogen oxides (NOX), sulfur dioxide
(SO2), and mercury (Hg) from potential
energy conservation standards for the
considered products (here, furnace
fans). In addition to estimating impacts
of standards on power sector emissions,
DOE estimated emissions impacts in
production activities (extracting,
processing, and transporting fuels) that
provide the energy inputs to power
plants. These are referred to as
‘‘upstream’’ emissions. Together, these
emissions account for the full-fuel-cycle
(FFC). In accordance with DOE’s FFC
Statement of Policy (76 FR 51281
(August 18, 2011) as amended at 77 FR
49701 (August 17, 2012)), this FFC
analysis also includes impacts on
emissions of methane (CH4) and nitrous
oxide (N2O), both of which are
recognized as greenhouse gases.
DOE primarily conducted the
emissions analysis using emissions
factors for CO2 and most of the other
gases derived from data in AEO 2013,
supplemented by data from other
sources. DOE developed separate
emissions factors for power sector
emissions and upstream emissions. The
method that DOE used to derive
emissions factors is described in chapter
13 of the final rule TSD.
For CH4 and N2O, DOE calculated
emissions reduction in tons and also in
terms of units of carbon dioxide
equivalent (CO2eq). Gases are converted
to CO2eq by multiplying each ton of the
greenhouse gas by the gas’s global
warming potential (GWP) over a 100year time horizon. Based on the Fourth
Assessment Report of the
Intergovernmental Panel on Climate
Change,49 DOE used GWP values of 25
for CH4 and 298 for N2O.
EIA prepares the Annual Energy
Outlook using the National Energy
49 Forster, P., V. Ramaswamy, P. Artaxo, T.
Berntsen, R. Betts, D.W. Fahey, J. Haywood, J. Lean,
D.C. Lowe, G. Myhre, J. Nganga, R. Prinn, G. Raga,
M. Schulz and R. Van Dorland, 2007: Changes in
Atmospheric Constituents and in Radiative Forcing.
In Climate Change 2007: The Physical Science
Basis. Contribution of Working Group I to the
Fourth Assessment Report of the Intergovernmental
Panel on Climate Change. S. Solomon, D. Qin, M.
Manning, Z. Chen, M. Marquis, K.B. Averyt, M.
Tignor and H.L. Miller, Editors (2007) Cambridge
University Press, Cambridge, United Kingdom and
New York, NY, USA. p. 212.
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Modeling System (NEMS). Each annual
version of NEMS incorporates the
projected impacts of existing air quality
regulations on emissions. AEO 2013
generally represents current legislation
and environmental regulations,
including recent government actions, for
which implementing regulations were
available as of December 31, 2012.
SO2 emissions from affected electric
generating units (EGUs) are subject to
nationwide and regional emissions capand-trade programs. Title IV of the
Clean Air Act sets an annual emissions
cap on SO2 for affected EGUs in the 48
contiguous States (42 U.S.C. 7651 et
seq.) and the District of Columbia (DC).
SO2 emissions from 28 eastern States
and DC were also limited under the
Clean Air Interstate Rule (CAIR; 70 FR
25162 (May 12, 2005)), which created an
allowance-based trading program. CAIR
was remanded to the U.S.
Environmental Protection Agency (EPA)
by the U.S. Court of Appeals for the
District of Columbia, but it remained in
effect.50 See North Carolina v. EPA, 550
F.3d 1176 (D.C. Cir. 2008); North
Carolina v. EPA, 531 F.3d 896 (D.C. Cir.
2008). In 2011, EPA issued a
replacement for CAIR, the Cross-State
Air Pollution Rule (CSAPR). 76 FR
48208 (August 8, 2011). On August 21,
2012, the DC Circuit issued a decision
to vacate CSAPR.51 The court ordered
EPA to continue administering CAIR.
The AEO 2013 emissions factors used
for today’s final rule assume that CAIR
remains a binding regulation through
2040.
The attainment of emissions caps is
typically flexible among EGUs and is
enforced through the use of tradable
emissions allowances. Under existing
EPA regulations, any excess SO2
emissions allowances resulting from the
lower electricity demand caused by the
adoption of a new or amended
efficiency standard could be used to
allow offsetting increases in SO2
emissions by any regulated EGU. In past
rulemakings, DOE recognized that there
was uncertainty about the effects of
efficiency standards on SO2 emissions
covered by the existing cap-and-trade
system, but it concluded that negligible
reductions in power sector SO2
emissions would occur as a result of
standards.
Beginning in 2015, however, SO2
emissions will fall as a result of the
Mercury and Air Toxics Standards
50 See North Carolina v. EPA, 550 F.3d 1176 (D.C.
Cir. 2008); North Carolina v. EPA, 531 F.3d 896
(D.C. Cir. 2008).
51 See EME Homer City Generation, LP v. EPA,
696 F.3d 7, 38 (D.C. Cir. 2012), cert. granted, 81
U.S.L.W. 3567, 81 U.S.L.W. 3696, 81 U.S.L.W. 3702
(U.S. June 24, 2013) (No. 12–1182).
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(MATS) for power plants. 77 FR 9304
(Feb. 16, 2012). In the final MATS rule,
EPA established a standard for hydrogen
chloride as a surrogate for acid gas
hazardous air pollutants (HAP), and also
established a standard for SO2 (a nonHAP acid gas) as an alternative
equivalent surrogate standard for acid
gas HAP. The same controls are used to
reduce HAP and non-HAP acid gas;
thus, SO2 emissions will be reduced as
a result of the control technologies
installed on coal-fired power plants to
comply with the MATS requirements
for acid gas. AEO2013 assumes that, in
order to continue operating, coal plants
must have either flue gas
desulfurization or dry sorbent injection
systems installed by 2015. Both
technologies, which are used to reduce
acid gas emissions, also reduce SO2
emissions. Under the MATS, NEMS
shows a reduction in SO2 emissions
when electricity demand decreases (e.g.,
as a result of energy efficiency
standards). Emissions will be far below
the cap that would be established by
CAIR, so it is unlikely that excess SO2
emissions allowances resulting from the
lower electricity demand would be
needed or used to allow offsetting
increases in SO2 emissions by any
regulated EGU. Therefore, DOE believes
that energy efficiency standards will
reduce SO2 emissions in 2015 and
beyond.
CAIR established a cap on NOX
emissions in 28 eastern States and the
District of Columbia. Energy
conservation standards are expected to
have little effect on NOX emissions in
those States covered by CAIR because
excess NOX emissions allowances
resulting from the lower electricity
demand could be used to allow
offsetting increases in NOX emissions.
However, standards would be expected
to reduce NOX emissions in the States
not affected by the caps, so DOE
estimated NOX emissions reductions
from the standards considered in
today’s final rule for these States.
The MATS limit mercury emissions
from power plants, but they do not
include emissions caps, and, as such,
DOE’s energy conservation standards
would likely reduce Hg emissions. DOE
estimated mercury emissions reduction
using emissions factors based on AEO
2013, which incorporates the MATS.
JCI and EEI stated that DOE did not
consider the impact of the EPA
rulemakings on new and existing power
plants, which likely will materially
affect the projections of CO2 emissions
reductions on which the DOE’s SCC
benefit calculations are based. (JCI, No.
95 at p. 10–11; EEI, No. 87 at p. 9)
Consistent with past practice, DOE has
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concluded that it would not be
appropriate for its analysis to assume
implementation of regulations that are
not in effect at this time. The shape of
any final EPA regulations is uncertain,
as is the outcome of potential legal
challenges to those regulations.
EEI stated that, to be consistent with
other rulemakings, DOE should use
modeling that calculates no emissions
reductions as a result of efficiency
standards where such emissions are
capped by State, regional, or Federal
regulations. In particular, DOE should
eliminate any estimated CO2 reductions
in California and in the Northeastern/
Mid-Atlantic states that participate in
the Regional Greenhouse Gas Initiative
(RGGI). (EEI, No. 87 at p. 10) Morrison
stated that different agencies
simultaneously addressing similar
sources of CO2 emissions should not
double-count emissions reductions.
(Morrison, No. 108 at p. 10)
As stated above, DOE based its
emissions analysis on AEO 2013, which
represents current legislation and
environmental regulations, including
recent government actions, for which
implementing regulations were
available as of December 31, 2012. AEO
2013 accounts for the implementation of
regional and State air emissions
regulations, including those cited by
EEI.52 Its analysis also considers the
impact of caps set by Federal
regulations, as discussed above.
Consequently, the emissions reductions
estimated to result from today’s
standards are over and above any
reductions attributable to other State,
regional, or Federal regulations.
EEI stated that DOE’s analysis
significantly overestimates the future
emissions from power plants, as coalfired power plants are being retired and
large amounts of wind and solar
capacity are being added. It stated that
due to these factors, along with EPA
regulations, there will be a significant
reduction in the baseline emissions
from power plants and a reduced
emissions impact from any efficiency
standard. (EEI, No. 87 at p. 9)
DOE bases its emissions analysis on
the latest projections from the AEO,
which consider retirement of coal-fired
power plants, addition of wind and
solar capacity, and current EPA
regulations. Decline in baseline
emissions from power plants does not
mean that there would be reduced
impact from any efficiency standard,
however. The impact of standards on
electricity demand takes place at the
52 See Assumptions to AEO 2013 (Available at:
https://www.eia.gov/forecasts/aeo/assumptions/).
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margin, and DOE’s analysis endeavors
to reflect this marginal impact.
EEI stated that it is not clear how or
why the power plant emissions factors
would increase for any regulated
emission (SO2, NOX, Hg, and CO2) after
2025 or 2030, based on current trends
and Federal and State regulations. (EEI,
No. 87 at p. 10) DOE agrees that average
power plant emissions factors for the
Nation as a whole would likely not
increase after 2025 or 2030. DOE’s
analysis uses marginal emissions
factors, however, which depend on
changes to the mix of generation
capacity by fuel type induced by a
marginal reduction in electricity
demand for a particular end use (e.g.,
residential heating). The behavior of
marginal emissions factors can be
significantly different from the behavior
of average emissions factors. Marginal
emissions factors are very sensitive to
shifts in the capacity mix relative to the
AEO reference case, whereas average
emissions factors are not affected by
these small shifts.
L. Monetizing Carbon Dioxide and Other
Emissions Impacts
As part of the development of the
standards in this final rule, DOE
considered the estimated monetary
benefits from the reduced emissions of
CO2 and NOX that are expected to result
from each of the TSLs considered. In
order to make this calculation analogous
to the calculation of the NPV of
consumer benefit, DOE considered the
reduced emissions expected to result
over the lifetime of equipment shipped
in the forecast period for each TSL. This
section summarizes the basis for the
monetary values used for each of these
emissions and presents the values
considered in this final rule.
For today’s final rule, DOE is relying
on a set of values for the SCC that was
developed by a Federal interagency
process. The basis for these values is
summarized below, and a more detailed
description of the methodologies used is
provided as an appendix to chapter 14
of the final rule TSD.
1. Social Cost of Carbon
The SCC is an estimate of the
monetized damages associated with an
incremental increase in carbon
emissions in a given year. It is intended
to include (but is not limited to) changes
in net agricultural productivity, human
health, property damages from
increased flood risk, and the value of
ecosystem services. Estimates of the
SCC are provided in dollars per metric
ton of carbon dioxide. A domestic SCC
value is meant to reflect the value of
damages in the United States resulting
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from a unit change in carbon dioxide
emissions, while a global SCC value is
meant to reflect the value of damages
worldwide.
Under section 1(b) of Executive Order
12866, agencies must, to the extent
permitted by law, ‘‘assess both the costs
and the benefits of the intended
regulation and, recognizing that some
costs and benefits are difficult to
quantify, propose or adopt a regulation
only upon a reasoned determination
that the benefits of the intended
regulation justify its costs.’’ The purpose
of the SCC estimates presented here is
to allow agencies to incorporate the
monetized social benefits of reducing
CO2 emissions into cost-benefit analyses
of regulatory actions. The estimates are
presented with an acknowledgement of
the many uncertainties involved and
with a clear understanding that they
should be updated over time to reflect
increasing knowledge of the science and
economics of climate impacts.
As part of the interagency process that
developed these SCC estimates,
technical experts from numerous
agencies met on a regular basis to
consider public comments, explore the
technical literature in relevant fields,
and discuss key model inputs and
assumptions. The main objective of this
process was to develop a range of SCC
values using a defensible set of input
assumptions grounded in the existing
scientific and economic literatures. In
this way, key uncertainties and model
differences transparently and
consistently inform the range of SCC
estimates used in the rulemaking
process.
Monetizing Carbon Dioxide Emissions
When attempting to assess the
incremental economic impacts of carbon
dioxide emissions, the analyst faces a
number of challenges. A report from the
National Research Council 53 points out
that any assessment will suffer from
uncertainty, speculation, and lack of
information about: (1) Future emissions
of GHGs; (2) the effects of past and
future emissions on the climate system;
(3) the impact of changes in climate on
the physical and biological
environment; and (4) the translation of
these environmental impacts into
economic damages. As a result, any
effort to quantify and monetize the
harms associated with climate change
will raise questions of science,
economics, and ethics and should be
viewed as provisional.
53 National Research Council. Hidden Costs of
Energy: Unpriced Consequences of Energy
Production and Use (2009) National Academies
Press: Washington, DC.
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Despite the limits of both
quantification and monetization, SCC
estimates can be useful in estimating the
social benefits of reducing CO2
emissions. The agency can estimate the
benefits from reduced (or costs from
increased) emissions in any future year
by multiplying the change in emissions
in that year by the SCC values
appropriate for that year. The net
present value of the benefits can then be
calculated by multiplying each of these
future benefits by an appropriate
discount factor and summing across all
affected years.
It is important to emphasize that the
interagency process is committed to
updating these estimates as the science
and economic understanding of climate
change and its impacts on society
improves over time. In the meantime,
the interagency group will continue to
explore the issues raised by this analysis
and consider public comments as part of
the ongoing interagency process.
Development of Social Cost of Carbon
Values
In 2009, an interagency process was
initiated to offer a preliminary
assessment of how best to quantify the
benefits from reducing carbon dioxide
emissions. To ensure consistency in
how benefits are evaluated across
Federal agencies, the Administration
sought to develop a transparent and
defensible method, specifically
designed for the rulemaking process, to
quantify avoided climate change
damages from reduced CO2 emissions.
The interagency group did not
undertake any original analysis. Instead,
models, while respecting the different
approaches to quantifying damages
taken by the key modelers in the field.
An extensive review of the literature
was conducted to select three sets of
input parameters for these models:
climate sensitivity, socio-economic and
emissions trajectories, and discount
rates. A probability distribution for
climate sensitivity was specified as an
input into all three models. In addition,
the interagency group used a range of
scenarios for the socio-economic
parameters and a range of values for the
discount rate. All other model features
were left unchanged, relying on the
model developers’ best estimates and
judgments.
The interagency group selected four
sets of SCC values for use in regulatory
analyses. Three sets of values are based
on the average SCC from the three IAMs,
at discount rates of 2.5, 3, and 5 percent.
The fourth set, which represents the
95th percentile SCC estimate across all
three models at a 3-percent discount
rate, was included to represent higherthan-expected impacts from temperature
change further out in the tails of the
SCC distribution. The values grow in
real terms over time. Additionally, the
interagency group determined that a
range of values from 7 percent to 23
percent should be used to adjust the
global SCC to calculate domestic
effects,54 although preference is given to
consideration of the global benefits of
reducing CO2 emissions. Table IV.15
presents the values in the 2010
interagency group report,55 which is
reproduced in appendix 14A of the DOE
final rule TSD.
it combined SCC estimates from the
existing literature to use as interim
values until a more comprehensive
analysis could be conducted. The
outcome of the preliminary assessment
by the interagency group was a set of
five interim values: Global SCC
estimates for 2007 (in 2006$) of $55,
$33, $19, $10, and $5 per metric ton of
CO2. These interim values represented
the first sustained interagency effort
within the U.S. government to develop
an SCC for use in regulatory analysis.
The results of this preliminary effort
were presented in several proposed and
final rules.
Current Approach and Key
Assumptions
After the release of the interim values,
the interagency group reconvened on a
regular basis to generate improved SCC
estimates. Specially, the group
considered public comments and
further explored the technical literature
in relevant fields. The interagency group
relied on three integrated assessment
models commonly used to estimate the
SCC: the FUND, DICE, and PAGE
models. These models are frequently
cited in the peer-reviewed literature and
were used in the last assessment of the
Intergovernmental Panel on Climate
Change (IPCC). Each model was given
equal weight in the SCC values that
were developed.
Each model takes a slightly different
approach to model how changes in
emissions result in changes in economic
damages. A key objective of the
interagency process was to enable a
consistent exploration of the three
TABLE IV.15—ANNUAL SCC VALUES FROM 2010 INTERAGENCY REPORT, 2010–2050
[2007$ per metric ton CO2]
Discount rate
Year
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3%
2.5%
3%
Average
2010
2015
2020
2025
2030
2035
2040
2045
2050
5%
Average
Average
95th percentile
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
54 It is recognized that this calculation for
domestic values is approximate, provisional, and
highly speculative. There is no a priori reason why
domestic benefits should be a constant fraction of
net global damages over time.
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4.7
5.7
6.8
8.2
9.7
11.2
12.7
14.2
15.7
21.4
23.8
26.3
29.6
32.8
36.0
39.2
42.1
44.9
55 Social Cost of Carbon for Regulatory Impact
Analysis Under Executive Order 12866. Interagency
Working Group on Social Cost of Carbon, United
States Government (February 2010) (Available at:
www.whitehouse.gov/sites/default/files/omb/
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35.1
38.4
41.7
45.9
50.0
54.2
58.4
61.7
65.0
64.9
72.8
80.7
90.4
100.0
109.7
119.3
127.8
136.2
inforeg/for-agencies/Social-Cost-of-Carbon-forRIA.pdf).
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The SCC values used for today’s
notice were generated using the most
recent versions of the three integrated
assessment models that have been
published in the peer-reviewed
literature.56
38179
models at the 3-percent discount rate.
However, for purposes of capturing the
uncertainties involved in regulatory
impact analysis, the interagency group
emphasizes the importance of including
all four sets of SCC values.
Table IV.16 shows the updated sets of
SCC estimates in 5-year increments from
2010 to 2050. The full set of annual SCC
estimates between 2010 and 2050 is
reported in appendix 14B of the DOE
final rule TSD. The central value that
emerges is the average SCC across
TABLE IV.16—ANNUAL SCC VALUES FROM 2013 INTERAGENCY REPORT, 2010–2050
[2007$ per metric ton CO2]
Discount rate
Year
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3%
2.5%
3%
Average
2010
2015
2020
2025
2030
2035
2040
2045
2050
5%
Average
Average
95th percentile
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
.........................................................................................
11
11
12
14
16
19
21
24
26
32
37
43
47
52
56
61
66
71
51
57
64
69
75
80
86
92
97
89
109
128
143
159
175
191
206
220
It is important to recognize that a
number of key uncertainties remain, and
that current SCC estimates should be
treated as provisional and revisable
because they will evolve with improved
scientific and economic understanding.
The interagency group also recognizes
that the existing models are imperfect
and incomplete. The 2009 National
Research Council report mentioned
above points out that there is tension
between the goal of producing
quantified estimates of the economic
damages from an incremental ton of
carbon and the limits of existing efforts
to model these effects. There are a
number of analytical challenges that are
being addressed by the research
community, including research
programs housed in many of the Federal
agencies participating in the interagency
process to estimate the SCC. The
interagency group intends to
periodically review and reconsider
those estimates to reflect increasing
knowledge of the science and
economics of climate impacts, as well as
improvements in modeling.
In summary, in considering the
potential global benefits resulting from
reduced CO2 emissions, DOE used the
values from the 2013 interagency report
adjusted to 2013$ using the GDP price
deflator. For each of the four sets of SCC
values, the values for emissions in 2015
were $12.0, $40.5, $62.4, and $119 per
metric ton avoided (values expressed in
2013$). DOE derived values after 2050
using the relevant growth rates for the
2040–2050 period in the interagency
update.
DOE multiplied the CO2 emissions
reduction estimated for each year by the
SCC value for that year in each of the
four cases. To calculate a present value
of the stream of monetary values, DOE
discounted the values in each of the
four cases using the specific discount
rate that had been used to obtain the
SCC values in each case.
In responding to the NOPR, many
commenters questioned the scientific
and economic basis of the SCC values.
A number of stakeholders stated that
DOE should not use SCC values to
establish monetary figures for emissions
reductions until the SCC undergoes a
more rigorous notice, review, and
comment process. (Morrison, No. 108 at
p. 9; JCI, No. 95 at p. 10; AHRI, No. 98
at pp. 12–13; The Associations, No. 99
at p. 2; NAM, No. 84 at p. 1–2; Cato
Institute, No. 81 at p. 2) Ingersoll Rand
agrees with AHRI’s comments. (Ingersoll
Rand, No. 107 at p. 11) Rheem stated
that the Federal Interagency Working
Group has failed to disclose and
quantify key uncertainties to inform
decision makers and the public about
the effects and uncertainties of
alternative regulatory actions, as
required by OMB. (Rheem, No. 83 at p.
9) NAM stated that the SCC estimates
were developed without sufficient
transparency, inadequate supporting
information related to assumptions and
other data, and a failure to peer-review
critical model inputs. (NAM, No. 84 at
pp. 1–2) Morrison stated that the SCC
estimates are the product of an opaque
process and that any pretensions to their
supposed accuracy are unsupportable.
(Morrison, No. 108 at p. 9) JCI stated
that the SCC has not been adequately
noticed and reviewed before being used
in this NOPR or any other rulemaking.
JCI added that it is aware that the SCC
process is undergoing a current review
and comment process, which has the
potential for significant changes in how
those SCC calculations are used in any
rulemakings. (JCI, No. 95 at p. 10)
Rheem stated that even if the SCC
estimate development process were
transparent, rigorous, and peerreviewed, the modeling conducted in
this effort does not offer a reasonably
acceptable range of accuracy for use in
policymaking. (Rheem, No. 83 at p. 9)
In conducting the interagency process
that developed the SCC values,
technical experts from numerous
agencies met on a regular basis to
consider public comments, explore the
technical literature in relevant fields,
and discuss key model inputs and
assumptions. Key uncertainties and
model differences transparently and
consistently inform the range of SCC
estimates. These uncertainties and
model differences are discussed in the
interagency working group’s reports,
which are reproduced in appendix 14A
and 14B of the final rule TSD, as are the
major assumptions. The 2010 SCC
56 Technical Update of the Social Cost of Carbon
for Regulatory Impact Analysis Under Executive
Order 12866, Interagency Working Group on Social
Cost of Carbon, United States Government (May
2013; revised November 2013) (Available at:
https://www.whitehouse.gov/sites/default/files/omb/
assets/inforeg/technical-update-social-cost-ofcarbon-for-regulator-impact-analysis.pdf).
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values have been used in a number of
Federal rulemakings in which the
public had opportunity to comment. In
November 2013, the OMB announced a
new opportunity for public comment on
the TSD underlying the revised SCC
estimates. See 78 FR 70586 (Nov. 26,
2013). OMB is currently reviewing
comments and considering whether
further revisions to the 2013 SCC
estimates are warranted. DOE stands
ready to work with OMB and the other
members of the interagency working
group on further review and revision of
the SCC estimates as appropriate.
NAM stated that in using the SCC
estimates, DOE fails to adhere to its own
guidelines for ensuring and maximizing
the quality, objectivity, utility, and
integrity of information disseminated by
the DOE. (NAM, No. 84 at pp. 1–2) DOE
has sought to ensure that the data and
research used to support its policy
decisions—including the SCC values—
are of high scientific and technical
quality and objectivity, as called for by
the Secretarial Policy Statement on
Scientific Integrity.57 See section VI.J for
DOE’s evaluation of today’s final rule
and supporting analyses under the DOE
and OMB information quality
guidelines.
Rheem stated that the modeling
systems used for the SCC estimates and
the subsequent analyses were not
subject to peer review as appropriate.
(Rheem, No. 83 at p. 9) The Cato
Institute stated that the determination of
the SCC is discordant with the best
scientific literature on the equilibrium
climate sensitivity and the fertilization
effect of carbon dioxide—two critically
important parameters for establishing
the net externality of carbon dioxide
emissions. (Cato Institute, No. 81 at p.
2)
The three integrated assessment
models used to estimate the SCC are
frequently cited in the peer-reviewed
literature and were used in the last
assessment of the IPCC. In addition,
new versions of the models that were
used in 2013 to estimate revised SCC
values were published in the peerreviewed literature (see appendix 14B of
the final rule TSD). The revised
estimates that were issued in November
2013 are based on the best available
scientific information on the impacts of
climate change. The issue of
equilibrium climate sensitivity is
addressed in section 14A.4 of appendix
14A in the final rule TSD. The EPA, in
collaboration with other Federal
agencies, continues to investigate
potential improvements to the way in
57 See https://www.directives.doe.gov/directivesdocuments/0411.2-APolicy.
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which economic damages associated
with changes in CO2 emissions are
quantified.
Morrison stated that the CO2
emissions reductions benefits are
overestimated, because the SCC values
do not account for any prior changes
that impact the baseline emissions
trends in previous years. According to
the commenter, DOE fails to take into
consideration EPA regulations of
greenhouse gas emissions from power
plants, which would affect the SCC
values. (Morrison, No. 108 at p. 10)
The SCC values are based on
projections of global GHG emissions
over many decades. Such projections
are influenced by many factors,
particularly economic growth rates and
prices of different energy sources. In the
context of these projections, the
proposed EPA regulations of greenhouse
gas emissions from new power plants
are a minor factor. In any case, it would
not be appropriate for DOE to account
for regulations that are not currently in
effect, because whether such regulations
will be adopted and their final form are
matters of speculation at this time.
Miller stated that the Department
appears to violate the directive in OMB
Circular A–4, which states: ‘‘The
analysis should focus on benefits and
costs that accrue to citizens and
residents of the United States. Where
the agency chooses to evaluate a
regulation that is likely to have effects
beyond the borders of the United States,
these effects should be reported
separately.’’ Miller stated that instead of
focusing on domestic benefits and
separately reporting any international
effects, the Department focused on
much-larger global benefits in the text of
the proposed rule and separately
reported the (much smaller) domestic
effects in a chapter of the TSD. (Miller,
No. 79 at pp. 6–7) Similarly, Rheem
stated that by presenting only global
SCC estimates and downplaying
domestic SCC estimates in 2013, the
IWG has severely limited the utility of
the SCC for use in benefit-cost analysis
and policymaking. (Rheem, No. 83 at
p. 9) Mercatus stated that OMB
guidelines specifically require that
benefit-cost analysis of Federal
regulations be reported for domestic
estimates, with global estimates being
optional. Mercatus argued that by using
the global estimate at a three-percent
discount rate, DOE inflated the benefits
of reducing carbon emissions by almost
double compared to using a domestic
SCC at five percent. (Mercatus, No. 82
at pp. 7–8) EEI stated that the use of
global SCC values, which are estimates
that are based on many global
assumptions and are subject to a great
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deal of uncertainty, may be important in
assessing the overall costs and benefits
of particular regulations, but using these
values in the context of setting energy
conservation standards is problematic,
as the geographic and temporal scales of
the LCC and SCC values are very
different. (EEI, No. 87 at p. 10–11)
Although the relevant analyses
address both domestic and global
impacts, the interagency group has
determined that it is appropriate to
focus on a global measure of SCC
because of the distinctive nature of the
climate change problem, which is
highly unusual in at least two respects.
First, it involves a global externality:
Emissions of most greenhouse gases
contribute to damages around the world
when they are emitted in the United
States. Second, climate change presents
a problem that the United States alone
cannot solve. The issue of global versus
domestic measures of the SCC is further
discussed in appendix 14A of the final
rule TSD.
NAM stated that under DOE’s
analysis, the cost-benefit results and the
proposed rule are legally sufficient
without the inclusion of the SCC
estimate. (NAM, No. 84 at p. 3) In
contrast, JCI stated that the monetary
value of the CO2 emissions reduction
plays a significant role in DOE’s
justification to set the TSL 4 levels as
the national standards. (JCI, No. 95 at
p. 10)
DOE disagrees with NAM’s
assessment, which suggests that
consideration of the SCC in the context
of this rulemaking is somehow
unnecessary or unimportant. When
selecting a proposed standard level or
adopting a final standard level, DOE
considers and carefully weighs all
relevant factors. Thus, the monetary
value of the CO2 emissions reduction
did play a role in DOE’s decision to
propose TSL 4 (and to adopt TSL 4 in
today’s notice), as appropriate. DOE has
determined that today’s standards are
expected to achieve the maximum
improvement in energy efficiency that is
technologically feasible and
economically justified, with or without
consideration of the economic benefits
associated with reduced CO2 emissions.
Morrison stated that DOE does not
conduct the cost-benefit analysis for
NPV and SCC values over the same time
frame and within the same scope, an
important principle of cost-benefit
analysis. (Morrison, No. 108 at p. 9)
For the analysis of national impacts of
standards, DOE considers the lifetime
impacts of equipment shipped in a 30year period. With respect to energy and
energy cost savings, impacts continue
past 30 years until all of the equipment
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shipped in the 30-year period is retired.
With respect to the valuation of CO2
emissions reductions, the SCC estimates
developed by the interagency working
group are meant to represent the full
discounted value (using an appropriate
range of discount rates) of emissions
reductions occurring in a given year.
DOE is thus comparing the costs of
achieving the emissions reductions in
each year of the analysis, with the
carbon reduction value of the emissions
reductions in those same years. Neither
the costs nor the benefits of emissions
reductions outside the analytic time
frame are included in the analysis.
M. Utility Impact Analysis
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The utility impact analysis estimates
several effects on the power generation
industry that would result from the
adoption of new or amended energy
conservation standards. In the utility
impact analysis, DOE analyzes the
changes in electric installed capacity
and generation that result for each trial
standard level. The utility impact
analysis uses a variant of NEMS, which
is a public domain, multi-sectored,
partial equilibrium model of the U.S.
energy sector. DOE uses a variant of this
model, referred to as NEMS–BT,58 to
account for selected utility impacts of
new or amended energy conservation
standards. DOE’s analysis consists of a
comparison between model results for
the most recent AEO Reference Case and
for cases in which energy use is
decremented to reflect the impact of
potential standards. The energy savings
inputs associated with each TSL come
from the NIA. Chapter 15 of the final
rule TSD describes the utility impact
analysis in further detail.
EEI stated that it is not possible under
most operational scenarios to increase
electric capacity and decrease the
amount of electric generation, as is
indicated by DOE’s analysis. (EEI, No.
87 at p. 8) In response, it would appear
that the commenter has misinterpreted
Table 15.3.1 in the NOPR TSD. The
figure shows the capacity reduction as
a positive value; it is not an increase as
it might appear at first glance.
EEI stated that it is ironic that DOE is
showing that an estimated reduction of
renewable power plants provides an
economic benefit to the United States.
(EEI, No. 87 at p. 9) DOE reports the
58 DOE/EIA approves use of the name NEMS to
describe only an official version of the model
without any modification to code or data. Because
this analysis entails some minor code modifications
and the model is run under various policy scenarios
that are variations on DOE/EIA assumptions, DOE
refers to it by the name ‘‘NEMS–BT’’ (‘‘BT’’ is DOE’s
Building Technologies Program, under whose aegis
this work has been performed).
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projected changes in the installed
capacity of different types of power
plants resulting from potential
standards. Since the change in demand
occurs at the margin, it is not surprising
that plant types with relatively high first
cost (such as solar and wind power)
would be affected by standards. When
assessing the energy savings associated
with energy conservation standards,
DOE does not claim that any particular
changes in installed capacity of different
types of power plants provide an
economic benefit to the Nation relative
to other types of power plant facilities.
EEI stated that the analysis appears to
ignore the impacts of renewable
portfolio standards in 29 States and the
District of Columbia (as well as the
renewable power goals in 8 other
States). (EEI, No. 87 at p. 9) DOE
disagrees with EEI’s assertion regarding
DOE’s consideration of renewable
portfolio standards. In the utility impact
analysis, DOE used the projections of
electricity generation by plant type in
AEO 2013. These projections account
for the estimated impacts of all
renewable portfolio standards that were
in place at the end of 2012.
Several stakeholders stated that DOE
did not adequately consider power
quality issues, specifically that DOE did
not account for the effect of such a large
number of non-linear power supplies
(constant-torque BPM motors and multistaging controls) without power factor
correction on the grid. Several of them
stated that the non-linear loads
produced by constant-torque and
constant-airflow BPM motors tend to
cause harmonic distortions in both
voltage and current, and could
potentially cause voltage control
problems within a power grid system.
(JCI, No. 95 at p. 9; Morrison, No. 108
at p. 7; AHRI, No. 98 at p. 11) JCI stated
that the Electric Power Research
Institute suggests that while harmonic
emissions from a single system may not
have a major impact on the grid, the
cumulative impact of millions of
furnaces could be significant on the grid
systems within the U.S. (JCI, No. 95 at
p. 9) Southern Company stated that the
BPM motors considered in this
rulemaking typically have poor power
factors and emit strong 3rd and 5th
order harmonics, which is likely to
cause problems with utility systems at
a future date when most of the older
equipment has been retired and
replaced by BPM motors. (Southern
Company, No. 85 at p. 4) JCI, Morrison,
and AHRI stated that the mitigation
costs associated with harmonic
distortions would have a significant
impact on consumers, especially related
to failure rates, maintenance and repair
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38181
costs, and the overall economic analysis
for life-cycle costs. (JCI, No. 95 at p. 9;
Morrison, No. 108 at p. 7; AHRI, No. 98
at p. 11) Southern Company stated that,
for furnace fans with BPM motors, DOE
could assume a percentage of
households would require wiring
upgrades and some additional costs to
either the utility or the homeowner for
filtering of harmonics or power factor
correction. (Southern Company, No. 85
at p. 4) APGA stated that DOE should
include the cost of installation of
harmonic filters in the LCC analysis and
recalculate the economic justification of
design options incorporating ECM
motors. (APGA, No. 110 at p. 3)
Regarding these comments, DOE notes
that a number of studies assume that
output from BPM motors is constant at
full load at time of use, similar to
operation of PSC motors. However, BPM
motors are specifically designed to
accommodate reduced-load operation,
and, therefore, most of the time, they
will operate at part load (i.e., at lower
speeds and higher efficiency). The
current of a BPM motor at lower-speed
operation is significantly lower than a
PSC motor at normal operation;
therefore, total current contribution will
not exceed the existing system grid
capacity. In addition, the harmonic
contribution is a small part of total
circuit loading, at the lower current
levels. For example, motor performance
data from GE 59 shows an increase in
power of 133 volt-amperes (VA) from a
1⁄3 HP PSC to BPM at full output. On
average, 5 to 20 residential customers
are served per distribution transformer,
which are normally rated between 15
and 50 kVA.60 61 An increase of this
current would result in an increase in
loading less than 3 percent at the
extreme case. (The extreme case is all
HVAC at full load concurrently, served
by the same distribution transformer.)
The transformers are normally rated
approximately 30 percent to 50 percent
above predicted peak load.62 In this
case, the increased current draw (VA)
would have negligible impact. Measured
59 GE Industrial Systems, GE ECM 2.3 Series
motors datasheet (Available at: https://
www.columbiaheating.com/page_images/file/GET8068.pdf).
60 Farmer, C., Hines, P., Dowds, J., Blumsack, S.,
Modeling the Impact of Increasing PHEV Loads on
the Distribution Infrastructure, Proceedings of the
43rd International Conference on System Sciences
(2010).
61 NEMA. NEMA TP 1–2002: Guide for
Determining Energy Efficiency for Distribution
Transformers.
62 NEMA Standards Publication TP 1–2002:
Guide for Determining Energy Efficiency for
Distribution Transformers (Available at: https://
www.nema.org/Standards/Pages/Guide-forDetermining-Energy-Efficiency-for-DistributionTransformers.aspx?#download).
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performance data 63 show a decrease in
current drawn for cooling functionality
(152 VA) and an increase for heating
functionality (32 VA) from PSC to
equivalent BPM, confirming the small
BPM loading impact. In addition, an
evaluation of increased penetration of
BPM motors in commercial buildings
was presented at the ASHRAE 6 ECM
Motor Workshop at the CEC, which
reviewed California Utility Codes with
regards to the BPM-specific issue.64 It
was stated in this study that while the
power factor could be reduced to 50
percent, a BPM motor will have a lower
current draw than a PSC motor at 100
percent power factor due to efficiency
gains.
Regarding the EPRI study 65
referenced in the JCI comment, DOE
noticed that the power factor impacts
are associated with several types of
loads becoming common in the modern
household: Low power factor lighting,
modern entertainment systems, and
electric vehicle chargers, as well as
HVAC with BPM motors. This reference
indicates that the power quality issues
caused by the BPM motors are a small
contributor to the total harmonic
distortion experienced at the utility
level compared to all contributing loads.
The study indicated that for devices
with an existing 3rd harmonic
resonance, the contribution of all new
devices would require filtering;
however, this correction is not
attributed to the high penetration of EC
motors alone. The BPM’s third
harmonic distortion contributed a 1.5percent current increase to the circuit.
The study showed the overall impact on
the 3rd, 5th, 7th order and included in
total harmonic distortion (THD) was
within 0.1 percent of the original
harmonic profile applied to the studied
feeder. In summary, the impact of
introducing BPM motors for HVAC
under a high penetration scenario on a
residential line was negligible.
63 Gusdorf, J., M. Swinton, C. Simpson, E. Enchev,
S. Hayden, D. Furdas, and B. Castellan, Saving
Electricity and Reducing GHG Emissions with ECM
Furnace Motors: Results from the CCHT and
Projections to Various Houses and Locations (2004)
ACEEE Proceedings (Available at: https://aceee.org/
files/proceedings/2004/data/papers/SS04_Panel1_
Paper12.pdf).
64 Taylor Engineering LLC, ASHRAE 6 ECM
Motors, August 17th CEC Workshop (2011)
California Statewide Utility Code and Standard
Program (Available at: https://www.energy.ca.gov/
title24/2013standards/prerulemaking/documents/
2011-08-17_workshop/presentations/
08%20EC%20Motors.pdf).
65 Sharma, H. M. Rylander, and D. Dorr, Grid
Impacts due to Increased Penetration of Newer
Harmonic Sources, Proceedings of IEEE Rural
Electric Power Conference (April 2013) pp. B5–1—
B5–5 (Available at: https://ieeexplore.ieee.org/
stamp/stamp.jsp?tp=&arnumber=6681854).
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With regards to household power
quality, furnaces have a minimum basic
electrical requirement for THD of 5
percent, and individual harmonic
distortion of 3 percent.66 67 Furnaces
supplied with voltages with harmonic
distortion greater than 8 percent THD
may not be operated.68 The EPRI study,
which simulates a harmonic spectrum
of a large number of BPM-based HVAC,
shows that the BPM-related harmonic
distortions are within the 5 percent THD
limit, and within the 3 percent
individual harmonic limit. Therefore,
DOE concludes the BPM-related
harmonic distortions would not cause
the problems cited by the commenters.
In addition to the analysis described
above, DOE used NEMS–BT, along with
EIA data on the capital cost of various
power plant types, to estimate the
reduction in national expenditures for
electricity generating capacity due to
potential residential furnace fan
standards. The method used and the
results are described in chapter 15 of the
final rule TSD.
N. Employment Impact Analysis
Employment impacts from new or
amended energy conservation standards
include direct and indirect impacts.
Direct employment impacts are any
changes in the number of employees of
manufacturers of the products subject to
standards; the MIA addresses those
impacts. Indirect employment impacts
are changes in national employment
that occur due to the shift in
expenditures and capital investment
caused by the purchase and operation of
more-efficient appliances. Indirect
employment impacts from standards
consist of the jobs created or eliminated
in the national economy due to: (1)
Reduced spending by end users on
energy; (2) reduced spending on new
energy supply by the utility industry; (3)
increased consumer spending on the
purchase of new products; and (4) the
effects of those three factors throughout
the economy.
One method for assessing the possible
effects on the demand for labor of such
shifts in economic activity is to compare
sector employment statistics developed
by the Labor Department’s Bureau of
Labor Statistics (BLS). BLS regularly
publishes its estimates of the number of
66 IEEE Standard 519–1992—IEEE Recommended
Practices and Requirements for Harmonic Control
in Electric Power Systems (April 9 1993) pp. 1–112
(Available at: https://ieeexplore.ieee.org/stamp/
stamp.jsp?tp=&arnumber=210894).
67 Fluke Corporation, Generator power quality
and furnaces: The effects of harmonic distortion
(2009) (Available at: https://support.fluke.com/findsales/Download/Asset/3497420_6112_ENG_A_
W.PDF).
68 Id.
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jobs per million dollars of economic
activity in different sectors of the
economy, as well as the jobs created
elsewhere in the economy by this same
economic activity. Data from BLS
indicate that expenditures in the utility
sector generally create fewer jobs (both
directly and indirectly) than
expenditures in other sectors of the
economy.69 There are many reasons for
these differences, including wage
differences and the fact that the utility
sector is more capital-intensive and less
labor-intensive than other sectors.
Energy conservation standards have the
effect of reducing consumer utility bills.
Because reduced consumer
expenditures for energy likely lead to
increased expenditures in other sectors
of the economy, the general effect of
efficiency standards is to shift economic
activity from a less labor-intensive
sector (i.e., the utility sector) to more
labor-intensive sectors (e.g., the retail
and service sectors). Thus, based on the
BLS data alone, DOE believes net
national employment may increase
because of shifts in economic activity
resulting from energy conservation
standards for residential furnace fans.
For the standard levels considered in
today’s document, DOE estimated
indirect national employment impacts
using an input/output model of the U.S.
economy called Impact of Sector Energy
Technologies version 3.1.1 (ImSET).70
ImSET is a special-purpose version of
the ‘‘U.S. Benchmark National InputOutput’’ (I–O) model, which was
designed to estimate the national
employment and income effects of
energy-saving technologies. The ImSET
software includes a computer-based I–O
model having structural coefficients that
characterize economic flows among the
187 sectors. ImSET’s national economic
I–O structure is based on a 2002 U.S.
benchmark table, specially aggregated to
the 187 sectors most relevant to
industrial, commercial, and residential
building energy use. DOE notes that
ImSET is not a general equilibrium
forecasting model, and understands the
uncertainties involved in projecting
employment impacts, especially
changes in the later years of the
analysis. Because ImSET does not
incorporate price changes, the
employment effects predicted by ImSET
69 See Bureau of Economic Analysis, ‘‘Regional
Multipliers: A User Handbook for the Regional
Input-Output Modeling System (RIMS II),’’ U.S.
Department of Commerce (1992).
70 J. M. Roop, M. J. Scott, and R. W. Schultz,
ImSET 3.1: Impact of Sector Energy Technologies,
PNNL–18412, Pacific Northwest National
Laboratory (2009) (Available at: www.pnl.gov/main/
publications/external/technical_reports/PNNL18412.pdf).
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may over-estimate actual job impacts
over the long run. For the final rule,
DOE used ImSET only to estimate shortterm (2019 and 2024) employment
impacts.
For more details on the employment
impact analysis, see chapter 16 of the
final rule TSD.
O. Comments on Proposed Standards
NEEP, CA IOUs, and the Joint
Advocates support the selection of
DOE’s proposed trial standard level,
given the limited impact on furnace fan
manufacturers, positive benefits to
consumers, and substantial energy
savings. (NEEP, No. 109 at p. 2; CA
IOUs, No. 106 at p. 2; Joint Advocates,
No. 105 at p. 1)
A number of stakeholders disagreed
with the proposed selection of TSL 4.
Rheem argued that TSL 4 is not
economically justified. (Rheem, No. 83
at p. 7) Lennox stated that because TSL
4 likely has costs that are understated,
and overly optimistic efficiency
projections, DOE should not pursue TSL
4, and instead adopt standards based on
a less-stringent, less-costly technology.
(Lennox, No. 100 at p. 2) EEI suggested
the adoption of TSL 1 or TSL 2 to
conserve energy, minimize economic
harm to consumers, and minimize the
possible negative impacts on the electric
grid from the motors that would be able
to meet the proposed standard. (EEI, No.
87 at p. 2)
DOE has addressed specific issues
regarding costs, efficiency projections,
and possible negative impacts on the
electric grid in previous parts of section
IV of this document. DOE addresses the
economic justification for today’s
standards in section V.C of this
document.
Southern Company believes that
under TSL 4, too large a proportion of
consumers have net costs. Southern
Company would prefer that a
substantial majority of consumers derive
benefits from a proposed rule. (Southern
Company, No. 85 at p. 3) EEI also stated
that a much higher percentages of
consumers will experience a net cost
than is the case with many other DOE
energy conservation standards. (EEI, No.
87 at p. 2) The Mercatus Center stated
that the proposed rule will confer net
benefits on a majority of the consumers
for only one product class (i.e., nonweatherized, non-condensing gas
furnace fans). It added that the aggregate
financial benefits to consumers are not
spread uniformly over the population,
but instead are mostly concentrated in
a minority of households. (Mercatus
Center, No. 82 at p. 7)
As shown in Table V.31 of today’s
final rule, more consumers would have
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a net benefit from standards at TSL 4
than would have a net cost for all of the
considered product classes. For the two
largest product classes (non-weatherized
non-condensing gas furnace fans and
non-weatherized condensing gas
furnace fans), nearly twice as many
consumers would have a net benefit
from standards at TSL 4 as would have
a net cost.
The Mercatus Center stated that seven
out of eight proposed standards at TSL
4 fail the rebuttable payback period
benchmark, thereby making it difficult
for DOE to demonstrate economic
justification for the proposed rule.
(Mercatus Center, No. 82 at p. 6) In
response, the commenter has
misinterpreted the role of the rebuttable
payback period presumption. As
discussed in section III.E.2, EPCA
provides that a rebuttable presumption
is established that an energy
conservation standard is economically
justified if the additional cost to the
consumer of a product that meets the
standard is less than three times the
value of the first year’s energy savings
resulting from the standard, as
calculated under the applicable DOE
test procedure. (42 U.S.C.
6295(o)(2)(B)(iii)) To determine
economic justification, DOE routinely
conducts an analysis that considers the
full range of impacts, including those to
consumers, manufacturers, the Nation,
and the environment, as required under
42 U.S.C. 6295(o)(2)(B)(i). The results of
this analysis serve as the basis for DOE
to definitively evaluate the economic
justification for a potential standard
level, thereby supporting or rebutting
the results of any preliminary
determination of economic justification.
Rheem and Miller stated that the
proposed standard may act as a transfer
payment from lower-income
households, who are more likely to bear
net costs as a result of this rule, to
higher-income households; and that
higher-priced furnace fans resulting
from this rule will be out of reach for
some consumers. They stated that these
distributive impacts necessitate close
scrutiny from the Department in order
to determine whether the proposed
standards will actually improve social
welfare. (Rheem, No. 83 at p. 14; Miller,
No. 79 at p. 14)
DOE’s consumer subgroup analysis
indicates that, for non-weatherized gas
furnace fans, lower-income households
would have positive average LCC
savings and median PBPs less than five
years (see section V.B.1). Furthermore,
many lower-income households rent
rather than own their dwelling, and are
responsible for utility bills but not for
purchase of a furnace. To the extent that
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38183
there is delay in the landlords’ passing
of extra costs into the rent, consumers
that rent will benefit more those who
own, all else being equal.
Ingersoll Rand stated that
promulgating a rule at TSL4 would force
the future generation of furnaces sold in
the U.S. to be less reliable than many of
those on the market today as a result of
eliminating PSC motors from the
market. (Ingersoll Rand, No. 107 at p. 7)
DOE notes that furnace fans meeting
today’s standards are already widely
available as a substitute for units with
baseline motors. DOE evaluated issues
related to reliability, as discussed in
section IV.F.2, and concluded that the
benefits to consumers outweigh any
costs related to reliability that may be
associated with products meeting the
standards.
V. Analytical Results and Conclusions
This section addresses the results
from DOE’s analyses with respect to
potential energy conservation standards
for residential furnace fans. It addresses
the TSLs examined by DOE, the
projected impacts of each of these levels
if adopted as energy conservation
standards for furnace fans, and the
standard levels ultimately adopted by
DOE in today’s final rule. Additional
details regarding DOE’s analyses are
contained in the TSD supporting this
document.
A. Trial Standard Levels
DOE developed trial standard levels
(TSLs) that combine efficiency levels for
each product class of residential furnace
fans. Table V.1 presents the efficiency
levels for each product class in each
TSL. TSL 6 consists of the max-tech
efficiency levels. TSL 5 consists of those
efficiency levels that provide the
maximum NPV using a 7-percent
discount rate (see section V.B.3 for NPV
results). TSL 4 consists of those
efficiency levels that provide the highest
NPV using a 7-percent discount rate,
and that also result in a higher
percentage of consumers that receive an
LCC benefit than experience an LCC loss
(see section V.B.1 for LCC results). TSL
3 uses efficiency level 3 for all product
classes. TSL 2 consists of efficiency
levels that are the same as TSL 3 for
non-weatherized gas furnace fans,
weatherized gas furnace fans, and
electric furnace fans, but are at
efficiency level 1 for oil-fired furnace
fans and mobile home furnace fans. TSL
1 consists of the most common
efficiency levels in the current market.
In summary, Table V.1 presents the six
TSLs which DOE has identified for
residential furnace fans, including the
efficiency level associated with each
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TSL, the technology options anticipated
to achieve those levels, and the
expected resulting percentage reduction
in FER from the baseline corresponding
to each efficiency level.
TABLE V.1—TRIAL STANDARD LEVELS FOR RESIDENTIAL FURNACE FANS
Trial standard levels
(Efficiency level) *
Product class
1
Non-Weatherized, Non-Condensing Gas Furnace Fan ..........................
Non-Weatherized, Condensing Gas Furnace Fan ..................................
Weatherized Non-Condensing Gas Furnace Fan ...................................
Non-Weatherized, Non-Condensing Oil Furnace Fan .............................
Non-Weatherized Electric Furnace/Modular Blower Fan ........................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan ....
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ............
Mobile Home Electric Furnace/Modular Blower Fan ...............................
2
1
1
1
1
1
1
1
1
3
4
3
3
3
1
3
1
1
1
5
3
3
3
3
3
3
3
3
6
4
4
4
1
4
1
1
4
4
4
4
3
4
3
3
4
6
6
6
6
6
6
6
6
* Efficiency level (EL) 1 = Improved PSC (12 percent). (For each EL, the percentages given refer to percent reduction in FER from the baseline
level.) EL 2 = Inverter-driven PSC (25 percent). EL 3 = Constant-torque BPM motor (38 percent). EL 4 = Constant-torque BPM motor + MultiStaging (51 percent). EL 5 = Constant-airflow BPM motor (57 percent). EL 6 = Constant-airflow BPM motor + Multi-Staging (61 percent).
B. Economic Justification and Energy
Savings
1. Economic Impacts on Consumers
Life-Cycle Cost and Payback Period
To evaluate the economic impact of
the considered efficiency levels on
consumers, DOE conducted an LCC
analysis for each efficiency level. Moreefficient residential furnace fans would
affect these consumers in two ways: (1)
Annual operating expense would
decrease; and (2) purchase price would
increase. Inputs used for calculating the
LCC include total installed costs (i.e.,
equipment price plus installation costs),
operating expenses (i.e., energy costs,
repair costs, and maintenance costs),
product lifetime, and discount rates.
The output of the LCC model is a
mean LCC savings (or cost) for each
product class, relative to the base-case
efficiency distribution for residential
furnace fans. The LCC analysis also
provides information on the percentage
of consumers for whom an increase in
the minimum efficiency standard would
have a positive impact (net benefit), a
negative impact (net cost), or no impact.
DOE also performed a PBP analysis as
part of the LCC analysis. The PBP is the
number of years it would take for the
consumer to recover the increased costs
of higher-efficiency products as a result
of energy savings based on the operating
cost savings. The PBP is an economic
benefit-cost measure that uses benefits
and costs without discounting. Chapter
8 of the final rule TSD provides detailed
information on the LCC and PBP
analyses.
DOE’s LCC and PBP analyses provide
five key outputs for each efficiency level
above the baseline, as reported in Table
V.2 through Table V.9 for the
considered TSLs. (Results for all
efficiency levels are reported in chapter
8 of the final rule TSD.) These outputs
include the proportion of residential
furnace fan purchases in which the
purchase of a furnace fan compliant
with the new energy conservation
standard creates a net LCC increase, no
impact, or a net LCC savings for the
consumer. Another output is the average
LCC savings from standards-compliant
products, as well as the median PBP for
the consumer investment in standardscompliant products. Savings are
measured relative to the base-case
efficiency distribution (see section
IV.F.4), not the baseline efficiency level.
TABLE V.2—LCC AND PBP RESULTS FOR NON-WEATHERIZED, NON-CONDENSING GAS FURNACE FANS
Life-cycle cost
2013$
Efficiency level
TSL
Discounted
operating
cost
Installed
cost
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Baseline ...............................
1 ...........................................
2 ...........................................
3 ...........................................
4 ...........................................
5 ...........................................
6 ...........................................
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..............
1 ...........
..............
2, 3 .......
4, 5 .......
..............
6 ...........
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359
408
423
501
658
694
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1,933
1,655
1,367
1,249
1,244
1,150
Fmt 4701
Life-cycle cost savings
Average
savings
2013$
LCC
$2,541
2,292
2,063
1,791
1,750
1,902
1,844
Sfmt 4700
Percent of consumers that
experience
Net
cost
$0
85
263
471
506
373
431
E:\FR\FM\03JYR2.SGM
No
impact
0
1
25
17
30
47
50
03JYR2
100
68
25
25
14
12
0
Net
benefit
0
30
50
58
56
41
50
Median
payback
period
years
................
1.1
3.8
2.6
5.4
10.6
10.2
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Federal Register / Vol. 79, No. 128 / Thursday, July 3, 2014 / Rules and Regulations
TABLE V.3—LCC AND PBP RESULTS FOR NON-WEATHERIZED, CONDENSING GAS FURNACE FANS
Life-cycle cost
2013$
Efficiency level
TSL
Discounted
operating
cost
Installed
cost
Baseline ...............................
1 ...........................................
2 ...........................................
3 ...........................................
4 ...........................................
5 ...........................................
6 ...........................................
..............
1 ...........
..............
2, 3 .......
4, 5 .......
..............
6 ...........
$343
355
403
416
493
652
687
$2,134
1,909
1,666
1,402
1,319
1,334
1,250
Life-cycle cost savings
Average
savings
2013$
LCC
$2,478
2,264
2,070
1,818
1,812
1,987
1,937
Percent of consumers that
experience
Net
cost
$0
58
182
335
341
219
268
No
impact
0
1
21
11
23
42
51
Net
benefit
100
75
41
41
34
29
0
0
24
38
48
43
30
49
Median
payback
period
years
................
1.2
4.2
2.9
5.8
12.0
11.0
TABLE V.4—LCC AND PBP RESULTS FOR WEATHERIZED, NON-CONDENSING GAS FURNACE FANS
Life-cycle cost
2013$
Efficiency level
TSL
Discounted
operating
cost
Installed
cost
Baseline ...............................
1 ...........................................
2 ...........................................
3 ...........................................
4 ...........................................
5 ...........................................
6 ...........................................
..............
1 ...........
..............
2, 3 .......
4, 5 .......
..............
6 ...........
$333
345
393
406
481
633
668
$2,667
2,329
2,025
1,609
1,434
1,476
1,354
Life-cycle cost savings
Average
savings
2013$
LCC
$3,000
2,674
2,418
2,015
1,914
2,109
2,022
Percent of consumers that
experience
Net
cost
$0
67
189
378
447
304
391
No
Impact
0
0
8
3
16
38
41
Net
benefit
100
81
56
56
33
27
0
0
19
36
41
51
35
59
Median
payback
period
years
................
0.7
3.2
1.8
4.4
10.3
8.2
TABLE V.5—LCC AND PBP RESULTS FOR NON-WEATHERIZED, NON-CONDENSING OIL FURNACE FANS
Life-cycle cost
2013$
Efficiency level
TSL
Discounted
operating
cost
Installed
cost
Baseline ...............................
1 ...........................................
2 ...........................................
3 ...........................................
4 ...........................................
5 ...........................................
6 ...........................................
..............
1, 2, 4 ...
..............
3, 5 .......
..............
..............
6 ...........
$417
427
501
507
589
813
863
$2,510
2,356
2,090
1,979
1,920
1,922
1,873
Life-cycle cost savings
Average
savings
2013$
LCC
$2,927
2,783
2,592
2,486
2,509
2,736
2,736
Percent of consumers that
experience
Net
cost
$0
46
181
259
244
80
80
No
impact
0
13
46
44
48
56
78
Net
benefit
100
71
28
28
28
28
0
0
17
26
28
24
16
22
Median
payback
period
years
................
1.7
10.3
4.6
8.1
18.3
18.6
TABLE V.6—LCC AND PBP RESULTS FOR NON-WEATHERIZED ELECTRIC FURNACE/MODULAR BLOWER FANS
Life-cycle cost
2013$
Efficiency level
TSL
Discounted
operating
cost
mstockstill on DSK4VPTVN1PROD with RULES2
Installed
cost
Baseline ...............................
1 ...........................................
2 ...........................................
3 ...........................................
4 ...........................................
5 ...........................................
6 ...........................................
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1 ...........
..............
2, 3 .......
4, 5 .......
..............
6 ...........
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255
299
292
309
444
477
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1,079
941
797
747
796
748
Fmt 4701
Life-cycle cost savings
Average
savings
2013$
LCC
$1,455
1,335
1,241
1,089
1,055
1,240
1,225
Sfmt 4700
Percent of consumers that
experience
Net
cost
$0
29
88
181
204
66
81
E:\FR\FM\03JYR2.SGM
No
impact
0
4
27
17
23
48
60
03JYR2
100
73
37
37
25
25
0
Net
benefit
0
22
36
45
51
27
39
Median
payback
period
years
................
1.9
6.2
2.6
3.2
12.0
11.5
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TABLE V.7—LCC AND PBP RESULTS FOR MOBILE HOME NON-WEATHERIZED, NON-CONDENSING GAS FURNACE FANS
Life-cycle cost
2013$
Efficiency level
TSL
Discounted
operating
cost
Installed
cost
Baseline ...............................
1 ...........................................
2 ...........................................
3 ...........................................
4 ...........................................
5 ...........................................
6 ...........................................
..............
1, 2, 4 ...
..............
3, 5 .......
..............
..............
6 ...........
$256
268
313
318
390
530
563
$1,118
1,026
930
867
831
853
824
Life-cycle cost savings
Average
savings
2013$
LCC
$1,374
1,293
1,243
1,185
1,222
1,383
1,388
Percent of consumers that
experience
Net
cost
$0
36
87
144
108
(54)
(58)
No
impact
0
10
62
55
67
81
80
Net
benefit
100
56
0
0
0
0
0
0
34
38
45
33
19
20
Median
payback
period
years
................
2.7
10.2
6.8
12.7
24.3
24.4
* Parentheses indicate negative values.
TABLE V.8—LCC AND PBP RESULTS FOR MOBILE HOME NON-WEATHERIZED, CONDENSING GAS FURNACE FANS
Life-cycle cost
2013$
Efficiency level
TSL
Discounted
operating
cost
Installed
cost
Baseline ...............................
1 ...........................................
2 ...........................................
3 ...........................................
4 ...........................................
5 ...........................................
6 ...........................................
..............
1, 2, 4 ...
..............
3, 5 .......
..............
..............
6 ...........
$274
285
330
339
411
558
591
$1,283
1,170
1,061
977
936
953
917
Life-cycle cost savings
Average
savings
2013$
LCC
$1,556
1,454
1,391
1,316
1,347
1,510
1,508
Percent of consumers that
experience
Net
cost
$0
35
79
133
103
(53)
(51)
No
impact
0
5
43
37
66
80
82
Net
benefit
100
68
29
29
4
4
0
0
27
28
33
29
16
18
Median
payback
period
years
................
2.3
9.7
6.6
15.8
33.3
31.3
* Parentheses indicate negative values.
TABLE V.9—LCC AND PBP RESULTS FOR MOBILE HOME ELECTRIC FURNACE/MODULAR BLOWER FAN
Life-cycle cost
2013$
Efficiency level
TSL
Discounted
operating
cost
Installed
cost
Baseline ...............................
1 ...........................................
2 ...........................................
3 ...........................................
4 ...........................................
5 ...........................................
6 ...........................................
..............
1, 2 .......
..............
3 ...........
4, 5 .......
..............
6 ...........
$194
204
245
237
251
375
406
$643
575
531
466
433
487
462
Life-cycle cost savings
Average
savings
2013$
LCC
$837
778
777
702
685
862
868
Percent of consumers that
experience
Net
cost
$0
19
20
70
85
(48)
(54)
No
impact
0
7
36
26
32
57
75
100
71
38
38
26
26
0
Net
benefit
0
22
26
37
43
18
25
Median
payback
period
years
................
2.1
8.9
3.6
4.1
15.0
14.9
* Parentheses indicate negative values.
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Consumer Subgroup Analysis
DOE estimated the impacts of the
considered efficiency levels (TSLs) on
the following consumer subgroups: (1)
Senior-only households; and (2) lowincome households. The results of the
consumer subgroup analysis indicate
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that for residential furnace fans, senioronly households and low-income
households experience lower average
LCC savings and longer payback periods
than consumers overall, with the
difference being larger for low-income
households. The difference between the
two subgroups and all consumers is
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larger for non-weatherized, noncondensing gas furnace fans (see Table
V.10) than for non-weatherized,
condensing gas furnace fans (see Table
V.11). Chapter 11 of the final rule TSD
provides more detailed discussion on
the consumer subgroup analysis and
results for the other product classes.
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TABLE V.10—COMPARISON OF IMPACTS FOR CONSUMER SUBGROUPS WITH ALL CONSUMERS, NON-WEATHERIZED, NONCONDENSING GAS FURNACE FANS
Average life-cycle cost savings
(2013$)
Median payback period
(years)
Efficiency level
Senior-only
TSL
1
2
3
4
5
6
.................................................................
.................................................................
.................................................................
.................................................................
.................................................................
.................................................................
Low-income
All
consumers
Senior-only
Low-income
All
consumers
$65
209
366
373
226
264
$48
133
251
234
77
96
$85
263
471
506
373
431
1.6
5.2
3.7
7.6
14.5
13.7
1.7
6.3
3.6
7.8
15.9
15.3
1.1
3.8
2.6
5.4
10.6
10.2
1 ...............
..................
2, 3 ..........
4, 5 ..........
..................
6 ...............
TABLE V.11—COMPARISON OF IMPACTS FOR CONSUMER SUBGROUPS WITH ALL CONSUMERS, NON-WEATHERIZED,
CONDENSING GAS FURNACE FANS
Average life-cycle cost savings
(2013$)
Median payback period
(years)
Efficiency level
Senior-only
TSL
1
2
3
4
5
6
.................................................................
.................................................................
.................................................................
.................................................................
.................................................................
.................................................................
Low-income
All
consumers
Senior-only
Low-income
All
consumers
$49
155
288
275
141
178
$38
121
230
202
66
90
$58
182
335
341
219
268
1.5
5.5
3.7
7.5
15.4
12.2
2.0
7.1
4.4
9.7
19.5
17.0
1.2
4.2
2.9
5.8
12.0
11.0
1 ...............
..................
2, 3 ..........
4, 5 ..........
..................
6 ...............
Rebuttable Presumption Payback
As discussed in section III.E.2, EPCA
provides a rebuttable presumption that,
in essence, an energy conservation
standard is economically justified if the
increased purchase cost for a product
that meets the standard is less than
three times the value of the first-year
energy savings resulting from the
standard. However, DOE routinely
conducts a full economic analysis that
considers the full range of impacts,
including those to the consumer,
manufacturer, Nation, and environment,
as required under 42 U.S.C.
6295(o)(2)(B)(i). The results of this
analysis serve as the basis for DOE to
definitively evaluate the economic
justification for a potential standard
level, thereby supporting or rebutting
the results of any preliminary
determination of economic justification.
For comparison with the more detailed
analytical results, DOE calculated a
rebuttable presumption payback period
for each TSL. Table V.12 shows the
rebuttable presumption payback results
to determine whether any of them meet
the rebuttable presumption conditions
for the residential furnace fans product
classes.
TABLE V.12—REBUTTABLE PRESUMPTION PAYBACK PERIODS FOR RESIDENTIAL FURNACE FAN PRODUCT CLASSES
Rebuttable presumption payback
(years)
Product class
TSL 1
Non-Weatherized, Non-Condensing Gas Furnace Fan ..........................
Non-Weatherized, Condensing Gas Furnace Fan ..................................
Weatherized Non-Condensing Gas Furnace Fan ...................................
Non-Weatherized, Non-Condensing Oil Furnace Fan .............................
Non-Weatherized Electric Furnace/Modular Blower Fan ........................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan ....
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ............
Mobile Home Electric Furnace/Modular Blower Fan ...............................
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2. Economic Impact on Manufacturers
As noted above, DOE performed an
MIA to estimate the impact of new
energy conservation standards on
manufacturers of residential furnace
fans. The following section describes
the expected impacts on manufacturers
at each considered TSL. Chapter 12 of
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TSL 2
3.3
3.1
3.0
2.3
3.2
3.8
3.5
4.3
5.3
4.9
4.8
2.3
5.1
3.8
3.5
4.3
the final rule TSD explains the analysis
in further detail.
Industry Cash-Flow Analysis Results
Table V.13 and Table V.14 depict the
financial impacts (represented by
changes in INPV) of new energy
standards on manufacturers of
residential furnace fans, as well as the
conversion costs that DOE expects
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TSL 3
5.3
4.9
4.8
5.9
5.1
6.1
5.7
6.8
TSL 4
10.3
9.6
9.4
2.3
5.8
3.8
3.5
7.7
TSL 5
10.3
9.6
9.4
5.9
5.8
6.1
5.7
7.7
TSL 6
19.4
18.2
17.6
19.8
15.4
22.1
20.9
20.2
manufacturers would incur for all
product classes at each TSL. To evaluate
the range of cash flow impacts on the
residential furnace fans industry, DOE
modeled two different mark-up
scenarios using different assumptions
that correspond to the range of
anticipated market responses to
potential new energy conservation
standards: (1) The preservation of gross
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margin percentage; and (2) the
preservation of per-unit operating profit.
Each of these scenarios is discussed
immediately below.
To assess the lower (less severe) end
of the range of potential impacts, DOE
modeled a preservation of gross margin
percentage markup scenario, in which a
uniform ‘‘gross margin percentage’’
markup is applied across all potential
efficiency levels. In this scenario, DOE
assumed that a manufacturer’s absolute
dollar markup would increase as
production costs increase in the
standards case.
To assess the higher (more severe) end
of the range of potential impacts, DOE
modeled the preservation of per-unit
operating profit markup scenario, which
assumes that manufacturers would be
able to earn the same operating margin
in absolute dollars per-unit in the
standards case as in the base case. In
this scenario, while manufacturers make
the necessary investments required to
convert their facilities to produce new
standards-compliant products, operating
profit does not change in absolute
dollars per unit and decreases as a
percentage of revenue.
The set of results below shows
potential INPV impacts for residential
furnace fan manufacturers; Table V.13
reflects the lower bound of impacts, and
Table V.14 represents the upper bound.
Each of the modeled scenarios results
in a unique set of cash flows and
corresponding industry values at each
TSL. In the following discussion, the
INPV results refer to the difference in
industry value between the base case
and each standards case that results
from the sum of discounted cash flows
from the base year 2014 through 2048,
the end of the analysis period. To
provide perspective on the short-run
cash flow impact, DOE includes in the
discussion of the results below a
comparison of free cash flow between
the base case and the standards case at
each TSL in the year before new
standards would take effect. This figure
provides an understanding of the
magnitude of the required conversion
costs relative to the cash flow generated
by the industry in the base case.
TABLE V.13—MANUFACTURER IMPACT ANALYSIS FOR RESIDENTIAL FURNACE FANS—PRESERVATION OF GROSS MARGIN
PERCENTAGE MARKUP SCENARIO *
Base
case
Units
INPV ..................................................................
Change in INPV .................................................
Product Conversion Costs .................................
Capital Conversion Costs ..................................
Total Conversion Costs .....................................
Free Cash Flow (2018) .....................................
Free Cash Flow (change from Base Case)
(2018).
$M ........
$M ........
(%) .......
$M ........
$M ........
$M ........
$M ........
% ..........
349.6
................
................
2.2
................
2.2
20.3
0.0
Trial standard level
1
2
3
4
5
336.6
(13.0)
(3.7)
18.8
8.8
27.7
11.3
(44.5)
360.0
10.4
3.0
23.6
11.1
34.7
8.8
(56.7)
359.1
9.4
2.7
25.3
11.8
37.1
8.0
(60.8)
397.8
48.2
13.8
25.5
15.1
40.6
6.4
(68.3)
397.6
48.0
13.7
27.1
15.7
42.8
5.6
(72.2)
6
422.4
72.8
20.8
29.4
134.7
164.2
(48.6)
(339.8)
* Values in parentheses are negative values. All values have been rounded to the nearest tenth.
M = millions.
TABLE V.14—MANUFACTURER IMPACT ANALYSIS FOR RESIDENTIAL FURNACE FANS—PRESERVATION OF OPERATING
PROFIT MARKUP SCENARIO *
Base
case
Units
INPV ..................................................................
Change in INPV .................................................
Product Conversion Costs .................................
Capital Conversion Costs ..................................
Total Conversion Costs .....................................
Free Cash Flow .................................................
Free Cash Flow (change from Base Case) ......
$M ........
$M ........
(%) .......
$M ........
$M ........
$M ........
$M ........
% ..........
349.6
................
................
2.2
................
2.2
20.3
0.0
Trial standard level
1
2
3
4
5
332.3
(17.3)
(5.0)
18.8
8.8
27.7
11.3
(44.5)
313.2
(36.4)
(10.4)
23.6
11.1
34.7
8.8
(56.7)
311.0
(38.6)
(11.0)
25.3
11.8
37.1
8.0
(60.8)
290.6
(59.0)
(16.9)
25.5
15.1
40.6
6.4
(68.3)
288.8
(60.8)
(17.4)
27.1
15.7
42.8
5.6
(72.2)
6
147.2
(202.5)
(57.9)
29.4
134.7
164.2
(48.6)
(339.8)
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* Values in parentheses are negative values. All values have been rounded to the nearest tenth.
M = millions.
TSL 1 represents the most common
efficiency levels in the current market
for all product classes. At TSL 1, DOE
estimates impacts on INPV for
residential furnace fan manufacturers to
range from ¥$17.3 million to ¥$13.0
million, or a change in INPV of ¥5.0
percent to ¥3.7 percent. At this
potential standard level, industry free
cash flow is estimated to decrease by as
much as 44.5 percent to $11.3 million,
compared to the base-case value of
$20.3 million in the year before the
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compliance date (2018). DOE anticipates
industry conversion costs totaling $27.7
million at TSL 1.
TSL 2 represents EL 1 for the oil and
mobile home product classes, and EL 3
for all other product classes. At TSL 2,
DOE estimates impacts on INPV for
residential furnace fan manufacturers to
range from ¥$36.4 million to $10.4
million, or a change in INPV of ¥10.4
percent to 3.0 percent. At this potential
standard level, industry free cash flow
is estimated to decrease by as much as
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56.7 percent to $8.8 million, compared
to the base-case value of $20.3 million
in the year before the compliance date
(2018). DOE anticipates industry
conversion costs of $34.7 million at TSL
2.
TSL 3 represents EL 3 for all product
classes. At TSL 3, DOE estimates
impacts on INPV for residential furnace
fan manufacturers to range from ¥$38.6
million to $9.4 million, or a change in
INPV of ¥11.0 percent to 2.7 percent.
At this potential standard level,
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industry free cash flow is estimated to
decrease by as much as 60.8 percent to
$8.0 million, compared to the base-case
value of $20.3 million in the year before
the compliance date (2018). DOE
anticipates industry conversion costs of
$37.1 million at TSL 3.
TSL 4 represents the efficiency levels
that provide the highest NPV using a 7percent discount rate, and that also
result in a higher percentage of
consumers receiving an LCC benefit
rather than an LCC loss. At TSL 4, DOE
estimates impacts on INPV for
residential furnace fan manufacturers to
range from ¥$59.0 million to $48.2
million, or a change in INPV of ¥16.9
percent to 13.8 percent. At this potential
standard level, industry free cash flow
is estimated to decrease by as much as
68.3 percent to $6.4 million, compared
to the base-case value of $20.3 million
in the year before the compliance date
(2018). DOE anticipates industry
conversion costs totaling $40.6 million
at TSL 4.
TSL 5 represents the efficiency levels
that provide the maximum NPV using a
7-percent discount rate. At TSL 5, DOE
estimates impacts on INPV for
residential furnace fan manufacturers to
range from ¥$60.8 million to $48.0
million, or a change in INPV of ¥17.4
percent to 13.7 percent. At this potential
standard level, industry free cash flow
is estimated to decrease by as much as
72.2 percent to $5.6 million, compared
to the base-case value of $20.3 million
in the year before the compliance date
(2018). DOE anticipates industry
conversion costs of $42.8 million at TSL
5.
TSL 6 represents the max-tech
efficiency level for all product classes.
At TSL 6, DOE estimates impacts on
INPV for residential furnace fan
manufacturers to range from ¥$202.5
million to $72.8 million, or a change in
INPV of ¥57.9 percent to 20.8 percent.
At this potential standard level,
industry free cash flow is estimated to
decrease by as much as 339.8 percent to
¥$48.6 million, compared to the basecase value of $20.3 million in the year
before the compliance date (2018). DOE
anticipates industry conversion costs
totaling $164.2 million at TSL 6.
DOE anticipates very high capital
conversion costs at TSL 6 because
manufacturers would need to make
significant changes to their
manufacturing equipment and
production processes in order to
accommodate the use of backwardinclined impellers. This design option
would require modifying, or potentially
eliminating, current fan housings. DOE
also anticipates high product conversion
costs to develop new designs with
backward-inclined impellers for all their
products. Some manufacturers may also
have stranded assets from specialized
machines for building fan housing that
can no longer be used.
Impacts on Employment
To quantitatively assess the impacts
of energy conservation standards on
direct employment in the residential
furnace fan industry, DOE used the
GRIM to estimate the domestic labor
expenditures and number of employees
in the base case and at each TSL from
2014 through 2048. DOE used statistical
data from the U.S. Census Bureau’s 2011
Annual Survey of Manufacturers
(ASM),71 the results of the engineering
analysis, and interviews with
manufacturers to determine the inputs
necessary to calculate industry-wide
labor expenditures and domestic
employment levels. Labor expenditures
related to manufacturing of the product
are a function of the labor intensity of
the product, the sales volume, and an
assumption that wages remain fixed in
real terms over time. The total labor
expenditures in each year are calculated
by multiplying the MPCs by the labor
percentage of MPCs.
The total labor expenditures in the
GRIM were then converted to domestic
production employment levels by
dividing production labor expenditures
by the annual payment per production
worker (production worker hours times
the labor rate found in the U.S. Census
Bureau’s 2011 ASM). The estimates of
production workers in this section cover
workers, including line-supervisors who
are directly involved in fabricating and
assembling a product within the
manufacturing facility. Workers
performing services that are closely
associated with production operations,
such as materials handling tasks using
forklifts, are also included as production
labor. DOE’s estimates only account for
production workers who manufacture
the specific products covered by this
rulemaking.
The total direct employment impacts
calculated in the GRIM are the sum of
the changes in the number of
production workers resulting from the
new energy conservation standards for
residential furnace fans, as compared to
the base case.
TABLE V.15—POTENTIAL CHANGES IN THE NUMBER OF FURNACE FAN INDUSTRY EMPLOYMENT IN 2019
Trial standard level *
Base case
Total Number of Domestic Production Workers
in 2019 (assuming no changes in production
locations).
Total Number of Domestic Non-Production
Workers in 2019.
Range of Potential Changes in Domestic
Workers in 2019 **.
1
2
3
4
5
6
303
303 .........
303 .........
303 .........
301 ..............
301 ..............
349.
107
107 .........
107 .........
107 .........
106 ..............
106 ..............
123.
..................
(410) to 0
(410) to 0
(410) to 0
(410) to (3) ..
(410) to (3) ..
(410) to 62.
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* Numbers in parentheses represent negative values.
** DOE presents a range of potential employment impacts, where the lower range represents the scenario in which all domestic manufacturers
move production to other countries.
The employment impacts shown in
Table V.15 represent the potential
production and non-production
employment changes that could result
following the compliance date of a new
energy conservation standard for
residential furnace fans. The upper end
of the results in the table estimates the
maximum increase in the number of
production and non-production workers
after the implementation of new energy
conservation standards, and it assumes
71 ‘‘Annual Survey of Manufactures (ASM),’’ U.S.
Census Bureau (2011) (Available at: https://
www.census.gov/manufacturing/asm/).
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that manufacturers would continue to
produce the same scope of covered
products within the United States. The
lower end of the range indicates the
total number of U.S. production and
non-production workers in the industry
who could lose their jobs if all existing
production were moved outside of the
United States or if companies exited the
market. This scenario is highly
conservative. Even if all production was
relocated overseas, manufacturers
would likely maintain large portions of
domestic non-production staff (e.g.,
sales, marketing, technical, and
management employees). The industry
did not provide sufficient information
for DOE fully quantify the percentage of
the non-production workers that would
leave the country or be eliminated at
each evaluated standard level.
For residential furnace fans, DOE does
not expect significant changes in
domestic employment levels from
baseline to TSL 5. Based on the
engineering analysis, DOE has
concluded that most product lines could
be converted to meet the standard with
changes in motor technology and the
application of multi-staging designs.
While such designs require more
controls and have more complex
assembly, DOE does not believe the perunit labor requirements for the furnace
fan assembly would change
significantly.
The only standard level at which
significant changes in employment
would be expected is at TSL 6, the maxtech level. At TSL 6, DOE estimates
increases in labor costs because
backwards-inclined impeller assemblies
are heavier and require more robust
mounting approaches than are currently
used for forward-curved impeller
assemblies. Backward-inclined impeller
assemblies could require manufacturers
to adjust their assembly processes, with
the potential for increases in per-unit
labor requirements. However, DOE
received limited feedback from
manufacturers regarding the labor
required to produce furnace fans with
backward-curved impellers, because
they generally do not have any
experience in working with this design
option.
DOE notes that the employment
impacts discussed here are independent
of the indirect employment impacts to
the broader U.S. economy, which are
documented in chapter 15 of the final
rule TSD.
Impacts on Manufacturing Capacity
According to the residential furnace
fan manufacturers interviewed, the new
energy conservation standards being
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adopted in today’s final rule would not
significantly affect manufacturers’
production capacity, or throughput
levels. Some manufacturers noted in
interviews that testing resources could
potentially be a bottleneck to the
conversion process and cited the
potential need for adding in-house
testing capacity. However, in written
comments, stakeholders generally
agreed that a five-year lead time
between the publication date and
compliance date is appropriate for this
rulemaking.
Impacts on Subgroups of Manufacturers
Small manufacturers, niche
equipment manufacturers, and
manufacturers exhibiting a cost
structure substantially different from the
industry average could be affected
disproportionately. As discussed in
section IV.J, using average cost
assumptions developed for an industry
cash-flow estimate is inadequate to
assess differential impacts among
manufacturer subgroups.
For the residential furnace fans
industry, DOE identified and evaluated
the impact of new energy conservation
standards on one subgroup, specifically
small manufacturers. The SBA defines a
‘‘small business’’ as having 750
employees or less for NAICS 333415,
‘‘Air-Conditioning and Warm Air
Heating Equipment and Commercial
and Industrial Refrigeration Equipment
Manufacturing.’’ Based on this
definition, DOE identified 15
manufacturers in the residential furnace
fans industry that qualify as small
businesses. For a discussion of the
impacts on the small manufacturer
subgroup, see the regulatory flexibility
analysis in section VI.B of this notice
and chapter 12 of the final rule TSD.
Cumulative Regulatory Burden
While any one regulation may not
impose a significant burden on
manufacturers, the combined effects of
recent or impending regulations may
have serious consequences for some
manufacturers, groups of manufacturers,
or an entire industry. Assessing the
impact of a single regulation may
overlook this cumulative regulatory
burden. In addition to energy
conservation standards, other
regulations can significantly affect
manufacturers’ financial operations.
Multiple regulations affecting the same
manufacturer can strain profits and lead
companies to abandon product lines or
markets with lower expected future
returns than competing products. For
these reasons, DOE conducts an analysis
of cumulative regulatory burden as part
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of its rulemakings pertaining to
appliance efficiency.
During previous stages of this
rulemaking, DOE identified a number of
requirements in addition to new energy
conservation standards for residential
furnace fans. The following section
briefly summarizes those identified
regulatory requirements and addresses
comments DOE received with respect to
cumulative regulatory burden, as well as
other key related concerns that
manufacturers raised during interviews.
While the cumulative regulatory
burden analysis contained in the NOPR
reflects manufacturers’ concerns
regarding CC&E costs, DOE has decided
to exclude CC&E costs from the
cumulative burden analysis for the final
rule. The furnace fan test procedure
changed from the NOPR to the final
rule. Much of the concern relating to
CC&E costs expressed by stakeholders,
and summarized in the NOPR, had to do
with the old test procedure. The new
test procedure reduces burden
substantially. Also, for the final rule,
CC&E costs have been explicitly
incorporated into product conversion
costs inputted into the GRIM, so they
are no longer considered separately in
the cumulative regulatory burdens
section.
DOE Energy Conservation Standards
Companies that produce a wide range
of regulated products and equipment
may face more capital and product
development expenditures than
competitors with a narrower scope of
products and equipment. Many furnace
fan manufacturers also produce other
residential and commercial equipment.
In addition to the amended energy
conservation standards for furnace fans,
these manufacturers contend with
several other Federal regulations and
pending regulations that apply to other
products and equipment. DOE
recognizes that each regulation can
significantly affect a manufacturer’s
financial operations. Multiple
regulations affecting the same
manufacturer can quickly strain
manufacturers’ profits and possibly
cause an exit from the market. Table
V.16 lists the other DOE energy
conservation standards that could also
affect manufacturers of furnace fans in
the 3 years leading up to and after the
compliance date of the new energy
conservation standards for this
equipment. Additionally, at the request
of stakeholders, DOE has listed several
DOE rulemakings in the table below that
are currently in process but that have
not been finalized.
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38191
TABLE V.16—OTHER DOE REGULATIONS IMPACTING FURNACE FAN MANUFACTURERS
Number of
impacted
companies
Compliance
year
Regulation
Commercial Refrigeration Equipment .....................................................................
Commercial Packaged Air-Conditioning and Heating Equipment ..........................
Commercial/Industrial Fans and Blowers ...............................................................
Residential Boilers ..................................................................................................
Residential Non-Weatherized Gas Furnaces .........................................................
2017
* 2018
* 2019
* 2019
n/a
4
24
29
9
38
Estimated total industry
conversion costs
$184.0 million (2012$).
N/A.**
N/A.**
N/A.**
N/A.**
* The dates listed are an approximation. The exact dates are pending final DOE action.
** For energy conservation standards that have not been issued, DOE does not have finalized industry conversion cost data available.
EPA ENERGY STAR
cumulative regulatory burden. ENERGY
STAR specifications are as follows:
STAR specifications for residential
furnaces, central air conditioners, and
heat pumps would be a source of
During interviews, some
manufacturers stated that ENERGY
TABLE V.17—ENERGY STAR SPECIFICATIONS FOR HVAC PRODUCTS THAT USE FURNACE FANS
Gas Furnaces .................................
Oil Furnaces ....................................
Air-Source Heat Pumps ..................
Central Air Conditioners ..................
Rating of 90% AFUE or greater for U.S. South gas furnaces.
Rating of 95% AFUE or greater for U.S. North gas furnaces.
Less than or equal to 2.0% furnace fan efficiency.*
Rating of 85% AFUE or greater.
Less than or equal to 2.0% furnace fan efficiency.*
>= 8.2 HSPF/>= 14.5 SEER/>= 12 EER for split systems.
>= 8.0 HSPF/>= 14 SEER/>=11 EER for single-package equipment.
>= 14.5 SEER/>= 12 EER for split systems.
>= 14 SEER/>=11 EER for single-package equipment.
* Furnace fan efficiency in this context is furnace fan electrical consumption as a percentage of total furnace energy consumption in heating
mode.
DOE realizes that the cumulative
effect of several regulations on an
industry may significantly increase the
burden faced by manufacturers that
need to comply with multiple
regulations and certification programs
from different organizations and levels
of government. However, DOE notes
that certain standards, such as ENERGY
STAR, are optional for manufacturers.
As they are voluntary standards, they
are not considered by DOE to be part of
manufacturers’ cumulative regulatory
burden.
DOE discusses these and other
requirements (e.g., Canadian Energy
Efficiency Regulations, California Title
24, Low NOX requirements), and
includes the full details of the
cumulative regulatory burden analysis,
in chapter 12 of the final rule TSD. DOE
also discusses the impacts on the small
manufacturer subgroup in the regulatory
flexibility analysis in section VI.B of
this final rule.
3. National Impact Analysis
Significance of Energy Savings
For each TSL, DOE projected energy
savings for residential furnace fans
purchased in the 30-year period that
begins in the first full year of
compliance with amended standards
(2019–2048). The savings are measured
over the entire lifetime of products
purchased in the 30-year period. DOE
quantified the energy savings
attributable to each TSL as the
difference in energy consumption
between each standards case and the
base case. Table V.18 presents the
estimated primary energy savings for
each considered TSL, and Table V.19
presents the estimated FFC energy
savings for each considered TSL. The
energy savings in the tables below are
net savings that reflect the subtraction of
the additional gas or oil used by the
furnace associated with higherefficiency furnace fans. The approach
for estimating national energy savings is
further described in section IV.H.1.
The difference between primary
energy savings and FFC energy savings
for all TSLs is small (less than 1
percent), because the upstream energy
savings associated with the electricity
savings are partially or fully offset by
the upstream energy use from the
additional gas or oil used by the furnace
due to higher-efficiency furnace fans.
TABLE V.18—CUMULATIVE NATIONAL PRIMARY ENERGY SAVINGS FOR TRIAL STANDARD LEVELS FOR RESIDENTIAL
FURNACE FANS SOLD IN 2019–2048
Trial standard level
Product class
mstockstill on DSK4VPTVN1PROD with RULES2
1
2
3
4
5
6
quads
Non-Weatherized, Non-Condensing Gas Furnace Fan ..
Non-Weatherized, Condensing Gas Furnace Fan ..........
Weatherized Non-Condensing Gas Furnace Fan ...........
Non-Weatherized, Non-Condensing Oil Furnace Fan .....
Non-Weatherized Electric Furnace/Modular Blower Fan
Mobile Home Non-Weatherized, Non-Condensing Gas
Furnace Fan .................................................................
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0.278
0.048
0.006
0.032
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1.188
0.224
0.006
0.143
1.341
1.188
0.224
0.022
0.143
1.796
1.614
0.330
0.006
0.193
1.796
1.614
0.330
0.022
0.193
2.426
2.324
0.462
0.046
0.264
0.009
0.009
0.023
0.009
0.023
0.053
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TABLE V.18—CUMULATIVE NATIONAL PRIMARY ENERGY SAVINGS FOR TRIAL STANDARD LEVELS FOR RESIDENTIAL
FURNACE FANS SOLD IN 2019–2048—Continued
Trial standard level
Product class
1
2
3
4
5
6
quads
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ......................................................................
Mobile Home Electric Furnace/Modular Blower Fan .......
0.001
0.009
0.001
0.009
0.003
0.030
0.001
0.044
0.003
0.044
0.008
0.055
Total—All Classes ....................................................
0.679
2.922
2.974
3.994
4.024
5.639
Note: Components may not sum to total due to rounding.
TABLE V.19—CUMULATIVE NATIONAL FULL-FUEL-CYCLE ENERGY SAVINGS FOR TRIAL STANDARD LEVELS FOR
RESIDENTIAL FURNACE FANS SOLD IN 2019–2048
Trial standard level
Product class
1
2
3
4
5
6
quads
Non-Weatherized, Non-Condensing Gas Furnace Fan ..
Non-Weatherized, Condensing Gas Furnace Fan ..........
Weatherized Non-Condensing Gas Furnace Fan ...........
Non-Weatherized, Non-Condensing Oil Furnace Fan .....
Non-Weatherized Electric Furnace/Modular Blower Fan
Mobile Home Non-Weatherized, Non-Condensing Gas
Furnace Fan .................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ......................................................................
Mobile Home Electric Furnace/Modular Blower Fan .......
Total—All Classes ....................................................
0.297
0.278
0.048
0.006
0.032
1.338
1.176
0.225
0.006
0.145
1.338
1.176
0.225
0.020
0.145
1.793
1.604
0.331
0.006
0.196
1.793
1.604
0.331
0.020
0.196
2.428
2.314
0.463
0.044
0.268
0.009
0.009
0.022
0.009
0.022
0.052
0.001
0.010
0.680
0.001
0.010
2.909
0.003
0.030
2.958
0.001
0.045
3.986
0.003
0.045
4.014
0.008
0.056
5.635
Note: Components may not sum to total due to rounding.
OMB Circular A–4 72 requires
agencies to present analytical results,
including separate schedules of the
monetized benefits and costs that show
the type and timing of benefits and
costs. Circular A–4 also directs agencies
to consider the variability of key
elements underlying the estimates of
benefits and costs. For this rulemaking,
DOE undertook a sensitivity analysis
using nine, rather than 30, years of
product shipments. The choice of a ninyear period is a proxy for the timeline
in EPCA for the review of certain energy
conservation standards and potential
revision of and compliance with such
revised standards.73 The review
timeframe established in EPCA is
generally not synchronized with the
product lifetime, product manufacturing
cycles, or other factors specific to
residential furnace fans. Thus, such
results are presented for informational
purposes only and are not indicative of
any change in DOE’s analytical
methodology. The NES results based on
a 9-year analytical period are presented
in Table V.20. The impacts are counted
over the lifetime of products purchased
in 2019–2027.
TABLE V.20—CUMULATIVE NATIONAL PRIMARY ENERGY SAVINGS FOR TRIAL STANDARD LEVELS FOR RESIDENTIAL
FURNACE FANS SOLD IN 2019–2027
Trial standard level
Product class
1
2
3
4
5
6
mstockstill on DSK4VPTVN1PROD with RULES2
quads
Non-Weatherized, Non-Condensing Gas Furnace Fan ..
Non-Weatherized, Condensing Gas Furnace Fan ..........
Weatherized Non-Condensing Gas Furnace Fan ...........
Non-Weatherized, Non-Condensing Oil Furnace Fan .....
Non-Weatherized Electric Furnace/Modular Blower Fan
72 U.S. Office of Management and Budget,
‘‘Circular A–4: Regulatory Analysis’’ (Sept. 17,
2003) (Last accessed September 17, 2013 from
https://www.whitehouse.gov/omb/circulars_a004_a4/.)
73 Section 325(m) of EPCA requires DOE to review
its standards at least once every 6 years, and
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0.016
0.002
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0.075
0.002
0.043
0.454
0.316
0.075
0.009
0.043
requires, for certain products, a 3-year period after
any new standard is promulgated before
compliance is required, except that in no case may
any new standards be required within 6 years of the
compliance date of the previous standards. While
adding a 6-year review to the 3-year compliance
period adds up to 9 years, DOE notes that it may
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0.611
0.429
0.108
0.002
0.058
0.611
0.429
0.108
0.009
0.058
0.838
0.612
0.150
0.020
0.080
undertake reviews at any time within the 6-year
period and that the 3-year compliance date may
yield to the 6-year backstop. A 9-year analysis
period may not be appropriate given the variability
that occurs in the timing of standards reviews and
the fact that for some consumer products, the
compliance period is 5 years rather than 3 years.
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38193
TABLE V.20—CUMULATIVE NATIONAL PRIMARY ENERGY SAVINGS FOR TRIAL STANDARD LEVELS FOR RESIDENTIAL
FURNACE FANS SOLD IN 2019–2027—Continued
Trial standard level
Product class
1
2
3
4
5
6
quads
Mobile Home Non-Weatherized, Non-Condensing Gas
Furnace Fan .................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ......................................................................
Mobile Home Electric Furnace/Modular Blower Fan .......
0.003
0.003
0.007
0.003
0.007
0.018
0.000
0.003
0.000
0.003
0.001
0.009
0.000
0.013
0.001
0.013
0.002
0.017
Total—All Classes ....................................................
0.207
0.897
0.914
1.225
1.236
1.737
Note: Components may not sum to total due to rounding.
Net Present Value of Consumer Costs
and Benefits
DOE estimated the cumulative NPV of
the total costs and savings for
consumers that would result from the
TSLs considered for residential furnace
fans. In accordance with OMB’s
guidelines on regulatory analysis,74
DOE calculated NPV using both a 7percent and a 3-percent real discount
rate. Table V.21 shows the consumer
NPV results for each TSL considered for
residential furnace fans. In each case,
the impacts cover the lifetime of
products purchased in 2019–2048.
TABLE V.21—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFIT FOR TRIAL STANDARD LEVELS FOR RESIDENTIAL
FURNACE FANS SOLD IN 2019–2048
Discount
rate
%
Product class
Trial standard level
1
2
3
4
5
6
billion 2013$ *
Non-Weatherized,
Non-Condensing
Gas Furnace Fan ...............................
Non-Weatherized, Condensing Gas
Furnace Fan .......................................
Weatherized Non-Condensing Gas Furnace Fan ............................................
Non-Weatherized, Non-Condensing Oil
Furnace Fan .......................................
Non-Weatherized Electric Furnace/Modular Blower Fan ..................................
Mobile Home Non-Weatherized, NonCondensing Gas Furnace Fan ...........
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan .................
Mobile Home Electric Furnace/Modular
Blower Fan .........................................
3
mstockstill on DSK4VPTVN1PROD with RULES2
13.309
13.309
11.943
10.769
10.769
11.444
11.444
10.156
1.849
1.849
2.288
2.288
2.082
0.028
0.028
0.154
0.028
0.154
0.078
0.215
1.237
1.237
1.480
1.480
0.615
0.045
0.045
0.171
0.045
0.171
(0.039)
0.007
0.007
0.025
0.007
0.025
(0.005)
0.047
0.047
0.168
0.209
0.209
(0.099)
4.668
26.013
26.403
28.810
29.079
24.731
0.823
4.502
4.502
4.713
4.713
3.381
0.677
3.856
3.856
3.876
3.876
2.686
0.129
0.702
0.702
0.825
0.825
0.604
0.012
0.012
0.061
0.012
0.061
0.006
0.078
0.438
0.438
0.515
0.515
0.014
0.017
0.017
0.058
0.017
0.058
(0.071)
0.003
0.003
0.008
0.003
0.008
(0.010)
0.017
7
12.031
0.335
Non-Weatherized,
Non-Condensing
Gas Furnace Fan ...............................
Non-Weatherized, Condensing Gas
Furnace Fan .......................................
Weatherized Non-Condensing Gas Furnace Fan ............................................
Non-Weatherized, Non-Condensing Oil
Furnace Fan .......................................
Non-Weatherized Electric Furnace/Modular Blower Fan ..................................
Mobile Home Non-Weatherized, NonCondensing Gas Furnace Fan ...........
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan .................
Mobile Home Electric Furnace/Modular
Blower Fan .........................................
12.031
1.842
Total—All Classes ..........................
2.150
0.017
0.054
0.065
0.065
(0.102)
74 OMB Circular A–4, section E (Sept. 17, 2003)
(Available at: https://www.whitehouse.gov/omb/
circulars_a004_a-4).
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TABLE V.21—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFIT FOR TRIAL STANDARD LEVELS FOR RESIDENTIAL
FURNACE FANS SOLD IN 2019–2048—Continued
Discount
rate
%
Product class
Trial standard level
1
2
3
4
5
6
10.120
6.509
billion 2013$ *
Total—All Classes ..........................
1.754
9.545
9.679
10.024
* Numbers in parentheses indicate negative NPV.
The NPV results based on the
aforementioned 9-year analytical period
are presented in Table V.22. The
impacts are counted over the lifetime of
products purchased in 2019–2027. As
mentioned previously, this information
is presented for informational purposes
only and is not indicative of any change
in DOE’s analytical methodology or
decision criteria.
TABLE V.22—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFIT FOR TRIAL STANDARD LEVELS FOR RESIDENTIAL
FURNACE FANS SOLD IN 2019–2027
Discount
rate
%
Product class
Trial standard level
1
2
3
4
5
6
billion 2013$ *
Non-Weatherized,
Non-Condensing
Gas Furnace Fan ...............................
Non-Weatherized, Condensing Gas
Furnace Fan .......................................
Weatherized Non-Condensing Gas Furnace Fan ............................................
Non-Weatherized, Non-Condensing Oil
Furnace Fan .......................................
Non-Weatherized Electric Furnace/Modular Blower Fan ..................................
Mobile Home Non-Weatherized, NonCondensing Gas Furnace Fan ...........
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan .................
Mobile Home Electric Furnace/Modular
Blower Fan .........................................
3
5.527
4.908
3.784
3.784
4.005
4.005
3.550
0.777
0.777
0.945
0.945
0.864
0.015
0.082
0.015
0.082
0.064
0.080
0.463
0.463
0.549
0.549
0.217
0.019
0.019
0.073
0.019
0.073
(0.012)
0.003
0.003
0.010
0.003
0.010
(0.001)
0.017
0.017
0.061
0.074
0.074
(0.052)
1.819
10.106
10.278
11.137
11.266
9.537
0.444
2.433
2.433
2.531
2.531
1.799
0.325
1.840
1.840
1.845
1.845
1.290
0.070
0.384
0.384
0.446
0.446
0.333
0.008
0.008
0.040
0.008
0.040
0.015
0.039
0.220
0.220
0.257
0.257
0.001
0.009
0.009
0.033
0.009
0.033
(0.037)
0.001
0.001
0.004
0.001
0.004
(0.005)
0.008
0.008
0.026
0.031
0.031
(0.059)
0.905
Total—All Classes ..........................
5.527
0.015
7
5.028
0.139
Non-Weatherized,
Non-Condensing
Gas Furnace Fan ...............................
Non-Weatherized, Condensing Gas
Furnace Fan .......................................
Weatherized Non-Condensing Gas Furnace Fan ............................................
Non-Weatherized, Non-Condensing Oil
Furnace Fan .......................................
Non-Weatherized Electric Furnace/Modular Blower Fan ..................................
Mobile Home Non-Weatherized, NonCondensing Gas Furnace Fan ...........
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan .................
Mobile Home Electric Furnace/Modular
Blower Fan .........................................
5.028
0.652
Total—All Classes ..........................
0.893
4.904
4.980
5.128
5.186
3.338
mstockstill on DSK4VPTVN1PROD with RULES2
* Numbers in parentheses indicate negative NPV.
As noted in section IV.H.2, DOE
assumed no change in residential
furnace fan prices over the 2019–2048
period. In addition, DOE conducted a
sensitivity analysis using alternative
price trends: One in which prices
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decline over time, and one in which
prices increase over time. These price
trends, and the NPV results from the
associated sensitivity cases, are
described in appendix 10–C of the final
rule TSD.
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Indirect Impacts on Employment
DOE expects energy conservation
standards for residential furnace fans to
reduce energy costs for consumers, with
the resulting net savings being
redirected to other forms of economic
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activity. Those shifts in spending and
economic activity could affect the
demand for labor. As described in
section IV.N, DOE used an input/output
model of the U.S. economy to estimate
indirect employment impacts of the
TSLs that DOE considered in this
rulemaking. DOE understands that there
are uncertainties involved in projecting
employment impacts, especially
changes in the later years of the
analysis. Therefore, DOE generated
results for near-term time frames (2019
and 2024), where these uncertainties are
reduced.
The results suggest that today’s
standards would be likely to have
negligible impact on the net demand for
labor in the economy. The net change in
jobs is so small that it would be
imperceptible in national labor statistics
and might be offset by other,
unanticipated effects on employment.
Chapter 16 of the final rule TSD
presents more detailed results about
anticipated indirect employment
impacts.
4. Impact on Product Utility or
Performance
DOE has concluded that the standards
it is adopting in this final rule would
not lessen the utility or performance of
residential furnace fans.
5. Impact of Any Lessening of
Competition
EPCA directs DOE to consider any
lessening of competition that is likely to
result from standards. It also directs the
Attorney General of the United States
(Attorney General) to determine the
impact, if any, of any lessening of
competition likely to result from a
proposed standard and to transmit such
determination in writing to the
Secretary within 60 days of the
publication of a proposed rule, together
with an analysis of the nature and
extent of the impact. (42 U.S.C.
6295(o)(2)(B)(i)(V) and (ii))
To assist the Attorney General in
making such a determination for today’s
standards, DOE provided the
Department of Justice (DOJ) with copies
of the NOPR and the TSD for review. In
its assessment letter responding to DOE,
DOJ concluded that the proposed energy
conservation standards for residential
furnace fans are unlikely to have a
significant adverse impact on
competition. DOE is publishing the
Attorney General’s assessment at the
end of this final rule.
6. Need of the Nation To Conserve
Energy
An improvement in the energy
efficiency of the products subject to this
rule is likely to improve the security of
the nation’s energy system by reducing
overall demand for energy. Reduction in
the growth of electricity demand
resulting from energy conservation
standards may also improve the
reliability of the electricity system.
Reductions in national electric
38195
generating capacity estimated for each
considered TSL are reported in chapter
15 of the final rule TSD.
Energy savings from standards for the
residential furnace fan products covered
in today’s final rule could also produce
environmental benefits in the form of
reduced emissions of air pollutants and
greenhouse gases associated with
electricity production. Table V.23
provides DOE’s estimate of cumulative
emissions reductions projected to result
from the TSLs considered in this
rulemaking. The table includes both
power sector emissions and upstream
emissions. The emissions were
calculated using the multipliers
discussed in section IV.K. DOE reports
annual emissions reductions for each
TSL in chapter 13 of the final rule TSD.
As discussed in section IV.K, DOE did
not include NOX emissions reduction
from power plants in States subject to
CAIR, because an energy conservation
standard would not affect the overall
level of NOX emissions in those States
due to the emissions caps mandated by
CAIR. For SO2, under the MATS,
projected emissions will be far below
the cap established by CAIR, so it is
unlikely that excess SO2 emissions
allowances resulting from lower
electricity demand would be needed or
used to permit offsetting increases in
SO2 emissions by any regulated EGU.
Therefore, DOE believes that efficiency
standards will reduce SO2 emissions.
TABLE V.23—CUMULATIVE EMISSIONS REDUCTION FOR POTENTIAL STANDARDS FOR RESIDENTIAL FURNACE FANS
TSL
1
2
3
4
5
6
126.3
178.0
(33.8)
0.3
4.6
23.9
171.1
232.5
(38.7)
0.4
6.0
31.3
172.0
235.2
(40.2)
0.4
6.1
31.6
241.5
323.5
(51.1)
0.5
8.4
43.7
6.7
2.4
85.0
0.0
0.1
455.4
9.6
3.2
122.8
0.0
0.1
663.7
9.5
3.2
122.0
0.0
0.1
666.1
13.7
4.4
177.5
0.0
0.2
984.3
133.1
180.4
51.2
0.3
4.7
1402.4
479.3
180.6
235.7
84.0
0.4
6.2
1843.7
695.0
181.5
238.4
81.8
0.4
6.2
1859.3
697.7
255.2
327.9
126.4
0.5
8.6
2569.2
1028.0
Primary Energy Emissions *
CO2 (million metric tons) ......................................
SO2 (thousand tons) ............................................
NOX (thousand tons) ...........................................
Hg (tons) ..............................................................
N2O (thousand tons) ............................................
CH4 (thousand tons) ............................................
29.3
38.1
(5.2)
0.1
1.0
5.2
124.5
174.3
(32.4)
0.3
4.5
23.4
Upstream Emissions
mstockstill on DSK4VPTVN1PROD with RULES2
CO2 (million metric tons) ......................................
SO2 (thousand tons) ............................................
NOX (thousand tons) ...........................................
Hg (tons) ..............................................................
N2O (thousand tons) ............................................
CH4 (thousand tons) ............................................
1.7
0.5
22.5
0.0
0.0
127.0
6.7
2.4
84.9
0.0
0.1
447.7
Total FFC Emissions
CO2 (million metric tons) ......................................
SO2 (thousand tons) ............................................
NOX (thousand tons) ...........................................
Hg (tons) ..............................................................
N2O (thousand tons) ............................................
N2O thousand tons CO2eq ** ...............................
CH4 (thousand tons) ............................................
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38.6
17.2
0.1
1.0
302.2
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52.6
0.3
4.6
1378.9
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TABLE V.23—CUMULATIVE EMISSIONS REDUCTION FOR POTENTIAL STANDARDS FOR RESIDENTIAL FURNACE FANS—
Continued
TSL
1
CH4 million tons CO2eq ** ....................................
2
3303.3
3
4
5
6
11778
11982
17375
17442
25700
* Includes emissions from additional gas use associated with more-efficient furnace fans.
** CO2eq is the quantity of CO2 that would have the same global warming potential (GWP).
Note: Parentheses indicate negative values.
As part of the analysis for this final
rule, DOE estimated monetary benefits
likely to result from the reduced
emissions of CO2 and NOX estimated for
each of the TSLs considered for
residential furnace fans. As discussed in
section IV.L, for CO2, DOE used four
sets of values for the SCC developed by
an interagency process. Three sets of
values are based on the average SCC
from three integrated assessment
models, at discount rates of 2.5 percent,
3 percent, and 5 percent. The fourth set
represents the 95th-percentile SCC
estimate across all three models at a 3percent discount rate. The SCC values
for CO2 emissions reductions in 2015,
expressed in 2013$, are $12.0/ton,
$40.5/ton, $62.4/ton, and $119/ton. The
values for later years are higher due to
increasing damages as the magnitude of
projected climate change increases.
Table V.24 presents the global value of
CO2 emissions reductions at each TSL.
DOE calculated domestic values as a
range from 7 percent to 23 percent of the
global values, and these results are
presented in chapter 14 of the final rule
TSD.
TABLE V.24—GLOBAL PRESENT VALUE OF CO2 EMISSIONS REDUCTION FOR POTENTIAL STANDARDS FOR RESIDENTIAL
FURNACE FANS
SCC Case *
TSL
5% discount
rate, average
3% discount
rate, average
2.5% discount
rate, average
3% discount
rate, 95th
percentile
million 2013$
Primary Energy Emissions **
1
2
3
4
5
6
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
184
785
797
1,077
1,083
1,517
880
3,755
3,811
5,152
5,181
7,265
1,409
6,007
6,096
8,245
8,291
11,628
2,722
11,612
11,784
15,934
16,023
22,467
10.2
40.0
40.0
57.0
56.6
81.7
50.1
196
196
279
278
401
81
315
316
449
447
644
155
607
608
866
861
1,241
194
825
837
1,134
1,140
1,599
930
3,951
4,007
5,432
5,459
7,666
1,489
6,323
6,412
8,694
8,737
12,272
2,878
12,219
12,392
16,799
16,884
23,709
Upstream Emissions
1
2
3
4
5
6
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
Total FFC Emissions
1
2
3
4
5
6
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
mstockstill on DSK4VPTVN1PROD with RULES2
* For each of the four cases, the corresponding SCC value for emissions in 2015 is $12.0, $40.5, $62.4, and $119 per metric ton (2013$). The
values are for CO2 only (i.e., not CO2eq of other greenhouse gases).
** Includes site emissions from additional use of natural gas associated with more-efficient furnace fans.
DOE is well aware that scientific and
economic knowledge about the
contribution of CO2 and other
greenhouse gas (GHG) emissions to
changes in the future global climate and
the potential resulting damages to the
world economy continues to evolve
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rapidly. Thus, any value placed in this
rulemaking on reducing CO2 emissions
is subject to change. DOE, together with
other Federal agencies, will continue to
review various methodologies for
estimating the monetary value of
reductions in CO2 and other GHG
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emissions. This ongoing review will
consider the comments on this subject
that are part of the public record for this
and other rulemakings, as well as other
methodological assumptions and issues.
However, consistent with DOE’s legal
obligations, and taking into account the
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uncertainty involved with this
particular issue, DOE has included in
this final rule the most recent values
and analyses resulting from the
interagency review process.
DOE also estimated a range for the
cumulative monetary value of the
economic benefits associated with NOX
emissions reductions anticipated to
result from standards for the residential
furnace fan products that are the subject
of this final rule. The dollar-per-ton
values that DOE used are discussed in
38197
section IV.L. Table V.25 presents the
present value of cumulative NOX
emissions reductions for each TSL
calculated using the average dollar-perton values and 7-percent and 3-percent
discount rates.
TABLE V.25—PRESENT VALUE OF NOX EMISSIONS REDUCTION FOR POTENTIAL STANDARDS FOR RESIDENTIAL FURNACE
FANS
TSL
3% Discount rate
7% Discount rate
million 2013$
Power Sector and Site Emissions *
1
2
3
4
5
6
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
(3.8)
(27.1)
(28.6)
(31.0)
(32.5)
(39.4)
0.0
(3.7)
(4.1)
(2.8)
(3.3)
(2.1)
25.9
98.1
98.3
141.8
140.9
205.5
10.2
38.7
38.8
55.9
55.6
81.4
22.1
71.0
69.7
110.8
108.4
166.1
10.2
35.1
34.7
53.1
52.3
79.3
Upstream Emissions
1
2
3
4
5
6
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
Total FFC Emissions **
1
2
3
4
5
6
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
...............................................................................................................................................................
* Includes site emissions from additional use of natural gas associated with more-efficient furnace fans.
** Components may not sum to total due to rounding.
Note: Parentheses indicate negative values.
The NPV of the monetized benefits
associated with emissions reductions
can be viewed as a complement to the
NPV of the consumer savings calculated
for each TSL considered in this
rulemaking. Table V.26 presents the
NPV values that result from adding the
estimates of the potential economic
benefits resulting from reduced fullfuel-cycle CO2 and NOX emissions in
each of four valuation scenarios to the
NPV of consumer savings calculated for
each TSL considered in this rulemaking,
at both a 7-percent and a 3-percent
discount rate. The CO2 values used in
the columns of each table correspond to
the four scenarios for the valuation of
CO2 emission reductions discussed
above.
TABLE V.26—POTENTIAL STANDARDS FOR RESIDENTIAL FURNACE FANS: NET PRESENT VALUE OF CONSUMER SAVINGS
COMBINED WITH PRESENT VALUE OF MONETIZED BENEFITS FROM CO2 AND NOX EMISSIONS REDUCTIONS
Consumer NPV at 3% Discount Rate added with:
SCC Case $12.0/
metric ton CO2*
and low value for
NOX**
TSL
SCC Case $40.5/
metric ton CO2*
and medium value
for NOX**
SCC Case $62.4/
metric ton CO2*
and medium value
for NOX**
SCC Case $119/
metric ton CO2*
and high value for
NOX**
mstockstill on DSK4VPTVN1PROD with RULES2
billion 2013$
1
2
3
4
5
6
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
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30.3
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30.0
30.5
34.4
34.6
32.6
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32.9
37.6
37.9
37.2
03JYR2
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38.3
38.9
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46.1
48.6
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Federal Register / Vol. 79, No. 128 / Thursday, July 3, 2014 / Rules and Regulations
Consumer NPV at 7% Discount Rate added with:
SCC Case $12.0/
metric ton CO2*
and low value for
NOX**
TSL
SCC Case $40.5/
metric ton CO2*
and medium value
for NOX**
SCC Case $62.4/
metric ton CO2*
and medium value
for NOX**
SCC Case $119/
metric ton CO2*
and high value for
NOX**
billion 2013$
1
2
3
4
5
6
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
2.0
10.4
10.6
11.2
11.3
8.2
2.7
13.5
13.7
15.5
15.6
14.3
3.3
15.9
16.1
18.8
18.9
18.9
4.6
21.8
22.1
26.9
27.1
30.3
* These label values represent the global SCC in 2015, in 2013$.
** Low Value corresponds to $476 per ton of NOX emissions. Medium Value corresponds to $2,684 per ton, and High Value corresponds to
$4,893 per ton.
Although adding the value of
consumer savings to the values of
emission reductions provides a valuable
perspective, two issues should be
considered. First, the national operating
cost savings are domestic U.S. consumer
monetary savings that occur as a result
of market transactions, while the value
of CO2 reductions is based on a global
value. Second, the assessments of
operating cost savings and the SCC are
performed with different methods that
use quite different time frames for
analysis. The national operating cost
savings is measured for the lifetime of
products shipped in 2019–2048. The
SCC values, on the other hand, reflect
the present value of future climaterelated impacts resulting from the
emission of one metric ton of CO2 in
each year. Because of the long residence
time of CO2 in the atmosphere, these
impacts continue well beyond 2100.
mstockstill on DSK4VPTVN1PROD with RULES2
7. Other Factors
The Secretary of Energy, in
determining whether a standard is
economically justified, may consider
any other factors that the Secretary
deems to be relevant. (42 U.S.C.
6295(o)(2)(B)(i)(VI)) No other factors
were considered in this analysis.
C. Conclusions
When considering proposed
standards, the new or amended energy
conservation standard that DOE adopts
for any type (or class) of covered
product shall be designed to achieve the
maximum improvement in energy
efficiency that the Secretary determines
is technologically feasible and
economically justified. (42 U.S.C.
6295(o)(2)(A)) In determining whether a
standard is economically justified, the
Secretary must determine whether the
benefits of the standard exceed its
burdens by, to the greatest extent
practicable, considering the seven
statutory factors discussed previously.
(42 U.S.C. 6295(o)(2)(B)(i)) The new or
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amended standard must also result in
significant conservation of energy. (42
U.S.C. 6295(o)(3)(B))
For today’s final rule, DOE considered
the impacts of standards at each TSL,
beginning with the maximum
technologically feasible level, to
determine whether that level was
economically justified. Where the maxtech level was not justified, DOE then
considered the next most efficient level
and undertook the same evaluation until
it reached the highest efficiency level
that is both technologically feasible and
economically justified and saves a
significant amount of energy.
To aid the reader in understanding
the benefits and/or burdens of each TSL,
tables in this section summarize the
quantitative analytical results for each
TSL, based on the assumptions and
methodology discussed herein. The
efficiency levels contained in each TSL
are described in section V.A. In addition
to the quantitative results presented in
the tables, DOE also considers other
burdens and benefits that affect
economic justification. These include
the impacts on identifiable subgroups of
consumers who may be
disproportionately affected by a national
standard, and impacts on employment.
Section V.B.1.b presents the estimated
impacts of each TSL for these
subgroups. DOE discusses the impacts
on direct employment in residential
furnace fan manufacturing in section
V.B.2.b, and discusses the indirect
employment impacts in section V.B.3.c.
DOE also notes that the economics
literature provides a wide-ranging
discussion of how consumers trade off
upfront costs and energy savings in the
absence of government intervention.
Much of this literature attempts to
explain why consumers appear to
undervalue energy efficiency
improvements. There is evidence that
consumers undervalue future energy
savings as a result of: (1) A lack of
information; (2) a lack of sufficient
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salience of the long-term or aggregate
benefits; (3) a lack of sufficient savings
to warrant delaying or altering
purchases; (4) excessive focus on the
short term, in the form of inconsistent
weighting of future energy cost savings
relative to available returns on other
investments; (5) computational or other
difficulties associated with the
evaluation of relevant tradeoffs; and (6)
a divergence in incentives (for example,
renter versus owner or builder versus
purchaser). Other literature indicates
that with less than perfect foresight and
a high degree of uncertainty about the
future, consumers may trade off at a
higher than expected rate between
current consumption and uncertain
future energy cost savings. This
undervaluation suggests that regulation
that promotes energy efficiency can
produce significant net private gains (as
well as producing social gains by, for
example, reducing pollution).
In DOE’s current regulatory analysis,
potential changes in the benefits and
costs of a regulation due to changes in
consumer purchase decisions are
included in two ways. First, if
consumers forego a purchase of a
product in the standards case, this
decreases sales for product
manufacturers and the cost to
manufacturers is included in the MIA.
Second, DOE accounts for energy
savings attributable only to products
actually used by consumers in the
standards case; if a standard decreases
the number of products purchased by
consumers, this decreases the potential
energy savings from an energy
conservation standard. DOE provides
estimates of changes in the volume of
product purchases in chapter 9 of the
final rule TSD. DOE’s current analysis
does not explicitly control for
heterogeneity in consumer preferences,
preferences across subcategories of
products or specific features, or
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Federal Register / Vol. 79, No. 128 / Thursday, July 3, 2014 / Rules and Regulations
consumer price sensitivity variation
according to household income.75
While DOE is not prepared at present
to provide a fuller quantifiable
framework for estimating the benefits
and costs of changes in consumer
purchase decisions due to an energy
conservation standard, DOE is
committed to developing a framework
that can support empirical quantitative
tools for improved assessment of the
consumer welfare impacts of appliance
standards. DOE has posted a paper that
discusses the issue of consumer welfare
impacts of appliance standards, and
potential enhancements to the
methodology by which these impacts
are defined and estimated in the
regulatory process.76 DOE welcomes
comments on how to more fully assess
the potential impact of energy
conservation standards on consumer
choice and how to quantify this impact
in its regulatory analysis.
estimated for each TSL for residential
furnace fans. The national impacts are
measured over the lifetime of furnace
fans purchased in the 30-year period
that begins in the first full year of
compliance with amended standards
(2019–2048). The energy savings,
emissions reductions, and value of
emissions reductions refer to full-fuelcycle results. Results that refer to
primary energy savings are presented in
chapter 10 of the final rule TSD.
1. Benefits and Burdens of Trial
Standard Levels Considered for
Residential Furnace Fans
Table V.27 through Table V.29
summarize the quantitative impacts
TABLE V.27—SUMMARY OF ANALYTICAL RESULTS FOR RESIDENTIAL FURNACE FAN STANDARDS: NATIONAL IMPACTS
Category
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
National Full-Fuel-Cycle Energy Savings quads
0.680
2.909
2.958
3.986
4.014
5.635
26.013
9.545
26.403
9.679
28.810
10.024
29.079
10.120
24.731
6.509
131.2
176.7
52.6
0.3
4.6
1378.9
471.1
11778
133.1
180.4
51.2
0.3
4.7
1402.4
479.3
11982
180.6
235.7
84.0
0.4
6.2
1843.7
695.0
17375
181.5
238.4
81.8
0.4
6.2
1859.3
697.7
17442
255.2
327.9
126.4
0.5
8.6
2569.2
1028.0
25700
0.837 to 12.392
0.0697
0.0347
1.134 to 16.799
0.1108
0.0531
1.140 to 16.884
0.1084
0.0523
1.599 to 23.709
0.1661
0.0793
NPV of Consumer Benefits 2013$ billion
3% discount rate ....................
7% discount rate ....................
4.668
1.754
Cumulative Emissions Reduction (FFC Emissions)
CO2 million metric tons ..........
SO2 thousand tons .................
NOX thousand tons ................
Hg tons ...................................
N2O thousand tons ................
N2O thousand tons CO2eq * ..
CH4 thousand tons .................
CH4 million tons CO2eq * .......
31.0
38.6
17.2
0.1
1.0
302.2
132.1
3303
Value of Emissions Reduction (FFC Emissions) 2013$ billion
CO2 ** .....................................
NOX—3% discount rate .........
NOX—7% discount rate .........
0.194 to 2.878
0.0221
0.0102
0.825 to 12.219
0.0710
0.0351
* CO2eq is the quantity of CO2 that would have the same global warming potential (GWP).
** Range of the economic value of CO2 reductions is based on interagency estimates of the global benefit of reduced CO2 emissions.
TABLE V.28—SUMMARY OF ANALYTICAL RESULTS FOR RESIDENTIAL FURNACE FAN STANDARDS: MANUFACTURER AND
AVERAGE OR MEDIAN CONSUMER IMPACTS
Category
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
311.0 to
359.1
(11.0) to
2.7
290.6 to
397.8
(16.9) to
13.8
288.8 to
397.6
(17.4) to
13.7
147.2 to
422.4
(57.9) to
20.8
Manufacturer Impacts
Industry NPV (baseline value is 349.6) (2013$ in millions) ........
Change in Industry NPV (% change) ..........................................
332.3 to
336.6
(5.0) to
(3.7)
313.2 to
360.0
(10.4) to
3.0
mstockstill on DSK4VPTVN1PROD with RULES2
Consumer Average LCC Savings (2013$)
Non-Weatherized, Non-condensing Gas Furnace Fan ...............
Non-Weatherized, Condensing Gas Furnace Fan ......................
Weatherized Non-Condensing Gas Furnace Fan .......................
Non-Weatherized, Non-Condensing Oil Furnace Fan .................
Non-Weatherized Electric Furnace/Modular Blower Fan ............
Mobile Home Non-Weatherized, Non-condensing Gas Furnace
Fan ...........................................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan
75 P.C. Reiss and M.W. White, Household
Electricity Demand, Revisited, Review of Economic
Studies (2005) 72, 853–883.
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$85
$58
$67
$46
$29
$471
$335
$378
$46
$181
$471
$335
$378
$259
$181
$506
$341
$447
$46
$204
$506
$341
$447
$259
$204
$431
$268
$391
$80
$81
$36
$35
$36
$35
$144
$133
$36
$35
$144
$133
($58)
($51)
76 Alan Sanstad, Notes on the Economics of
Household Energy Consumption and Technology
Choice. Lawrence Berkeley National Laboratory
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(2010) (Available at: https://www1.eere.energy.gov/
buildings/appliance_standards/pdfs/consumer_ee_
theory.pdf (Last accessed May 3, 2013).
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TABLE V.28—SUMMARY OF ANALYTICAL RESULTS FOR RESIDENTIAL FURNACE FAN STANDARDS: MANUFACTURER AND
AVERAGE OR MEDIAN CONSUMER IMPACTS—Continued
Category
TSL 1
Mobile Home Electric Furnace/Modular Blower Fan ...................
TSL 2
$19
TSL 3
$19
TSL 4
TSL 5
TSL 6
$70
$85
$85
($54)
Consumer Median PBP (years)
Non-Weatherized, Non-condensing Gas Furnace Fan ...............
Non-Weatherized, Condensing Gas Furnace Fan ......................
Weatherized Non-Condensing Gas Furnace Fan .......................
Non-Weatherized, Non-Condensing Oil Furnace Fan .................
Non-Weatherized Electric Furnace/Modular Blower Fan ............
Mobile Home Non-Weatherized, Non-condensing Gas Furnace
Fan ...........................................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan
Mobile Home Electric Furnace/Modular Blower Fan ...................
1.12
1.18
0.73
1.70
1.94
2.60
2.87
1.79
1.70
2.64
2.60
2.87
1.79
4.65
2.64
5.41
5.78
4.42
1.70
3.21
5.41
5.78
4.42
4.65
3.21
10.16
11.01
8.19
18.56
11.45
2.72
2.31
2.07
2.72
2.31
2.07
6.84
6.65
3.58
2.72
2.31
4.09
6.84
6.65
4.09
24.38
31.27
14.90
Note: Parentheses indicate negative values.
TABLE V.29—SUMMARY OF ANALYTICAL RESULTS FOR RESIDENTIAL FURNACE FAN STANDARDS: DISTRIBUTION OF
CONSUMER LCC IMPACTS
Product Class
TSL 1
Non-Weatherized, Non-Condensing Gas Furnace Fan:
Net Cost ............................................................................................
No Impact .........................................................................................
Net Benefit ........................................................................................
Non-Weatherized, Condensing Gas Furnace Fan:
Net Cost ............................................................................................
No Impact .........................................................................................
Net Benefit ........................................................................................
Weatherized Non-Condensing Gas Furnace Fan:
Net Cost ............................................................................................
No Impact .........................................................................................
Net Benefit ........................................................................................
Non-Weatherized, Non-Condensing Oil Furnace Fan:
Net Cost ............................................................................................
No Impact .........................................................................................
Net Benefit ........................................................................................
Non-Weatherized Electric Furnace/Modular Blower Fan:
Net Cost ............................................................................................
No Impact .........................................................................................
Net Benefit ........................................................................................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan:
Net Cost ............................................................................................
No Impact .........................................................................................
Net Benefit ........................................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan:
Net Cost ............................................................................................
No Impact .........................................................................................
Net Benefit ........................................................................................
Mobile Home Electric Furnace/Modular Blower Fan:
Net Cost ............................................................................................
No Impact .........................................................................................
Net Benefit ........................................................................................
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
1%
68%
30%
17%
25%
58%
17%
25%
58%
30%
14%
56%
30%
14%
56%
50%
0%
50%
1%
75%
24%
11%
41%
48%
11%
41%
48%
23%
34%
43%
23%
34%
43%
51%
0%
49%
0%
81%
19%
3%
56%
41%
3%
56%
41%
16%
33%
51%
16%
33%
51%
41%
0%
59%
13%
71%
17%
13%
71%
17%
44%
28%
28%
13%
71%
17%
44%
28%
28%
78%
0%
22%
4%
73%
22%
17%
37%
45%
17%
37%
45%
23%
25%
51%
23%
25%
51%
60%
0%
39%
10%
56%
34%
10%
56%
34%
55%
0%
45%
10%
56%
34%
55%
0%
45%
80%
0%
20%
5%
68%
27%
5%
68%
27%
37%
29%
33%
5%
68%
27%
37%
29%
33%
82%
0%
18%
7%
71%
22%
7%
71%
22%
26%
38%
37%
32%
26%
43%
32%
26%
43%
75%
0%
25%
mstockstill on DSK4VPTVN1PROD with RULES2
Note: Components may not sum to total due to rounding.
First, DOE considered TSL 6, which
would save an estimated total of 5.63
quads of energy, an amount DOE
considers significant. TSL 6 has an
estimated NPV of consumer benefit of
$6.51 billion using a 7-percent discount
rate, and $24.7 billion using a 3-percent
discount rate.
The cumulative CO2 emissions
reduction at TSL 6 is 255.2 million
metric tons. The estimated monetary
value of the CO2 emissions reductions
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ranges from $1.60 billion to $23.71
billion. The other emissions reductions
are 327.9 thousand tons of SO2, 126.4
thousand tons of NOX, 0.5 tons of Hg,
8.6 thousand tons of N2O, and 1,028.0
thousand tons of CH4.
At TSL 6, the average LCC savings are
positive for: (1) Non-weatherized, noncondensing gas furnace fans; (2) nonweatherized, condensing gas furnace
fans; (3) weatherized non-condensing
gas furnace fans; (4) non-weatherized,
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non-condensing oil furnace fans; and (5)
non-weatherized electric furnace/
modular blower fans. The LCC savings
are negative for: (1) Mobile home nonweatherized, non-condensing gas
furnace fans; (2) mobile home nonweatherized, condensing gas furnace
fans; and (3) mobile home electric
furnace/modular blower fans. The
median payback period is lower than
the median product lifetime (which is
21.2 years for gas and electric furnace
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fans) for all of the product classes
except for: (1) Mobile home nonweatherized, non-condensing gas
furnace fans, and (2) mobile home nonweatherized, condensing. The share of
consumers experiencing an LCC cost
(increase in LCC) is higher than the
share experiencing an LCC benefit
(decrease in LCC) for all of the product
classes except for weatherized noncondensing gas furnace fans.
At TSL 6, manufacturers may expect
diminished profitability due to
increases in product costs, stranded
assets, capital investments in equipment
and tooling, decreases in unit
shipments, and expenditures related to
engineering and testing. The projected
change in INPV ranges from a decrease
of $202.5 million to an increase of $72.8
million based on DOE’s manufacturer
markup scenarios. The upper bound of
$72.8 million is considered an
optimistic scenario for manufacturers
because it assumes manufacturers can
fully pass on substantial increases in
product costs and maintain existing
mark ups. DOE recognizes the risk of
large negative impacts on industry if
manufacturers’ expectations concerning
reduced profit margins are realized. TSL
6 could reduce INPV in the residential
furnace fan industry by up to 57.9
percent if impacts reach the lower
bound of the range.
Accordingly, the Secretary concludes
that at TSL 6 for residential furnace
fans, the benefits of significant energy
savings, positive NPV of consumer
benefit, emission reductions and the
estimated monetary value of the CO2
emissions reductions, as well as positive
average LCC savings for most product
classes would be outweighed by the
high percentage of consumers that
would experience an LCC cost in all of
the product classes, and the substantial
reduction in INPV for manufacturers.
Consequently, DOE has concluded that
TSL 6 is not economically justified.
Next, DOE considered TSL 5, which
would save an estimated total of 4.01
quads of energy, an amount DOE
considers significant. TSL 5 has an
estimated NPV of consumer benefit of
$10.1 billion using a 7-percent discount
rate, and $29.1 billion using a 3-percent
discount rate.
The cumulative CO2 emissions
reduction at TSL 5 is 181.5 million
metric tons. The estimated monetary
value of the CO2 emissions reductions
ranges from $1.14 billion to $16.88
billion. The other emissions reductions
are 238.4 thousand tons of SO2, 81.8
thousand tons of NOX, 0.4 tons of Hg,
6.2 thousand tons of N2O, and 697.7
thousand tons of CH4.
At TSL 5, the average LCC savings are
positive for all of the product classes.
The median payback period is lower
than the average product lifetime for all
of the product classes. The share of
consumers experiencing an LCC benefit
(decrease in LCC) is higher than the
share experiencing an LCC cost
(increase in LCC) for five of the product
classes (non-weatherized, noncondensing gas furnace fans; nonweatherized, condensing gas furnace
fans; weatherized non-condensing gas
furnace fans; non-weatherized electric
furnace/modular blower fans; and
mobile home electric furnace/modular
blower fans), but lower for the other
three product classes.
At TSL 5, the projected change in
INPV ranges from a decrease of $60.8
million to an increase of $48.0 million.
At TSL 5, DOE recognizes the risk of
negative impacts if manufacturers’
expectations concerning reduced profit
margins are realized. If the lower bound
of the range of impacts is reached, as
DOE expects, TSL 5 could result in a net
loss of 17.4 percent in INPV for
residential furnace fan manufacturers.
Accordingly, the Secretary concludes
that at TSL 5 for residential furnace
fans, the benefits of significant energy
savings, positive NPV of consumer
benefit, positive average LCC savings for
all of the product classes, emission
reductions and the estimated monetary
value of the CO2 emissions reductions,
would be outweighed by the high
percentage of consumers that would be
negatively impacted for some of the
product classes, and the substantial
reduction in INPV for manufacturers.
Consequently, DOE has concluded that
TSL 5 is not economically justified.
Next, DOE considered TSL 4, which
would save an estimated total of 3.99
quads of energy, an amount DOE
considers significant. TSL 4 has an
estimated NPV of consumer benefit of
$10.0 billion using a 7-percent discount
rate, and $28.8 billion using a 3-percent
discount rate.
The cumulative CO2 emissions
reduction at TSL 4 is 180.6 million
metric tons. The estimated monetary
value of the CO2 emissions reductions
ranges from $1.13 billion to $16.8
billion. The other emissions reductions
are 235.7 thousand tons of SO2, 84.0
thousand tons of NOX, 0.4 tons of Hg,
6.2 thousand tons of N2O, and 695.0
thousand tons of CH4.
At TSL 4, the average LCC savings are
positive for all of the product classes.
The median payback period is lower
than the average product lifetime for all
of the product classes. The share of
consumers experiencing an LCC benefit
(decrease in LCC) is higher than the
share experiencing an LCC cost
(increase in LCC) for all of the product
classes.
At TSL 4, the projected change in
INPV ranges from a decrease of $59.0
million to an increase of $48.2 million.
At TSL 4, DOE recognizes the risk of
negative impacts if manufacturers’
expectations concerning reduced profit
margins are realized. If the lower bound
of the range of impacts is reached, as
DOE expects, TSL 4 could result in a net
loss of 16.9 percent in INPV for
residential furnace fan manufacturers.
After considering the analysis and
weighing the benefits and the burdens,
the Secretary concludes that at TSL 4 for
residential furnace fans, the benefits of
significant energy savings, positive NPV
of consumer benefit, positive average
LCC savings for all of the product
classes, emission reductions and the
estimated monetary value of the CO2
emissions reductions would outweigh
the reduction in INPV for
manufacturers. The Secretary has
concluded that TSL 4 would save a
significant amount of energy and is
technologically feasible and
economically justified. Therefore, DOE
today is adopting the energy
conservation standards for residential
furnace fans at TSL 4. Table V.30
presents the energy conservation
standards for residential furnace fans.
mstockstill on DSK4VPTVN1PROD with RULES2
TABLE V.30—ENERGY CONSERVATION STANDARDS FOR RESIDENTIAL FURNACE FANS
Product class
Standard: FER * (W/1000 cfm)
Non-Weatherized, Non-Condensing Gas Furnace Fan .............................................................................................
Non-Weatherized, Condensing Gas Furnace Fan ....................................................................................................
Weatherized Non-Condensing Gas Furnace Fan .....................................................................................................
Non-Weatherized, Non-Condensing Oil Furnace Fan ...............................................................................................
Non-Weatherized Electric Furnace/Modular Blower Fan ...........................................................................................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan ......................................................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan ..............................................................................
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03JYR2
FER
FER
FER
FER
FER
FER
FER
=
=
=
=
=
=
=
0.044
0.044
0.044
0.071
0.044
0.071
0.071
×
×
×
×
×
×
×
QMax
QMax
QMax
QMax
QMax
QMax
QMax
+
+
+
+
+
+
+
182
195
199
382
165
222
240
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Federal Register / Vol. 79, No. 128 / Thursday, July 3, 2014 / Rules and Regulations
TABLE V.30—ENERGY CONSERVATION STANDARDS FOR RESIDENTIAL FURNACE FANS—Continued
Product class
Standard: FER * (W/1000 cfm)
Mobile Home Electric Furnace/Modular Blower Fan .................................................................................................
Mobile Home Weatherized Non-Condensing Gas Furnace Fan ...............................................................................
Mobile Home Non-Weatherized Non-Condensing Oil Furnace Fan .........................................................................
FER = 0.044 × QMax + 101
Reserved
Reserved
* QMax is the airflow, in cfm, at the maximum airflow-control setting measured using the final DOE test procedure. 79 FR 500, 524 (Jan. 3,
2014).
2. Summary of Benefits and Costs
(Annualized) of Today’s Standards
The benefits and costs of today’s
standards can also be expressed in terms
of annualized values. The annualized
monetary values are the sum of: (1) The
annualized national economic value,
expressed in 2013$, of the benefits from
operating products that meet the
standards (consisting primarily of
operating cost savings from using less
energy, minus increases in equipment
purchase costs, which is another way of
representing consumer NPV), and (2)
the monetary value of the benefits of
emission reductions, including CO2
emission reductions.77 The value of the
CO2 reductions, otherwise known as the
Social Cost of Carbon (SCC), is
calculated using a range of values per
metric ton of CO2 developed by a recent
interagency process.
Although combining the values of
operating savings and CO2 reductions
provides a useful perspective, two
issues should be considered. First, the
national operating savings are domestic
U.S. consumer monetary savings that
occur as a result of market transactions
while the value of CO2 reductions is
based on a global value. Second, the
assessments of operating cost savings
and SCC are performed with different
methods that use different time frames
for analysis. The national operating cost
savings is measured for the lifetime of
products shipped in 2019–2048. The
SCC values, on the other hand, reflect
the present value of future climaterelated impacts resulting from the
emission of one metric ton of CO2 in
each year over a very long period.
Table V.31 shows the annualized
values for today’s standards for
residential furnace fans. The results
under the primary estimate are as
follows. (All monetary values below are
expressed in 2013$.) Using a 7-percent
discount rate for benefits and costs other
than CO2 reduction (for which DOE
used a 3-percent discount rate along
with the SCC series corresponding to a
value of $40.5/ton in 2015), the cost of
the residential furnace fan standards in
today’s rule is $358 million per year in
increased equipment costs, while the
benefits are $1,416 million per year in
reduced equipment operating costs,
$312 million in CO2 reductions, and
$5.61 million in reduced NOX
emissions. In this case, the net benefit
amounts to $1,376 million per year.
Using a 3-percent discount rate for all
benefits and costs and the SCC series
corresponding to a value of $40.5/ton in
2015, Table V.31 shows the cost of the
residential furnace fans standards in
today’s rule is $355 million per year in
increased equipment costs, while the
benefits are $2010 million per year in
reduced operating costs, $312 million in
CO2 reductions, and $6.36 million in
reduced NOX emissions. In this case, the
net benefit amounts to $1,973 million
per year.
TABLE V.31—ANNUALIZED BENEFITS AND COSTS OF STANDARDS (TSL 4) FOR RESIDENTIAL FURNACE FANS
Primary
estimate *
Discount rate
Low net
benefits
estimate
High net
benefits
estimate
million 2013$/year
Benefits:
Consumer Operating Cost Savings .....................................................
7%
3%
5%
3%
2.5%
3%
7%
3%
1416
2010
90
312
459
965
5.61
6.36
1167
1626
77
268
393
828
4.80
5.35
1718
2467
108
377
555
1166
6.82
7.86
7% plus CO2 range
7%
3% plus CO2 range
3%
1,512 to 2,387
1,734
2,106 to 2,981
2,328
1,249 to 2,000
1,439
1,708 to 2,459
1,899
1,833 to 2,891
2,102
2,583 to 3,641
2,852
7%
3%
358
355
314
304
410
419
7% plus CO2 range
7%
1,154 to 2,029
1,376
935 to 1,685
1,125
1,423 to 2,481
1,692
CO2 Reduction Monetized Value ($12.0/t case) ** ..............................
CO2 Reduction Monetized Value ($40.5/t case) ** ..............................
CO2 Reduction Monetized Value ($62.4/t case) ** ..............................
CO2 Reduction Monetized Value ($119/t case) ** ...............................
NOX Reduction Monetized Value (at $2,684/ton) ** ............................
Total Benefits † .................................................................................
Costs:
Consumer Incremental Product Costs .................................................
mstockstill on DSK4VPTVN1PROD with RULES2
Net Benefits:
Total † ...............................................................................................
77 DOE used a two-step calculation process to
convert the time-series of costs and benefits into
annualized values. First, DOE calculated a present
value in 2013, the year used for discounting the
NPV of total consumer costs and savings, for the
time-series of costs and benefits using discount
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rates of 3 and 7 percent for all costs and benefits
except for the value of CO2 reductions. For the
latter, DOE used a range of discount rates. From the
present value, DOE then calculated the fixed annual
payment over a 30-year period, starting in 2013,
that yields the same present value. The fixed annual
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payment is the annualized value. Although DOE
calculated annualized values, this does not imply
that the time-series of cost and benefits from which
the annualized values were determined would be a
steady stream of payments.
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TABLE V.31—ANNUALIZED BENEFITS AND COSTS OF STANDARDS (TSL 4) FOR RESIDENTIAL FURNACE FANS—Continued
Discount rate
Primary
estimate *
Low net
benefits
estimate
High net
benefits
estimate
million 2013$/year
3% plus CO2 range
3%
1,750 to 2,625
1,973
1,404 to 2,155
1,595
2,164 to 3,222
2,433
* This table presents the annualized costs and benefits associated with residential furnace fans shipped in 2019–2048. These results include
benefits to consumers which accrue after 2048 from the products purchased in 2019–2048. Costs incurred by manufacturers, some of which may
be incurred in preparation for the rule, are not directly included, but are indirectly included as part of incremental equipment costs. The Primary,
Low Benefits, and High Benefits Estimates utilize projections of energy prices and housing starts from the AEO 2013 Reference case, Low Estimate, and High Estimate, respectively. Incremental product costs reflect a constant product price trend in the Primary Estimate, an increasing
price trend in the Low Benefits Estimate, and a decreasing price trend in the High Benefits Estimate.
** The CO2 values represent global values of the SCC, in 2013$, in 2015 under several scenarios. The first three cases use the averages of
SCC distributions calculated using 5%, 3%, and 2.5% discount rates, respectively. The fourth case represents the 95th percentile of the SCC distribution calculated using a 3% discount rate. The SCC values increase over time. The value for NOX (in 2013$) is the average of the low and
high values used in DOE’s analysis.
† Total Benefits for both the 3% and 7% cases are derived using the series corresponding to the SCC value of $40.5/t in 2015. In the rows labeled ‘‘7% plus CO2 range’’ and ‘‘3% plus CO2 range,’’ the operating cost and NOX benefits are calculated using the labeled discount rate, and
those values are added to the full range of CO2 values.
VI. Procedural Issues and Regulatory
Review
A. Review Under Executive Orders
12866 and 13563
Section 1(b)(1) of Executive Order
12866, ‘‘Regulatory Planning and
Review,’’ 58 FR 51735 (Oct. 4, 1993),
requires each agency to identify the
problem that it intends to address,
including, where applicable, the failures
of private markets or public institutions
that warrant new agency action, as well
as to assess the significance of that
problem. The problems that today’s
standards address, are as follows:
mstockstill on DSK4VPTVN1PROD with RULES2
(1) There is a lack of consumer information
and/or information processing capability
about energy efficiency opportunities in the
home appliance market.
(2) There is asymmetric information (one
party to a transaction has more and better
information than the other) and/or high
transactions costs (costs of gathering
information and effecting exchanges of goods
and services).
(3) There are external benefits resulting
from improved energy efficiency of
residential furnace fans that are not captured
by the users of such equipment. These
benefits include externalities related to
environmental protection and energy security
that are not reflected in energy prices, such
as reduced emissions of greenhouse gases.
In addition, DOE has determined that
today’s regulatory action is an
‘‘economically significant regulatory
action’’ under section 3(f) of Executive
Order 12866. Accordingly, section
6(a)(3) of the Executive Order requires
that DOE prepare a regulatory impact
analysis (RIA) for this rule and that the
Office of Information and Regulatory
Affairs (OIRA) in the OMB review this
rule. DOE presented to OIRA for review
the draft rule and other documents
prepared for this rulemaking, including
the RIA, and has included these
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documents in the rulemaking record.
The assessments prepared pursuant to
Executive Order 12866 can be found in
the technical support document for this
rulemaking.
DOE has also reviewed this regulation
pursuant to Executive Order 13563,
issued on January 18, 2011. 76 FR 3281
(Jan. 21, 2011). Executive Order 13563
is supplemental to and explicitly
reaffirms the principles, structures, and
definitions governing regulatory review
established in Executive Order 12866.
To the extent permitted by law, agencies
are required by Executive Order 13563
to: (1) Propose or adopt a regulation
only upon a reasoned determination
that its benefits justify its costs
(recognizing that some benefits and
costs are difficult to quantify); (2) tailor
regulations to impose the least burden
on society, consistent with obtaining
regulatory objectives, taking into
account, among other things, and to the
extent practicable, the costs of
cumulative regulations; (3) select, in
choosing among alternative regulatory
approaches, those approaches that
maximize net benefits (including
potential economic, environmental,
public health and safety, and other
advantages; distributive impacts; and
equity); (4) to the extent feasible, specify
performance objectives, rather than
specifying the behavior or manner of
compliance that regulated entities must
adopt; and (5) identify and assess
available alternatives to direct
regulation, including providing
economic incentives to encourage the
desired behavior, such as user fees or
marketable permits, or providing
information upon which choices can be
made by the public.
DOE emphasizes as well that
Executive Order 13563 requires agencies
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to use the best available techniques to
quantify anticipated present and future
benefits and costs as accurately as
possible. In its guidance, the Office of
Information and Regulatory Affairs has
emphasized that such techniques may
include identifying changing future
compliance costs that might result from
technological innovation or anticipated
behavioral changes. For the reasons
stated in the preamble, DOE believes
that today’s final rule is consistent with
these principles, including the
requirement that, to the extent
permitted by law, benefits justify costs
and that net benefits are maximized.
B. Review Under the Regulatory
Flexibility Act
The Regulatory Flexibility Act (5
U.S.C. 601 et seq.) requires preparation
of a final regulatory flexibility analysis
(FRFA) for any rule that by law must be
proposed for public comment, unless
the agency certifies that the rule, if
promulgated, will not have a significant
economic impact on a substantial
number of small entities. As required by
Executive Order 13272, ‘‘Proper
Consideration of Small Entities in
Agency Rulemaking,’’ 67 FR 53461
(August 16, 2002), DOE published
procedures and policies on February 19,
2003, to ensure that the potential
impacts of its rules on small entities are
properly considered during the
rulemaking process. 68 FR 7990. DOE
has made its procedures and policies
available on the Office of the General
Counsel’s Web site (https://energy.gov/
gc/office-general-counsel). DOE has
prepared the following FRFA for the
products that are the subject of this
rulemaking.
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1. Description and Estimated Number of
Small Entities Regulated
mstockstill on DSK4VPTVN1PROD with RULES2
Methodology for Estimating the Number
of Small Entities
For the manufacturers of residential
furnace fans, the Small Business
Administration (SBA) has set a size
threshold, which defines those entities
classified as ‘‘small businesses’’ for the
purposes of the statute. DOE used the
SBA’s small business size standards to
determine whether any small entities
would be subject to the requirements of
the rule. 65 FR 30836, 30848 (May 15,
2000), as amended at 65 FR 53533,
53544 (Sept. 5, 2000) and codified at 13
CFR part 121. The size standards are
listed by NAICS code and industry
description and are available at: https://
www.sba.gov/sites/default/files/files/
Size_Standards_Table.pdf. Residential
furnace fan manufacturing is classified
under NAICS 333415, ‘‘AirConditioning and Warm Air Heating
Equipment and Commercial and
Industrial Refrigeration Equipment
Manufacturing.’’ The SBA sets a
threshold of 750 employees or less for
an entity to be considered as a small
business for this category.
To estimate the number of companies
that could be small business
manufacturers of products covered by
this rulemaking, DOE conducted a
market survey using available public
information to identify potential small
manufacturers. DOE’s research involved
public databases (e.g., AHRI Directory,78
the SBA Database 79), individual
company Web sites, and market
research tools (e.g., Hoovers Web site 80)
to create a list of companies that
manufacture or sell products covered by
this rulemaking. DOE also asked
stakeholders and industry
representatives if they were aware of
any other small manufacturers during
manufacturer interviews and at DOE
public meetings. DOE reviewed
publicly-available data and contacted
select companies on its list, as
necessary, to determine whether they
met the SBA’s definition of a small
business manufacturer of covered
residential furnace fans. DOE screened
out companies that do not offer
products covered by this rulemaking, do
not meet the definition of a ‘‘small
business,’’ or are foreign owned and
operated.
DOE initially identified 38
manufacturers of residential furnace fan
products sold in the U.S. DOE then
determined that 23 were large
78 See https://www.ahridirectory.org/
ahriDirectory/pages/home.aspx.
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manufacturers or manufacturers that are
foreign owned and operated. DOE was
able to determine that 15 domestic
manufacturers meet the SBA’s
definition of a ‘‘small business’’ and
manufacture products covered by this
rulemaking.
Manufacturer Participation
Before issuing this Notice, DOE
attempted to contact all the small
business manufacturers of residential
furnace fans it had identified. One of the
small businesses consented to being
interviewed during the MIA interviews.
DOE also obtained information about
small business impacts while
interviewing large manufacturers.
Industry Structure
The 15 identified domestic
manufacturers of residential furnace
fans that qualify as small businesses
under the SBA size standard account for
a small fraction of industry shipments.
Generally, manufacturers of furnaces are
also manufacturers of furnace fan
products. The market for residential gas
furnaces is almost completely held by
seven large manufacturers, and small
manufacturers in total account for only
1 percent of unit sales in the market.
These seven large manufacturers also
control 97 percent of the market for
central air conditioners. The market for
mobile home furnaces is primarily held
by one large manufacturer. In contrast,
the market for domestic oil furnaces is
almost entirely comprised of small
manufacturers.
Comparison Between Large and Small
Entities
Today’s standards for residential
furnace fans could cause small
manufacturers to be at a disadvantage
relative to large manufacturers. One way
in which small manufacturers could be
at a disadvantage is that they may be
disproportionately affected by product
conversion costs. Product redesign,
testing, and certification costs tend to be
fixed per basic model and do not scale
with sales volume. For each model,
small businesses must make
investments in research and
development to redesign their products,
but because they have lower sales
volumes, they must spread these costs
across fewer units. In addition, because
small manufacturers have fewer
engineers than large manufacturers, they
would need to allocate a greater portion
of their available resources to meet a
standard. Since engineers may need to
spend more time redesigning and testing
79 See https://dsbs.sba.gov/dsbs/search/dsp_
dsbs.cfm.
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existing models as a result of the new
standard, they may have less time to
develop new products.
Furthermore, smaller manufacturers
may lack the purchasing power of larger
manufacturers. For example, since
motor suppliers give discounts to
manufacturers based on the number of
motors they purchase, larger
manufacturers may have a pricing
advantage because they have higher
volume purchases. This purchasing
power differential between high-volume
and low-volume orders applies to other
furnace fan components as well,
including the impeller fan blade,
transformer, and capacitor.
2. Description and Estimate of
Compliance Requirements
Since the standard in today’s final
rule for residential furnace fans could
cause small manufacturers to be at a
disadvantage relative to large
manufacturers, DOE cannot certify that
today’s standards would not have a
significant impact on a significant
number of small businesses, and
consequently, DOE has prepared this
FRFA.
At TSL 4, the level adopted in today’s
document, DOE estimates capital
conversion costs of $0.14 million and
product conversion costs of $0.23
million over a five-year conversion
period for a typical small manufacturer.
This is compared to capital conversion
costs of $0.59 and product conversion
costs of $1.00 million over a five-year
conversion period for a typical large
manufacturer. These costs and their
impacts are described in detail below.
To estimate how small manufacturers
would be potentially impacted, DOE
used the market share of small
manufacturers to estimate the annual
revenue, earnings before interest and tax
(EBIT), and research and development
(R&D) expense for a typical small
manufacturer. DOE then compared these
costs to the required product conversion
costs at each TSL for both an average
small manufacturer and an average large
manufacturer. Table VI.1 and VI.2 show
the capital and product conversion costs
for a typical small manufacturer versus
those of a typical large manufacturer.
Tables VI.3 and VI.4 report the total
conversion costs as a percentage of
annual R&D expense, annual revenue,
and EBIT for a typical small and large
manufacturer, respectively. In the
following tables, TSL 4 represents the
adopted standard.
80 See
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TABLE VI.1—COMPARISON OF TYPICAL SMALL AND LARGE MANUFACTURER’S CAPITAL CONVERSION COSTS
Capital
conversion
costs for
typical small
manufacturer
(in 2013$
millions)
TSL
TSL
TSL
TSL
TSL
TSL
1
2
3
4
5
6
.......................................................................................................................................................................
.......................................................................................................................................................................
.......................................................................................................................................................................
.......................................................................................................................................................................
.......................................................................................................................................................................
.......................................................................................................................................................................
Capital
conversion
costs for
typical large
manufacturer
(in 2013$
millions)
0.08
0.10
0.11
0.14
0.14
1.24
0.35
0.44
0.46
0.59
0.62
5.28
TABLE VI.2:—COMPARISON OF TYPICAL SMALL AND LARGE MANUFACTURER’S PRODUCT CONVERSION COSTS
Product
conversion
costs for
typical small
manufacturer
(in 2013$
millions)
TSL
TSL
TSL
TSL
TSL
TSL
1
2
3
4
5
6
.......................................................................................................................................................................
.......................................................................................................................................................................
.......................................................................................................................................................................
.......................................................................................................................................................................
.......................................................................................................................................................................
.......................................................................................................................................................................
Product
conversion
costs for
typical large
manufacturer
(in 2013$
millions)
0.17
0.22
0.23
0.23
0.25
0.27
0.74
0.93
0.99
1.00
1.06
1.15
TABLE VI.3—IMPACTS OF CONVERSION COSTS ON A SMALL MANUFACTURER
Capital conversion cost
as a percentage of annual
capital
expenditures
TSL
TSL
TSL
TSL
TSL
TSL
1
2
3
4
5
6
Product conversion cost
as a percentage of annual
R&D expense
Total conversion cost as a
percentage of
annual
revenue
Total conversion cost as a
percentage of
annual EBIT
69%
86%
92%
117%
122%
1048%
185%
232%
249%
250%
266%
289%
5%
6%
7%
8%
8%
31%
72%
90%
96%
105%
111%
427%
...............................................................................................................
...............................................................................................................
...............................................................................................................
...............................................................................................................
...............................................................................................................
...............................................................................................................
TABLE VI.4—IMPACTS OF CONVERSION COSTS ON A LARGE MANUFACTURER
Capital conversion cost
as a percentage of annual
capital
expenditures
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TSL
TSL
TSL
TSL
TSL
TSL
1
2
3
4
5
6
Product conversion cost
as a percentage of annual
R&D
expense
Total conversion cost as a
percentage of
annual
revenue
Total conversion cost as a
percentage of
annual EBIT
3%
4%
4%
5%
5%
45%
8%
10%
11%
11%
11%
12%
0%
0%
0%
0%
0%
1%
3%
4%
4%
5%
5%
18%
...............................................................................................................
...............................................................................................................
...............................................................................................................
...............................................................................................................
...............................................................................................................
...............................................................................................................
Based on the results in Table VI.1 and
Table VI.2, DOE understands that the
potential conversions costs faced by
small manufacturers may be
proportionally greater than those faced
by larger manufacturers. Small
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manufacturers have less engineering
staff and lower R&D budgets. They also
have lower capital expenditures
annually. As a result, the conversion
costs incurred by a small manufacturer
would likely be a larger percentage of its
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annual capital expenditures, R&D
expenses, revenue, and EBIT, than those
for a large manufacturer.
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3. Duplication, Overlap, and Conflict
with Other Rules and Regulations
DOE is not aware of any rules or
regulations that duplicate, overlap, or
conflict with the rule being adopted
today.
4. Significant Alternatives to the Rule
The discussion above analyzes
impacts on small businesses that would
result from the other TSLs DOE
considered. Although TSLs lower than
the proposed TSLs would be expected
to reduce the impacts on small entities,
DOE is required by EPCA to establish
standards that achieve the maximum
improvement in energy efficiency that is
technologically feasible and
economically justified, and result in a
significant conservation of energy. Thus,
DOE rejected the lower TSLs.
In addition to the other TSLs being
considered, the NOPR TSD includes a
regulatory impact analysis in chapter
17. For residential furnace fans, this
report discusses the following policy
alternatives: (1) No standard, (2)
consumer rebates, (3) consumer tax
credits, (4) manufacturer tax credits, and
(5) early replacement. DOE does not
intend to consider these alternatives
further because they are either not
feasible to implement without authority
and funding from Congress, or are
expected to result in energy savings that
are much smaller (ranging from less
than 1 percent to less than 31 percent)
than those that would be achieved by
the considered energy conservation
standards.
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C. Review Under the Paperwork
Reduction Act
Manufacturers of furnace fans, or their
third party representatives, must certify
to DOE that their products comply with
any applicable energy conservation
standard. In certifying compliance,
manufacturers or their third-party
representatives must test their
equipment according to the DOE test
procedure for furnace fans, including
any amendments adopted for that test
procedure. Manufacturers or their thirdparty representatives must then submit
certification reports and compliance
statements using DOE’s electronic Webbased tool, the Compliance and
Certification Management System
(CCMS), regarding product
characteristics and energy consumption
information regarding basic models of
furnace fans distributed in commerce in
the U.S. CCMS uses product-specific
templates that manufacturers are
required to use when submitting
certification data to DOE. See https://
www.regulations.doe.gov/ccms.
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The collection-of-information
requirement for furnace fan certification
is subject to review and approval by
OMB under the Paperwork Reduction
Act (PRA). This requirement has been
submitted to OMB for approval. Public
reporting burden for the certification is
estimated to average 30 hours per
response, including the time for
reviewing instructions, searching
existing data sources, gathering and
maintaining the data needed, and
completing and reviewing the collection
of information. Note that the
certification and recordkeeping
requirements for certain consumer
products in 10 CFR part 430 have
previously been approved by OMB and
assigned OMB control number 1910–
1400; the certification requirement for
furnace fans will be included in this
collection once approved by OMB. DOE
will notify the public of OMB approval
through a Federal Register notice.
Public comment is sought regarding:
whether this proposed collection of
information is necessary for the proper
performance of the functions of the
agency, including whether the
information shall have practical utility;
the accuracy of the burden estimate;
ways to enhance the quality, utility, and
clarity of the information to be
collected; and ways to minimize the
burden of the collection of information,
including through the use of automated
collection techniques or other forms of
information technology. Send comments
on these or any other aspects of the
collection of information to the DOE
program official listed in the ADDRESSES
section above, and email to Chad_S._
Whiteman@omb.eop.gov.
Notwithstanding any other provision
of the law, no person is required to
respond to, nor shall any person be
subject to a penalty for failure to comply
with, a collection of information subject
to the requirements of the PRA, unless
that collection of information displays a
currently valid OMB Control Number.
B5.1(b) apply. Therefore, DOE has made
a CX determination for this rulemaking,
and DOE does not need to prepare an
Environmental Assessment or
Environmental Impact Statement for
this rule. DOE’s CX determination for
this rule is available at https://
cxnepa.energy.gov/.
D. Review Under the National
Environmental Policy Act of 1969
Pursuant to the National
Environmental Policy Act (NEPA) of
1969, DOE has determined that this rule
fits within the category of actions
included in Categorical Exclusion (CX)
B5.1 and otherwise meets the
requirements for application of a CX.
See 10 CFR Part 1021, App. B, B5.1(b);
1021.410(b) and Appendix B, B(1)–(5).
The rule fits within the category of
actions because it is a rulemaking that
establishes energy conservation
standards for consumer products or
industrial equipment, and for which
none of the exceptions identified in CX
F. Review Under Executive Order 12988
With respect to the review of existing
regulations and the promulgation of
new regulations, section 3(a) of
Executive Order 12988, ‘‘Civil Justice
Reform,’’ imposes on Federal agencies
the general duty to adhere to the
following requirements: (1) Eliminate
drafting errors and ambiguity; (2) write
regulations to minimize litigation; (3)
provide a clear legal standard for
affected conduct rather than a general
standard; and (4) promote simplification
and burden reduction. 61 FR 4729 (Feb.
7, 1996). Regarding the review required
by section 3(a), section 3(b) of Executive
Order 12988 specifically requires that
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E. Review Under Executive Order 13132
Executive Order 13132, ‘‘Federalism.’’
64 FR 43255 (August 10, 1999) imposes
certain requirements on Federal
agencies formulating and implementing
policies or regulations that preempt
State law or that have Federalism
implications. The Executive Order
requires agencies to examine the
constitutional and statutory authority
supporting any action that would limit
the policymaking discretion of the
States and to carefully assess the
necessity for such actions. The
Executive Order also requires agencies
to have an accountable process to
ensure meaningful and timely input by
State and local officials in the
development of regulatory policies that
have Federalism implications. On
March 14, 2000, DOE published a
statement of policy describing the
intergovernmental consultation process
it will follow in the development of
such regulations. 65 FR 13735. DOE has
examined this final rule and has
determined that it would not have a
substantial direct effect on the States, on
the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government. EPCA governs and
prescribes Federal preemption of State
regulations as to energy conservation for
the products that are the subject of
today’s final rule. States can petition
DOE for exemption from such
preemption to the extent, and based on
criteria, set forth in EPCA. (42 U.S.C.
6297) No further action is required by
Executive Order 13132.
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Executive agencies make every
reasonable effort to ensure that the
regulation: (1) Clearly specifies the
preemptive effect, if any; (2) clearly
specifies any effect on existing Federal
law or regulation; (3) provides a clear
legal standard for affected conduct
while promoting simplification and
burden reduction; (4) specifies the
retroactive effect, if any; (5) adequately
defines key terms; and (6) addresses
other important issues affecting clarity
and general draftsmanship under any
guidelines issued by the Attorney
General. Section 3(c) of Executive Order
12988 requires Executive agencies to
review regulations in light of applicable
standards in section 3(a) and section
3(b) to determine whether they are met
or it is unreasonable to meet one or
more of them. DOE has completed the
required review and determined that, to
the extent permitted by law, this final
rule meets the relevant standards of
Executive Order 12988.
G. Review Under the Unfunded
Mandates Reform Act of 1995
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA) requires
each Federal agency to assess the effects
of Federal regulatory actions on State,
local, and Tribal governments and the
private sector. Public Law 104–4, sec.
201 (codified at 2 U.S.C. 1531). For a
proposed regulatory action likely to
result in a rule that may cause the
expenditure by State, local, and Tribal
governments, in the aggregate, or by the
private sector of $100 million or more
in any one year (adjusted annually for
inflation), section 202 of UMRA requires
a Federal agency to publish a written
statement that estimates the resulting
costs, benefits, and other effects on the
national economy. (2 U.S.C. 1532(a), (b))
The UMRA also requires a Federal
agency to develop an effective process
to permit timely input by elected
officers of State, local, and Tribal
governments on a ‘‘significant
intergovernmental mandate,’’ and
requires an agency plan for giving notice
and opportunity for timely input to
potentially affected small governments
before establishing any requirements
that might significantly or uniquely
affect them. On March 18, 1997, DOE
published a statement of policy on its
process for intergovernmental
consultation under UMRA. 62 FR
12820. DOE’s policy statement is also
available at https://energy.gov/sites/
prod/files/gcprod/documents/umra_
97.pdf.
Although today’s final rule, which
adopts new energy conservation
standards for residential furnace fans,
does not contain a Federal
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intergovernmental mandate, it may
require annual expenditures of $100
million or more by the private sector.
Specifically, the final rule could require
expenditures of $100 million or more,
including: (1) Investment in research
and development and in capital
expenditures by residential furnace fans
manufacturers in the years between the
final rule and the compliance date for
the new standards, and (2) incremental
additional expenditures by consumers
to purchase higher-efficiency residential
furnace fans, starting at the compliance
date for the applicable standard.
Section 202 of UMRA authorizes a
Federal agency to respond to the content
requirements of UMRA in any other
statement or analysis that accompanies
the final rule. 2 U.S.C. 1532(c). The
content requirements of section 202(b)
of UMRA relevant to a private sector
mandate substantially overlap the
economic analysis requirements that
apply under section 325(o) of EPCA and
Executive Order 12866. The
SUPPLEMENTARY INFORMATION section of
this final rule and the ‘‘Regulatory
Impact Analysis’’ section of the TSD for
this final rule respond to those
requirements.
Under section 205 of UMRA, the
Department is obligated to identify and
consider a reasonable number of
regulatory alternatives before
promulgating a rule for which a written
statement under section 202 is required.
2 U.S.C. 1535(a). DOE is required to
select from those alternatives the most
cost-effective and least burdensome
alternative that achieves the objectives
of the rule unless DOE publishes an
explanation for doing otherwise, or the
selection of such an alternative is
inconsistent with law. As required by 42
U.S.C. 6295(f) and (o), today’s final rule
establishes energy conservation
standards for residential furnace fans
that are designed to achieve the
maximum improvement in energy
efficiency that DOE has determined to
be both technologically feasible and
economically justified. A full discussion
of the alternatives considered by DOE is
presented in the ‘‘Regulatory Impact
Analysis’’ section of the TSD for this
final rule.
H. Review Under the Treasury and
General Government Appropriations
Act, 1999
Section 654 of the Treasury and
General Government Appropriations
Act, 1999 (Pub. L. 105–277) requires
Federal agencies to issue a Family
Policymaking Assessment for any rule
that may affect family well-being. This
rule would not have any impact on the
autonomy or integrity of the family as
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38207
an institution. Accordingly, DOE has
concluded that it is not necessary to
prepare a Family Policymaking
Assessment.
I. Review Under Executive Order 12630
Pursuant to Executive Order 12630,
‘‘Governmental Actions and Interference
with Constitutionally Protected Property
Rights,’’ 53 FR 8859 (March 18, 1988),
DOE has determined that this regulation
would not result in any takings that
might require compensation under the
Fifth Amendment to the U.S.
Constitution.
J. Review Under the Treasury and
General Government Appropriations
Act, 2001
Section 515 of the Treasury and
General Government Appropriations
Act, 2001 (44 U.S.C. 3516 note) provides
for Federal agencies to review most
disseminations of information to the
public under information quality
guidelines established by each agency
pursuant to general guidelines issued by
OMB. OMB’s guidelines were published
at 67 FR 8452 (Feb. 22, 2002), and
DOE’s guidelines were published at 67
FR 62446 (Oct. 7, 2002). DOE has
reviewed today’s final rule under the
OMB and DOE guidelines and has
concluded that it is consistent with
applicable policies in those guidelines.
K. Review Under Executive Order 13211
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use,’’ 66 FR 28355 (May
22, 2001), requires Federal agencies to
prepare and submit to OIRA at OMB, a
Statement of Energy Effects for any
proposed significant energy action. A
‘‘significant energy action’’ is defined as
any action by an agency that
promulgates or is expected to lead to
promulgation of a final rule, and that:
(1) Is a significant regulatory action
under Executive Order 12866, or any
successor order; and (2) is likely to have
a significant adverse effect on the
supply, distribution, or use of energy, or
(3) is designated by the Administrator of
OIRA as a significant energy action. For
any proposed significant energy action,
the agency must give a detailed
statement of any adverse effects on
energy supply, distribution, or use
should the proposal be implemented,
and of reasonable alternatives to the
action and their expected benefits on
energy supply, distribution, and use.
DOE has concluded that today’s
regulatory action, which sets forth
energy conservation standards for
residential furnace fans, is not a
significant energy action because the
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new standards are not likely to have a
significant adverse effect on the supply,
distribution, or use of energy, nor has it
been designated as such by the
Administrator at OIRA. Accordingly,
DOE has not prepared a Statement of
Energy Effects on the final rule.
L. Review Under the Information
Quality Bulletin for Peer Review
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On December 16, 2004, OMB, in
consultation with the Office of Science
and Technology Policy (OSTP), issued
its Final Information Quality Bulletin
for Peer Review (the Bulletin). 70 FR
2664 (Jan. 14, 2005). The Bulletin
establishes that certain scientific
information shall be peer reviewed by
qualified specialists before it is
disseminated by the Federal
Government, including influential
scientific information related to agency
regulatory actions. The purpose of the
bulletin is to enhance the quality and
credibility of the Government’s
scientific information. Under the
Bulletin, the energy conservation
standards rulemaking analyses are
‘‘influential scientific information,’’
which the Bulletin defines as ‘‘scientific
information the agency reasonably can
determine will have or does have a clear
and substantial impact on important
public policies or private sector
decisions.’’ Id. at 2667.
In response to OMB’s Bulletin, DOE
conducted formal in-progress peer
reviews of the energy conservation
standards development process and
analyses and has prepared a Peer
Review Report pertaining to the energy
conservation standards rulemaking
analyses. Generation of this report
involved a rigorous, formal, and
documented evaluation using objective
criteria and qualified and independent
reviewers to make a judgment as to the
technical/scientific/business merit, the
actual or anticipated results, and the
productivity and management
effectiveness of programs and/or
projects. The ‘‘Energy Conservation
Standards Rulemaking Peer Review
Report’’ dated February 2007 has been
disseminated and is available at the
following Web site:
www1.eere.energy.gov/buildings/
appliance_standards/peer_review.html.
M. Congressional Notification
17:09 Jul 02, 2014
Jkt 232001
List of Subjects
10 CFR Part 429
Administrative practice and
procedure, Commercial equipment,
Confidential business information,
Energy conservation, Household
appliances, Imports, Reporting and
recordkeeping requirements.
10 CFR Part 430
Administrative practice and
procedure, Confidential business
information, Energy conservation,
Household appliances, Imports,
Intergovernmental relations, Small
businesses.
Issued in Washington, DC, on June 25,
2014.
David T. Danielson,
Assistant Secretary, Energy Efficiency and
Renewable Energy.
For the reasons stated in the
preamble, DOE amends parts 429 and
430 of chapter II, subchapter D, of title
10 of the Code of Federal Regulations,
as set forth below:
PART 429—CERTIFICATION,
COMPLIANCE, AND ENFORCEMENT
FOR CONSUMER PRODUCTS AND
COMMERCIAL AND INDUSTRIAL
EQUIPMENT
1. The authority citation for part 429
continues to read as follows:
■
Authority: 42 U.S.C. 6291–6317.
§ 429.12
[Amended]
2. Section 429.12 is amended by:
a. Removing in paragraph (b)(13)
‘‘429.54’’ and adding in its place
‘‘429.58’’;
■ b. Removing in paragraph (d) table,
first column, second row (i.e., for
products with a submission deadline of
May 1st) the word ‘‘and’’ and adding
‘‘and Residential furnace fans’’ at the
end of the listed products.
■ 3. Section 429.58 is amended by:
■ a. Adding in paragraph (a)(2)
introductory text ‘‘within the scope of
appendix AA of subpart B of part 430’’
after ‘‘basic model of furnace fan’’; and
■ b. Adding paragraph (b).
The addition reads as follows:
■
■
§ 429.58
As required by 5 U.S.C. 801, DOE will
report to Congress on the promulgation
of this rule prior to its effective date.
The report will state that it has been
determined that the rule is a ‘‘major
rule’’ as defined by 5 U.S.C. 804(2).
VerDate Mar<15>2010
VII. Approval of the Office of the
Secretary
The Secretary of Energy has approved
publication of this final rule.
Furnace fans.
*
*
*
*
*
(b) Certification reports. (1) The
requirements of § 429.12 are applicable
to residential furnace fans; and
(2) Pursuant to § 429.12(b)(13), a
certification report shall include the
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following public product-specific
information: The fan energy rating (FER)
in watts per thousand cubic feet per
minute (W/1000 cfm); the calculated
maximum airflow at the reference
system external static pressure (ESP) in
cubic feet per minute (cfm); the control
system configuration for achieving the
heating and constant-circulation
airflow-control settings required for
determining FER as specified in the
furnace fan test procedure (10 CFR part
430, subpart B, appendix AA); the
measured steady-state gas, oil, or
electric heat input rate (QIN) in the
heating setting required for determining
FER; and for modular blowers, the
manufacturer and model number of the
electric heat resistance kit with which it
is equipped for certification testing.
PART 430—ENERGY CONSERVATION
PROGRAM FOR CONSUMER
PRODUCTS
4. The authority citation for part 430
continues to read as follows:
■
Authority: 42 U.S.C. 6291–6309; 28 U.S.C.
2461 note.
5. Section 430.2 is amended by adding
definitions for ‘‘small-duct high-velocity
(SDHV) electric furnace’’ and ‘‘smallduct high-velocity (SDHV) modular
blower’’ in alphabetical order to read as
follows:
■
§ 430.2
Definitions.
*
*
*
*
*
Small-duct high-velocity (SDHV)
electric furnace means an electric
furnace that:
(1) Is designed for, and produces, at
least 1.2 inches of external static
pressure when operated at the certified
air volume rate of 220–350 CFM per
rated ton of cooling in the highest
default cooling airflow-control setting;
and
(2) When applied in the field, uses
high velocity room outlets generally
greater than 1,000 fpm that have less
than 6.0 square inches of free area.
Small-duct high-velocity (SDHV)
modular blower means a modular
blower that:
(1) Is designed for, and produces, at
least 1.2 inches of external static
pressure when operated at the certified
air volume rate of 220–350 CFM per
rated ton of cooling in the highest
default cooling airflow-controls setting;
and
(2) When applied in the field, uses
high velocity room outlets generally
greater than 1,000 fpm that have less
than 6.0 square inches of free area.
*
*
*
*
*
■ 6. Section 430.32 is amended by
adding paragraph (y) to read as follows:
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§ 430.32 Energy and water conservation
standards and their effective dates.
*
*
*
*
*
(y) Residential furnace fans.
Residential furnace fans incorporated in
the products listed in Table 1 of this
paragraph and manufactured on and
after July 3, 2019, shall have a fan
energy rating (FER) value that meets or
is less than the following values:
TABLE 1—ENERGY CONSERVATION STANDARDS FOR COVERED RESIDENTIAL FURNACE FANS*
Product class
FER ** (Watts/cfm)
Non-Weatherized, Non-Condensing Gas Furnace Fan (NWG–NC) .....................................................................
Non-Weatherized, Condensing Gas Furnace Fan (NWG–C) ...............................................................................
Weatherized Non-Condensing Gas Furnace Fan (WG–NC) ................................................................................
Non-Weatherized, Non-Condensing Oil Furnace Fan (NWO–NC) .......................................................................
Non-Weatherized Electric Furnace/Modular Blower Fan (NWEF/NWMB) ...........................................................
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan (MH–NWG–NC) ......................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan (MH–NWG–C) .................................................
Mobile Home Electric Furnace/Modular Blower Fan (MH–EF/MB) ......................................................................
Mobile Home Non-Weatherized Oil Furnace Fan (MH–NWO) .............................................................................
Mobile Home Weatherized Gas Furnace Fan (MH–WG) ** ..................................................................................
FER = 0.044
FER = 0.044
FER = 0.044
FER = 0.071
FER = 0.044
FER = 0.071
FER = 0.071
FER = 0.044
Reserved
Reserved
×
×
×
×
×
×
×
×
QMax
QMax
QMax
QMax
QMax
QMax
QMax
QMax
+
+
+
+
+
+
+
+
182
195
199
382
165
222
240
101
* Furnace fans incorporated into hydronic air handlers, SDHV modular blowers, SDHV electric furnaces, and CAC/HP indoor units are not subject to the standards listed in this table.
** QMax is the airflow, in cfm, at the maximum airflow-control setting measured using the final DOE test procedure at 10 CFR part 430, subpart
B, appendix AA.
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Note: The following will not appear in the
Code of Federal Regulations.
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Federal Register / Vol. 79, No. 128 / Thursday, July 3, 2014 / Rules and Regulations
U.S. DEPARTMENT OF JUSTICE
Antitrust Division
WILLIAM J. BAER
Assistant Attorney General
RFK Main Justice Building
950 Pe.llllS)'lvania Avenue, N.W.
Washington. D.C. 20530-0001
(202)514-2401/ (202)616-2645 (F~)
December 20, 2013
EricJ. Fygi
Deputy General Counsel
Department ofEnergy
Washington, DC 20585
Dear Deputy General Counsel Fygi:
I am responding to your October 23, 2013 letter seeking the views ofthe Attontey
about the potential impact on competition ofproposed energy conservation
standards for products that use electricity for purposes of circulating air through duct
work in residences (also referred to· as "residential furnace fans''). Your request was
submitted undet Section 325(o)(2)(B)(i)(V) of the Energy Policy and Conservation Act,
as amended (ECPA), 42 U.S.C. 6295(o)(2)(B)(i)(V), which requires the Attorney General
to make a detennination of the impact of any lessening of competition that is likely to
result from the imposition ofproposed energy conservation standards. The Attorney
General's responsibility for responding to requests from other departments about the
effect of a program on competition has been delegated to the Assistant Attorney General
for the Antitrust Division in 28 CFR § 0.40(g).
Gener~
In conducting its analysis the Antitrust Division examines whether a proposed
standard may lessen competition, for example, by substantially limiting consumer choice,
by placing certain manufacturers at an unjustified competitive disadvantage, or by
We have reviewed the proposed standards contained in the Notice of Proposed
Ru1emaking (78 Fed. Reg. 207, October 25, 2013) (NOPR). We have also reviewed
supplementary information submitted to the Attorney General by the Department of
Energy, including the technical support document. Based on this review, our conclusion
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inducing avoidable inefficiencies in production or distribution of particular products. A
lessening of competition could result in higher prices to manufacturers and consumers,
and perhaps thwart the intent ofthe revised standards by inducing substitution to less
efficient products.
·
Federal Register / Vol. 79, No. 128 / Thursday, July 3, 2014 / Rules and Regulations
38211
2
is that the proposed energy conservation standards for residential furnace fans are
unlikely to have a significant adverse impact on competition.
[FR Doc. 2014–15387 Filed 7–2–14; 8:45 am]
BILLING CODE 6450–01–P
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Enclosure
Agencies
[Federal Register Volume 79, Number 128 (Thursday, July 3, 2014)]
[Rules and Regulations]
[Pages 38129-38211]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2014-15387]
[[Page 38129]]
Vol. 79
Thursday,
No. 128
July 3, 2014
Part II
Department of Energy
-----------------------------------------------------------------------
10 CFR Parts 429 and 430
Energy Conservation Program for Consumer Products: Energy Conservation
Standards for Residential Furnace Fans; Final Rule
Federal Register / Vol. 79 , No. 128 / Thursday, July 3, 2014 / Rules
and Regulations
[[Page 38130]]
-----------------------------------------------------------------------
DEPARTMENT OF ENERGY
10 CFR Parts 429 and 430
[Docket Number EERE-2010-BT-STD-0011]
RIN 1904-AC22
Energy Conservation Program for Consumer Products: Energy
Conservation Standards for Residential Furnace Fans
AGENCY: Office of Energy Efficiency and Renewable Energy, Department of
Energy.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: Pursuant to the Energy Policy and Conservation Act of 1975
(EPCA), as amended, the U.S. Department of Energy (DOE) must prescribe
energy conservation standards for various consumer products and certain
commercial and industrial equipment, including residential furnace
fans. EPCA requires DOE to determine whether such standards would be
technologically feasible and economically justified, and would save a
significant amount of energy. In this final rule, DOE is adopting new
energy conservation standards for residential furnace fans. DOE has
determined that the prescribed energy conservation standards for these
products would result in significant conservation of energy, and are
technologically feasible and economically justified.
DATES: The effective date of this rule is September 2, 2014. Compliance
with the prescribed standards established for residential furnace fans
in this final rule is required on and after July 3, 2019.
ADDRESSES: The docket for this rulemaking, which includes Federal
Register notices, public meeting attendee lists and transcripts,
comments, and other supporting documents/materials, is available for
review at www.regulations.gov. All documents in the docket are listed
in the www.regulations.gov index. However, not all documents listed in
the index may be publicly available, such as information that is exempt
from public disclosure.
A link to the docket Web page can be found at: https://www1.eere.energy.gov/buildings/appliance_standards/rulemaking.aspx/ruleid/41. The www.regulations.gov Web page contains simple
instructions on how to access all documents, including public comments,
in the docket.
For further information on how to review the docket, contact Ms.
Brenda Edwards at (202) 586-2945 or by email:
Brenda.Edwards@ee.doe.gov.
FOR FURTHER INFORMATION CONTACT:
Mr. Ron Majette, U.S. Department of Energy, Office of Energy Efficiency
and Renewable Energy, Building Technologies Office, EE-5B, 1000
Independence Avenue SW., Washington, DC 20585-0121. Telephone: (202)
586-7935. Email: Ronald.Majette@ee.doe.gov.
Mr. Eric Stas, U.S. Department of Energy, Office of the General
Counsel, GC-71, 1000 Independence Avenue SW., Washington, DC 20585-
0121. Telephone: (202) 586-9507. Email: Eric.Stas@hq.doe.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Summary of the Final Rule
A. Benefits and Costs to Consumers
B. Impact on Manufacturers
C. National Benefits and Costs
D. Conclusion
II. Introduction
A. Authority
B. Background
1. Current Standards
2. History of Standards Rulemaking for Residential Furnace Fans
III. General Discussion
A. Test Procedures
B. Product Classes and Scope of Coverage
C. Technological Feasibility
1. General
2. Maximum Technologically Feasible Levels
D. Energy Savings
1. Determination of Savings
2. Significance of Savings
E. Economic Justification
1. Specific Criteria
a. Economic Impact on Manufacturers and Commercial Customers
b. Savings in Operating Costs Compared To Increase in Price
(Life-Cycle Costs)
c. Energy Savings
d. Lessening of Utility or Performance of Equipment
e. Impact of Any Lessening of Competition
f. Need of the Nation To Conserve Energy
g. Other Factors
2. Rebuttable Presumption
IV. Methodology and Discussion
A. Market and Technology Assessment
1. Definition and Scope of Coverage
2. Product Classes
3. Technology Options
a. Fan Housing and Airflow Path Design Improvements
b. Inverter Controls for PSC Motors
c. High-Efficiency Motors
d. Multi-Stage or Modulating Heating Controls
e. Backward-Inclined Impellers
B. Screening Analysis
1. Screened-Out Technologies
2. Remaining Technologies
a. High-Efficiency Motors
b. Backward-Inclined Impellers
C. Engineering Analysis
1. Efficiency Levels
a. Baseline
b. Percent Reduction in FER
2. Manufacturer Production Cost (MPC)
a. Production Volume Impacts on MPC
b. Inverter-Driven PSC Costs
c. Furnace Fan Motor MPC
d. Motor Control Costs
e. Backward-Inclined Impeller MPC
f. Other Components
D. Markups Analysis
E. Energy Use Analysis
F. Life-Cycle Cost and Payback Period Analysis
1. Installed Cost
2. Operating Costs
3. Furnace Fan Lifetime
4. Discount Rates
5. Compliance Date
6. Base-Case Efficiency Distribution
7. Payback Period
G. Shipments Analysis
H. National Impact Analysis
1. National Energy Savings Analysis
2. Net Present Value Analysis
I. Consumer Subgroup Analysis
J. Manufacturer Impact Analysis
1. Overview
2. Government Regulatory Impact Model
a. Government Regulatory Impact Model Key Inputs
b. Government Regulatory Impact Model Scenarios
3. Discussion of Comments
a. Conversion Costs
b. Cumulative Regulatory Burden
c. Scope of MIA Coverage
d. Markups Analysis
e. Employment Impacts
f. Consumer Utility
g. Small Businesses
K. Emissions Analysis
L. Monetizing Carbon Dioxide and Other Emissions Impacts
1. Social Cost of Carbon
a. Monetizing Carbon Dioxide Emissions
b. Development of Social Cost of Carbon Values
c. Current Approach and Key Assumptions
M. Utility Impact Analysis
N. Employment Impact Analysis
O. Comments on Proposed Standards
V. Analytical Results and Conclusions
A. Trial Standard Levels
B. Economic Justification and Energy Savings
1. Economic Impacts on Consumers
a. Life-Cycle Cost and Payback Period
b. Consumer Subgroup Analysis
c. Rebuttable Presumption Payback
2. Economic Impact on Manufacturers
a. Industry Cash-Flow Analysis Results
b. Impacts on Employment
c. Impacts on Manufacturing Capacity
d. Impacts on Subgroups of Manufacturers
e. Cumulative Regulatory Burden
3. National Impact Analysis
a. Significance of Energy Savings
b. Net Present Value of Consumer Costs and Benefits
c. Indirect Impacts on Employment
4. Impact on Product Utility or Performance
5. Impact of Any Lessening of Competition
6. Need of the Nation To Conserve Energy
7. Other Factors
C. Conclusions
1. Benefits and Burdens of Trial Standard Levels Considered for
Residential Furnace Fans
[[Page 38131]]
2. Summary of Benefits and Costs (Annualized) of Today's
Standards
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Orders 12866 and 13563
B. Review Under the Regulatory Flexibility Act
C. Review Under the Paperwork Reduction Act
D. Review Under the National Environmental Policy Act of 1969
E. Review Under Executive Order 13132
F. Review Under Executive Order 12988
G. Review Under the Unfunded Mandates Reform Act of 1995
H. Review Under the Treasury and General Government
Appropriations Act, 1999
I. Review Under Executive Order 12630
J. Review Under the Treasury and General Government
Appropriations Act, 2001
K. Review Under Executive Order 13211
L. Review Under the Information Quality Bulletin for Peer Review
M. Congressional Notification
VII. Approval of the Office of the Secretary
I. Summary of the Final Rule
Title III, Part B of the Energy Policy and Conservation Act of 1975
(EPCA or the Act), Public Law 94-163 (42 U.S.C. 6291-6309, as
codified), established the Energy Conservation Program for Consumer
Products Other Than Automobiles. Pursuant to EPCA, any new or amended
energy conservation standard that DOE prescribes for certain products,
such as furnace fans, must be designed to achieve the maximum
improvement in energy efficiency that is technologically feasible and
economically justified. (42 U.S.C. 6295(o)(2)(A)). Furthermore, the new
or amended standard must result in a significant conservation of
energy. (42 U.S.C. 6295(o)(3)(B)). In accordance with these and other
statutory provisions discussed in this notice, DOE proposes amended
energy conservation standards for furnace fans. The proposed standards
shall have a fan energy rating (FER) value that meets or is less than
the values shown in Table I.1. These standards would apply to all
products listed in Table I.1 and manufactured in, or imported into, the
United States on or after manufactured on and after July 3, 2019.
Table I.1.--Energy Conservation Standards for Covered Residential Furnace Fans
----------------------------------------------------------------------------------------------------------------
Percent
increase over
Product class FER\*\ (watts/cfm) baseline
(percent)
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace FER = 0.044 x QMax + 182......................... 46
Fan (NWG-NC).
Non-Weatherized, Condensing Gas Furnace Fan FER = 0.044 x QMax + 195......................... 46
(NWG-C).
Weatherized Non-Condensing Gas Furnace Fan FER = 0.044 x QMax + 199......................... 46
(WG-NC).
Non-Weatherized, Non-Condensing Oil Furnace FER = 0.071 x QMax + 382......................... 12
Fan (NWO-NC).
Non-Weatherized Electric Furnace/Modular FER = 0.044 x QMax + 165......................... 46
Blower Fan (NWEF/NWMB).
Mobile Home Non-Weatherized, Non-Condensing FER = 0.071 x QMax + 222......................... 12
Gas Furnace Fan (MH-NWG-NC).
Mobile Home Non-Weatherized, Condensing Gas FER = 0.071 x QMax + 240......................... 12
Furnace Fan (MH-NWG-C).
Mobile Home Electric Furnace/Modular Blower FER = 0.044 x QMax + 101......................... 46
Fan (MH-EF/MB).
Mobile Home Non-Weatherized Oil Furnace Fan Reserved......................................... ..............
(MH-NWO).
Mobile Home Weatherized Gas Furnace Fan (MH- Reserved......................................... ..............
WG).
----------------------------------------------------------------------------------------------------------------
* QMax is the airflow, in cfm, at the maximum airflow-control setting measured using the final DOE test
procedure at 10 CFR part 430, subpart B, appendix AA.
A. Benefits and Costs to Consumers
Table I.2 presents DOE's evaluation of the economic impacts of
today's standards on consumers of residential furnace fans, as measured
by the average life-cycle cost (LCC) savings and the median payback
period (PBP). The average LCC savings are positive for all product
classes.
Table I.2--Impacts of Energy Conservation Standards on Consumers of
Residential Furnace Fans
------------------------------------------------------------------------
Average LCC Median payback
Product class savings period
(2013$) (years)
------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas $506 5.4
Furnace Fan............................
Non-weatherized, Condensing Gas Furnace $341 5.8
Fan....................................
Weatherized Non-Condensing Gas Furnace $447 4.4
Fan....................................
Non-Weatherized, Non-Condensing Oil $46 1.7
Furnace Fan............................
Non-weatherized Electric Furnace/Modular $204 3.2
Blower Fan.............................
Mobile Home Non-Weatherized, Non- $36 2.7
Condensing Gas Furnace Fan.............
Mobile Home Non-Weatherized, Condensing $35 2.3
Gas Furnace Fan........................
Mobile Home Electric Furnace/Modular $85 4.1
Blower Fan.............................
------------------------------------------------------------------------
B. Impact on Manufacturers
The industry net present value (INPV) is the sum of the discounted
cash flows to the industry from the base year through the end of the
analysis period (2014 to 2048). Using a real discount rate of 7.8
percent, DOE estimates that the INPV for manufacturers of residential
furnace fans is $349.6 million.\1\ Under today's standards, DOE expects
that manufacturers may lose up to 16.9 percent of their INPV, which is
approximately $59.0 million. Total conversion costs incurred by
industry prior to the compliance date are expected to reach $40.6
million.
---------------------------------------------------------------------------
\1\ DOE calculated a present value in 2014; all monetary values
in this document are expressed in 2013 dollars unless explicitly
stated otherwise.
---------------------------------------------------------------------------
C. National Benefits and Costs \2\
---------------------------------------------------------------------------
\2\ All monetary values in this section are expressed in 2013$
and are discounted to 2014.
---------------------------------------------------------------------------
DOE's analyses indicate that today's standards would save a
significant amount of energy. The lifetime energy savings for
residential furnace fans purchased in the 30-year period that begins in
the year of compliance with the standards (2019-2048) amount to
[[Page 38132]]
3.99 quadrillion Btu (quads \3\). The estimated annual energy savings
in 2030 (0.07 quads) are equivalent to 0.3 percent of total U.S.
residential energy use in 2012.
---------------------------------------------------------------------------
\3\ A quad is equal to 10\15\ British thermal units (Btu).
---------------------------------------------------------------------------
The cumulative net present value (NPV) of total consumer costs and
savings of today's standards for residential furnace fans ranges from
$10,024 million (at a 7-percent discount rate) to $28,810 million (at a
3-percent discount rate). This NPV expresses the estimated total value
of future operating-cost savings minus the estimated increased product
costs for residential furnace fans purchased in 2019-2048.
In addition, today's standards are expected to have significant
environmental benefits. The energy savings would result in cumulative
emission reductions of approximately 180.6 million metric tons (Mt) \4\
of carbon dioxide (CO2), 695.0 thousand tons of methane
(CH4), 235.7 thousand tons of sulfur dioxide
(SO2), 84.0 thousand tons of nitrogen oxides
(NOX), 6.2 thousand tons of nitrous oxide (N2O),
and 0.4 tons of mercury (Hg).\5\ The cumulative reduction in
CO2 emissions through 2030 amounts to 34 million Mt.
---------------------------------------------------------------------------
\4\ A metric ton is equivalent to 1.1 short tons. Results for
NOX and Hg are presented in short tons.
\5\ DOE calculated emissions reductions relative to the Annual
Energy Outlook 2013 (AEO 2013) Reference case, which generally
represents current legislation and environmental regulations for
which implementing regulations were available as of December 31,
2012.
---------------------------------------------------------------------------
The value of the CO2 reductions is calculated using a
range of values per metric ton of CO2 (otherwise known as
the Social Cost of Carbon, or SCC) developed by a recent Federal
interagency process.\6\ The derivation of the SCC values is discussed
in section IV.L. Using discount rates appropriate for each set of SCC
values, DOE estimates that the net present monetary value of the
CO2 emissions reductions is between 1,134 million to 16,799
million. DOE also estimates that the net present monetary value of the
NOX emissions reductions is $53.1 million at a 7-percent
discount rate, and $110.8 million at a 3-percent discount rate.\7\
---------------------------------------------------------------------------
\6\ Technical Update of the Social Cost of Carbon for Regulatory
Impact Analysis Under Executive Order 12866, Interagency Working
Group on Social Cost of Carbon, United States Government (May 2013;
revised November 2013) (Available at: https://www.whitehouse.gov/sites/default/files/omb/assets/inforeg/technical-update-social-cost-of-carbon-for-regulator-impact-analysis.pdf).
\7\ DOE is investigating valuation of avoided Hg and
SO2 emissions.
---------------------------------------------------------------------------
Table I.3 summarizes the national economic costs and benefits
expected to result from today's standards for residential furnace fans.
Table I.3--Summary of National Economic Benefits and Costs of
Residential Furnace Fans Energy Conservation Standards*
------------------------------------------------------------------------
Present value Discount rate
Category million 2013 $ (percent)
------------------------------------------------------------------------
Benefits
------------------------------------------------------------------------
Consumer Operating Cost Savings........ 13,409 7
34,999 3
CO2 Reduction Monetized Value ($12.0/t 1,134 5
case)**...............................
CO2 Reduction Monetized Value ($40.5/t 5,432 3
case)**...............................
CO2 Reduction Monetized Value ($62.4/t 8,694 2.5
case)**...............................
CO2 Reduction Monetized Value ($119/t 16,799 3
case)**...............................
NOX Reduction Monetized Value (at 53 7
$2,684/ton)**.........................
111 3
Total Benefits[dagger]................. 18,894 7
40,542 3
------------------------------------------------------------------------
Costs
------------------------------------------------------------------------
Consumer Incremental Installed Costs... 3,385 7
6,189 3
------------------------------------------------------------------------
Net Benefits
------------------------------------------------------------------------
Including CO2 and NOX[dagger] Reduction 15,509 7
Monetized Value.......................
34,353 3
------------------------------------------------------------------------
* This table presents the costs and benefits associated with residential
furnace fans shipped in 2019-2048. These results include benefits to
consumers which accrue after 2048 from the products purchased in 2019-
2048. The results account for the incremental variable and fixed costs
incurred by manufacturers due to the standard, some of which may be
incurred in preparation for the rule.
** The CO2 values represent global monetized values of the SCC, in
2013$, in 2015 under several scenarios of the updated SCC values. The
first three cases use the averages of SCC distributions calculated
using 5%, 3%, and 2.5% discount rates, respectively. The fourth case
represents the 95th percentile of the SCC distribution calculated
using a 3% discount rate. The SCC time series used by DOE incorporate
an escalation factor. The value for NOX is the average of the low and
high values used in DOE's analysis.
[dagger] Total Benefits for both the 3% and 7% cases are derived using
the series corresponding to average SCC with 3-percent discount rate.
The benefits and costs of today's standards, for products sold in
2019-2048, can also be expressed in terms of annualized values. The
annualized monetary values are the sum of: (1) The annualized national
economic value of the benefits from operating the product that meets
the new or amended standard (consisting primarily of operating cost
savings from using less energy, minus increases in equipment purchase
and installation costs, which is another way of representing consumer
NPV), and (2) the annualized monetary value of the benefits of emission
reductions, including CO2 emission reductions.\8\
---------------------------------------------------------------------------
\8\ DOE used a two-step calculation process to convert the time-
series of costs and benefits into annualized values. First, DOE
calculated a present value in 2014, the year used for discounting
the NPV of total consumer costs and savings, for the time-series of
costs and benefits using discount rates of three and seven percent
for all costs and benefits except for the value of CO2
reductions. For the latter, DOE used a range of discount rates, as
shown in Table I.4. From the present value, DOE then calculated the
fixed annual payment over a 30-year period (2019 through 2048) that
yields the same present value. The fixed annual payment is the
annualized value. Although DOE calculated annualized values, this
does not imply that the time-series of cost and benefits from which
the annualized values were determined is a steady stream of
payments.
---------------------------------------------------------------------------
[[Page 38133]]
Although adding the value of consumer savings to the values of
emission reductions provides a valuable perspective, two issues should
be considered. First, the national operating cost savings are domestic
U.S. consumer monetary savings that occur as a result of market
transactions, whereas the value of CO2 reductions is based
on a global value. Second, the assessments of operating cost savings
and CO2 savings are performed with different methods that
use different time frames for analysis. The national operating cost
savings is measured for the lifetime of residential furnace fans
shipped in 2019-2048. The SCC values, on the other hand, reflect the
present value of all future climate-related impacts resulting from the
emission of one metric ton of carbon dioxide in each year. These
impacts continue well beyond 2100.
Estimates of annualized benefits and costs of today's standards are
shown in Table I.4. The results under the primary estimate are as
follows. Using a 7-percent discount rate for benefits and costs other
than CO2 reduction (for which DOE used a 3-percent discount
rate along with the SCC series that has a value of $40.5/t in 2015),
the cost of the residential furnace fans standards in today's final
rule is $358 million per year in increased equipment costs, while the
benefits are $1416 million per year in reduced equipment operating
costs, $312 million in CO2 reductions, and $5.61 million in
reduced NOX emissions. In this case, the net benefit amounts
to $1,376 million per year. Using a 3-percent discount rate for all
benefits and costs and the SCC series that has a value of $40.5/t in
2015, the cost of the residential furnace fans standards in today's
rule is $355 million per year in increased equipment costs, while the
benefits are $2010 million per year in reduced operating costs, $312
million in CO2 reductions, and $6.36 million in reduced
NOX emissions. In this case, the net benefit amounts to
$1,973 million per year.
Table I.4--Annualized Benefits and Costs of Standards for Residential Furnace Fans
----------------------------------------------------------------------------------------------------------------
Primary estimate Low net benefits High net benefits
Discount rate * estimate * estimate *
----------------------------------------------------------------------------------------------------------------
million 2013$/year
----------------------------------------------------------------------------------------------------------------
Benefits
----------------------------------------------------------------------------------------------------------------
Consumer Operating Cost Savings. 7%................ 1416.............. 1167.............. 1718
3%................ 2010.............. 1626.............. 2467
CO2 Reduction (at $12.0/t case) 5%................ 90................ 77................ 108
**.
CO2 Reduction (at $40.5/t case) 3%................ 312............... 268............... 377
**.
CO2 Reduction (at $62.4/t case) 2.5%.............. 459............... 393............... 555
**.
CO2 Reduction (at $119/t case) 3%................ 965............... 828............... 1166
**.
NOX Reduction (at $2,684/ton) ** 7%................ 5.61.............. 4.80.............. 6.82
3%................ 6.36.............. 5.35.............. 7.86
Total Benefits [dagger]......... 7% plus CO2 range. 1,512 to 2,387.... 1,249 to 2,000.... 1,833 to 2,891
7%................ 1,734............. 1,439............. 2,102
3% plus CO2 range. 2,106 to 2,981.... 1,708 to 2,459.... 2,583 to 3,641
3%................ 2,328............. 1,899............. 2,852
----------------------------------------------------------------------------------------------------------------
Costs
----------------------------------------------------------------------------------------------------------------
Consumer Incremental Product 7%................ 358............... 314............... 410
Costs. 3%................ 355............... 304............... 419
----------------------------------------------------------------------------------------------------------------
Net Benefits
----------------------------------------------------------------------------------------------------------------
Total [dagger].............. 7% plus CO2 range. 1,154 to 2,029.... 935 to 1,685...... 1,423 to 2,481
7%................ 1,376............. 1,125............. 1,692
3% plus CO2 range. 1,750 to 2,625.... 1,404 to 2,155.... 2,164 to 3,222
3%................ 1,973............. 1,595............. 2,433
----------------------------------------------------------------------------------------------------------------
* This table presents the annualized costs and benefits associated with residential furnace fans shipped in 2019-
2048. These results include benefits to consumers which accrue after 2048 from the products purchased from
2019-2048. The results account for the incremental, variable, and fixed costs incurred by manufacturers due to
the standard, some of which may be incurred in preparation for the rule. The Primary, Low Benefits, and High
Benefits Estimates utilize projections of energy prices and housing starts from the AEO 2013 Reference case,
Low Estimate, and High Estimate, respectively. In addition, incremental product costs reflect a flat rate for
projected product price trends in the Primary Estimate, a slightly increasing rate for projected product price
trends in the Low Benefits Estimate, and a slightly declining rate for projected product price trends in the
High Benefits Estimate. The methods used to derive projected price trends are explained in section IV.F.
** The CO2 values represent global monetized values of the SCC, in 2013$, in 2015 under several scenarios of the
updated SCC values. The first three cases use the averages of SCC distributions calculated using 5%, 3%, and
2.5% discount rates, respectively. The fourth case represents the 95th percentile of the SCC distribution
calculated using a 3% discount rate. The SCC time series used by DOE incorporate an escalation factor. The
value for NOX is the average of the low and high values used in DOE's analysis.
[dagger] Total Benefits for both the 3% and 7% cases are derived using the series corresponding to the average
SCC with a 3% discount rate. In the rows labeled ``7% plus CO2 range'' and ``3% plus CO2 range,'' the
operating cost and NOX benefits are calculated using the labeled discount rate, and those values are added to
the full range of CO2 values.
[[Page 38134]]
D. Conclusion
Based on the analyses culminating in this final rule, DOE found the
benefits to the nation of the standards (energy savings, consumer LCC
savings, positive NPV of consumer benefit, and emission reductions)
outweigh the burdens (loss of INPV and LCC increases for some users of
these products). DOE has concluded that the standards in today's final
rule represent the maximum improvement in energy efficiency that is
technologically feasible and economically justified, and would result
in significant conservation of energy.
II. Introduction
The following section briefly discusses the statutory authority
underlying today's final rule, as well as some of the relevant
historical background related to the establishment of standards for
residential furnace fans.
A. Authority
Title III, Part B \9\ of the Energy Policy and Conservation Act of
1975 (EPCA or the Act), Public Law 94-163 (42 U.S.C. 6291-6309, as
codified) established the Energy Conservation Program for Consumer
Products Other Than Automobiles, a program covering most major
household appliances (collectively referred to as ``covered
products''),\10\ which includes the types of residential furnace fans
that are the subject of this rulemaking. (42 U.S.C. 6295(f)(4)(D))
---------------------------------------------------------------------------
\9\ For editorial reasons, upon codification in the U.S. Code,
Part B was redesignated Part A.
\10\ All references to EPCA in this document refer to the
statute as amended through the American Energy Manufacturing
Technical Corrections Act (AEMTCA), Public Law 112-210 (Dec. 18,
2012).
---------------------------------------------------------------------------
Pursuant to EPCA, DOE's energy conservation program for covered
products consists of essentially of four parts: (1) Testing; (2)
labeling; (3) the establishment of Federal energy conservation
standards; and (4) certification and enforcement procedures. The
Federal Trade Commission (FTC) is primarily responsible for labeling,
and DOE implements the remainder of the program. Subject to certain
criteria and conditions, DOE is required by EPCA to consider and
establish energy conservation standards for ``electricity used for
purposes of circulating air through duct work'' (which DOE has referred
to in shorthand as residential ``furnace fans''). (42 U.S.C.
6295(f)(4)(D)) DOE is also required by EPCA to develop test procedures
to measure the energy efficiency, energy use, or estimated annual
operating cost of each covered product prior to the adoption of an
energy conservation standard. (42 U.S.C. 6295(o)(A)(3) and (r))
Manufacturers of covered products must use the prescribed DOE test
procedure as the basis for certifying to DOE that their products comply
with the applicable energy conservation standards adopted under EPCA
and when making representations to the public regarding the energy use
or efficiency of those products. (42 U.S.C. 6293(c) and 6295(s))
Similarly, DOE must use these test procedures to determine whether the
products comply with standards adopted pursuant to EPCA. (42 U.S.C.
6295(s)) The DOE test procedures for residential furnace fans currently
appear at title 10 of the Code of Federal Regulations (CFR) part 430,
subpart B, appendix AA.
DOE must follow specific statutory criteria for prescribing new or
amended standards for covered products, including furnace fans. As
indicated above, any standard for a covered product must be designed to
achieve the maximum improvement in energy efficiency that is
technologically feasible and economically justified. (42 U.S.C.
6295(o)(2)(A) and (3)(B)) Furthermore, DOE may not adopt any standard
that would not result in the significant conservation of energy. (42
U.S.C. 6295(o)(3)) Moreover, DOE may not prescribe a standard: (1) For
certain products, including residential furnace fans, if no test
procedure has been established for the product, or (2) if DOE
determines by rule that the standard is not technologically feasible or
economically justified. (42 U.S.C. 6295(o)(3)(A)-(B)) In deciding
whether a standard is economically justified, DOE must determine
whether the benefits of the standard exceed its burdens. (42 U.S.C.
6295(o)(2)(B)(i)) DOE must make this determination after receiving
comments on the proposed standard, and by considering, to the greatest
extent practicable, the following seven factors:
(1) The economic impact of the standard on manufacturers and
consumers of the products subject to the standard;
(2) The savings in operating costs throughout the estimated
average life of the covered products in the type (or class) compared
to any increase in the price, initial charges, or maintenance
expenses for the covered products that are likely to result from the
standard;
(3) The total projected amount of energy (or as applicable,
water) savings likely to result directly from the standard;
(4) Any lessening of the utility or the performance of the
covered products likely to result from the standard;
(5) The impact of any lessening of competition, as determined in
writing by the Attorney General, that is likely to result from the
standard;
(6) The need for national energy and water conservation; and
(7) Other factors the Secretary of Energy (Secretary) considers
relevant.
(42 U.S.C. 6295(o)(2)(B)(i)(I)-(VII))
EPCA, as codified, also contains what is known as an ``anti-
backsliding'' provision, which prevents the Secretary from prescribing
any standard that either increases the maximum allowable energy use or
decreases the minimum required energy efficiency of a covered product.
(42 U.S.C. 6295(o)(1)) Also, the Secretary may not prescribe an amended
or new standard if interested persons have established by a
preponderance of the evidence that the standard is likely to result in
the unavailability in the United States of any covered product type (or
class) of performance characteristics (including reliability),
features, sizes, capacities, and volumes that are substantially the
same as those generally available in the United States. (42 U.S.C.
6295(o)(4))
Further, EPCA, as codified, establishes a rebuttable presumption
that a standard is economically justified if the Secretary finds that
the additional cost to the consumer of purchasing a product complying
with an energy conservation standard level will be less than three
times the value of the energy savings during the first year that the
consumer will receive as a result of the standard, as calculated under
the applicable test procedure. (See 42 U.S.C. 6295(o)(2)(B)(iii))
Additionally, under 42 U.S.C. 6295(q)(1), the statute specifies
requirements when promulgating an energy conservation standard for a
covered product that has two or more subcategories. DOE must specify a
different standard level for a type of class of covered product that
has the same function or intended use, if DOE determines that products
within such group: (A) Consume a different kind of energy from that
consumed by other covered products within such type (or class); or (B)
have a capacity or other performance-related feature which other
products within such type (or class) do not have and such feature
justifies a higher or lower standard. (42 U.S.C. 6295(q)(1)) In
determining whether a performance-related feature justifies a different
standard for a group of products, DOE must consider such factors as the
utility to the consumer of such a feature and other factors DOE deems
appropriate. Id. Any rule prescribing such a standard must include an
explanation of the basis on which such higher or lower level was
established. (42 U.S.C. 6295(q)(2))
[[Page 38135]]
Federal energy conservation requirements generally supersede State
laws or regulations concerning energy conservation testing, labeling,
and standards. (42 U.S.C. 6297(a)-(c)) DOE may, however, grant waivers
of Federal preemption for particular State laws or regulations, in
accordance with the procedures and other provisions set forth under 42
U.S.C. 6297(d)).
Finally, pursuant to the amendments contained in the Energy
Independence and Security Act of 2007 (EISA 2007), Public Law 110-140,
any final rule for new or amended energy conservation standards
promulgated after July 1, 2010, is required to address standby mode and
off mode energy use. (42 U.S.C. 6295(gg)(3)) Specifically, when DOE
adopts a standard for a covered product after that date, it must, if
justified by the criteria for adoption of standards under EPCA (42
U.S.C. 6295(o)), incorporate standby mode and off mode energy use into
a single standard, or, if that is not feasible, adopt a separate
standard for such energy use for that product. (42 U.S.C.
6295(gg)(3)(A)-(B)) The furnace fan energy rating metric does not
account for the electrical energy consumption in standby mode and off
mode, because energy consumption in those modes is being fully
accounted for in the DOE energy conservation standards for residential
furnaces and residential central air conditioners (CAC) and heat pumps
(HP). Manufacturers will be required to use the new metrics and methods
adopted in those rulemakings for the purposes of certifying to DOE that
their products comply with the applicable energy conservation standards
adopted pursuant to EPCA and for making representations about the
efficiency of those products. (42 U.S.C. 6293(c); 42 U.S.C. 6295(s))
B. Background
1. Current Standards
Currently, no Federal energy conservation standards apply to
residential furnace fans.
2. History of Standards Rulemaking for Residential Furnace Fans
Pursuant to 42 U.S.C. 6295(f)(4)(D), DOE must consider and
prescribe new energy conservation standards or energy use standards for
electricity used for purposes of circulating air through duct work. DOE
has interpreted this statutory language to allow regulation of the
electricity use of any electrically-powered device applied to
residential central heating, ventilation, and air-conditioning (HVAC)
systems for the purpose of circulating air through duct work.
DOE initiated the current rulemaking by issuing an analytical
Framework Document, ``Rulemaking Framework for Furnace Fans'' (June 1,
2010). DOE then published the Notice of Public Meeting and Availability
of the Framework Document for furnace fans in the Federal Register on
June 3, 2010. 75 FR 31323. See https://www1.eere.energy.gov/buildings/appliance_standards/rulemaking.aspx/ruleid/41. The Framework Document
explained the issues, analyses, and process that DOE anticipated using
to develop energy conservation standards for residential furnace fans.
DOE held a public meeting on June 18, 2010 to solicit comments from
interested parties regarding DOE's analytical approach. DOE originally
scheduled the comment period on the Framework Document to close on July
6, 2010, but due to the large number and broad scope of questions and
issues raised, DOE subsequently published a notice in the Federal
Register reopening the comment period from July 15, 2010 until July 27,
2010, to allow additional time for interested parties to submit
comments. 75 FR 41102 (July 15, 2010).
As a concurrent effort to the residential furnace fan energy
conservation standard rulemaking, DOE also initiated a test procedure
rulemaking for residential furnace fans. On May 15, 2012, DOE published
a notice of proposed rulemaking (NOPR) for the test procedure in the
Federal Register. 77 FR 28674. In that NOPR, DOE proposed to establish
methods to measure the performance of covered furnace fans and to
obtain a value for the proposed metric, referred to as the ``fan
efficiency rating'' (FER).\11\ DOE held the test procedure NOPR public
meeting on June 15, 2012, and the comment period closed on July 30,
2012. After receiving comments on the NOPR alleging significant
manufacturer burden associated with the proposed test procedure, DOE
determined that an alternative test method should be developed. DOE
published in the Federal Register an SNOPR on April 2, 2013, which
contained its revised test procedure proposal and an explanation of the
changes intended to reduce burden. 78 FR 19606. DOE proposed to adopt a
modified version of the alternative test method recommended by the Air-
Conditioning, Heating, and Refrigeration Institute (AHRI) and other
furnace fan manufacturers to rate the electrical energy consumption of
furnace fans. DOE concluded that the AHRI-proposed method provides a
framework for accurate and repeatable determinations of FER that is
comparable to the test method previously proposed by DOE, but at a
significantly reduced test burden. DOE published in the Federal
Register a final rule on January 3, 2014, which contained the final
test procedure for residential furnace fans. 79 FR 500.
---------------------------------------------------------------------------
\11\ In the May 15, 2012 NOPR for the test procedure, DOE
referred to FER as ``fan efficiency rating.'' However, in the April
2, 2013 test procedure SNOPR, DOE proposed to rename the metric as
``fan energy rating,'' thereby keeping the same abbreviation (FER).
---------------------------------------------------------------------------
To further develop the energy conservation standards for
residential furnace fans, DOE gathered additional information and
performed a preliminary technical analysis. This process culminated in
publication in the Federal Register of a Notice of Public Meeting and
the Availability of the Preliminary Technical Support Document (TSD) on
July 10, 2012. 77 FR 40530. DOE published a NOPR in the Federal
Register and made available an accompanying NOPR TSD on October 25,
2013. 78 FR 64068. In that document, DOE requested comment on the
following matters discussed in the TSD: (1) Additional FER values; (2)
the methodology for accounting for the relationship between FER and
airflow capacity; (3) the reasonableness of the values that DOE used to
characterize the rebound effect with high-efficiency residential
furnace fans; (4) DOE's estimate of the base-case efficiency
distribution of residential furnace fans in 2018; (5) the long-term
market penetration of higher-efficiency residential furnace fans; (6)
data regarding manufacturer product costs for furnace fan equipment and
components; (7) the effect of standards on future furnace fan equipment
shipments; (8) whether there are features or attributes of the more
energy-efficient furnace fans that manufacturers would produce to meet
the standards in the proposed rule that might affect how they would be
used by consumers; (9) data that would refine the analytical timeline;
(10) input on average equipment lifetimes; (11) the new SCC values used
to determine the social benefits of CO2 emissions reductions
over the rulemaking analysis period; and (12) input on the cumulative
regulatory burden. Id. DOE also invited written comments on these
subjects, as well as any other relevant issues. A PDF copy of the NOPR
TSD is available at https://www.regulations.gov/#!documentDetail;D=EERE-
2010-BT-STD-0011-0068.
The NOPR TSD provided an overview of the activities DOE undertook
in developing proposed energy
[[Page 38136]]
conservation standards for residential furnace fans, and discussed the
comments DOE received in response to the Preliminary Analysis. It also
described the analytical methodology that DOE used and each analysis
DOE had performed up to that point. These analyses were as follows:
A market and technology assessment addressed the scope of
this rulemaking, identified the potential product classes of
residential furnace fans, characterized the markets for these products,
and reviewed techniques and approaches for improving their efficiency;
A screening analysis reviewed technology options to
improve the efficiency of furnace fans, and weighed these options
against DOE's four prescribed screening criteria;
An engineering analysis developed relationships that show
the manufacturer's cost of achieving increased efficiency;
A markups analysis developed distribution channel markups
that relate the manufacturer production cost (MPC) to the cost to the
consumer;
An energy use analysis estimated the annual energy use of
furnace fans at various potential standard levels;
A life-cycle cost (LCC) analysis calculated, at the
consumer level, the discounted savings in operating costs throughout
the estimated average life of the product, compared to any increase in
installed costs likely to result directly from the adoption of a given
standard;
A payback period (PBP) analysis estimated the amount of
time it would take consumers to recover the higher expense of
purchasing more-energy-efficient products through lower operating
costs;
A shipments analysis estimated shipments of residential
furnace fans over the time period examined in the analysis (30 years),
which were used in performing the national impact analysis;
A national impact analysis assessed the aggregate impacts
at the national level of potential energy conservation standards for
residential furnace fans, as measured by the net present value of total
consumer economic impacts and national energy savings;
A manufacturer impact analysis estimated the financial
impact of new energy conservation standards on manufacturers and
calculated impacts on competition, employment, and manufacturing
capacity;
A consumer subgroup analysis evaluated variations in
customer characteristics that might cause a standard to affect
particular consumer sub-populations (such as low-income households)
differently than the overall population;
An emissions analysis assessed the effects of the
considered standards on emissions of carbon dioxide (CO2),
sulfur dioxide (SO2) nitrogen oxides (NOX),
mercury (Hg), nitrous oxide (N20), and methane
(CH4);
An emissions monetization estimated the economic value of
reductions in CO2 and NOX emissions from the
considered standards;
A utility impact analysis estimated selected effects of
the considered standards on electric utilities;
An employment impact analysis assessed the impacts of the
considered standards on national employment; and
A regulatory impact analysis (RIA) evaluated alternatives
to amended energy conservation standards in order to assess whether
such alternatives could achieve substantially the same regulatory goal
at a lower cost.
The NOPR public meeting took place on December 3, 2013. At this
meeting, DOE presented the methodologies and results of the analyses
set forth in the NOPR TSD. The numerous comments received since
publication of the October 2013 NOPR, including those received at the
NOPR public meeting, have contributed to DOE's resolution of the issues
raised by interested parties.
The submitted comments include a comment from the American Council
for an Energy-Efficiency Economy (ACEEE); a joint comment from the
American Fuel and Petrochemical Manufacturers (AFPM), the U.S. Chamber
of Commerce (the Chamber), the Council of Industrial Boiler Owners
(CIBO), the American Forest and Paper Association (AF&PA), and the
American Petroleum Institute (API); a comment from the American Gas
Association (AGA); a comment from the Air-Conditioning, Heating, and
Refrigeration Institute (AHRI); a comment from the American Public Gas
Association (APGA); a joint comment from the Appliance Standards
Awareness Project (ASAP), Alliance to Save Energy (ASE), National
Consumer Law Center (NCLC) and the Natural Resources Defense Council
(NRDC); a second joint comment from California Investor-Owned Utilities
(CA IOUs) including Pacific Gas and Electric Company (PG&E), Southern
California Edison (SCE), Southern California Gas Company (SCGC), and
San Diego Gas and Electric (SDGE); a comment from the Cato Institute; a
comment from China WTO (WTO); a comment from Earthjustice; a comment
from Edison Electric Institute (EEI); a comment from the George
Washington University Regulatory Studies Center; a comment from Goodman
Global, Inc. (Goodman); a comment from Heating, Air-Conditioning and
Refrigeration Distributers International (HARDI); a comment from
Johnson Controls; a comment from Laclede Gas Company (Laclede); a
comment from a comment from Lennox International, Inc. (Lennox); a
comment from the Mercatus Center at George Mason University; a comment
from Morrison Products, Inc. (Morrison); a comment from Mortex Product,
Inc. (Mortex); a comment from the National Association of Manufacturers
(NAM); a joint comment from the Northwest Energy Efficiency Alliance
(NEEA) and the Northwest Power and Conservation Council (NPCC); a
comment from the Northeast Energy Efficiency Partnerships (NEEP); a
comment from Rheem Manufacturing Company (Rheem); a comment from
Southern Company; a comment from Ingersoll Rand; and a comment from
Unico, Incorporated. Comments made during the public meeting by those
not already listed include Nidec Motor Corporation (Nidec) and the
motor manufacturer Regal Beloit. This final rule summarizes and
responds to the issues raised in these comments. A parenthetical
reference at the end of a quotation or paraphrase provides the location
of the item in the public record.
III. General Discussion
A. Test Procedures
DOE published the furnace fan test procedure final rule in the
Federal Register on January 3, 2014. 79 FR 499. DOE's test procedure
for furnace fans (hereinafter referred to as ``the test procedure'') is
codified in appendix AA of subpart B of part 430 of the code of federal
regulations (CFR).The test procedure is applicable to circulation fans
used in weatherized and non-weatherized gas furnaces, oil furnaces,
electric furnaces, and modular blowers. The test procedure is not
applicable to any non-ducted products, such as whole-house ventilation
systems without ductwork, central air-conditioning (CAC) condensing
unit fans, room fans, and furnace draft inducer fans.
DOE aligned the test procedure with the DOE test procedure for
furnaces by incorporating by reference specific provisions from an
industry standard that is also incorporated by reference in the DOE
test procedure for furnaces. DOE's test procedure for furnaces is
codified in appendix N of subpart B of part 430 of the CFR. The DOE
furnace test procedure incorporates by reference American National
Standards Institute (ANSI)/American Society of Heating, Refrigerating
and Air Conditioning
[[Page 38137]]
Engineers (ASHRAE) 103-1993, Method of Testing for Annual Fuel
Utilization Efficiency of Residential Central Furnaces and Boilers
(ASHRAE 103-1993). The DOE furnace fan test procedure incorporates by
reference the definitions, test setup and equipment, and procedures for
measuring steady-state combustion efficiency provisions of the 2007
version of ASHRAE 103 (ASHRAE 103-2007). In addition to these
provisions, the test procedure includes provisions for apparatuses and
procedures for measuring temperature rise, external static pressure,
and furnace fan electrical input power. The test procedure also
incorporates by reference provisions for measuring temperature and
external static pressure from ANSI/ASHRAE 37-2009, Methods of Testing
for Rating Electrically Driven Unitary Air-Conditioning and Heat Pump
Equipment (ASHRAE 37-2009). There are no differences between the 2005
version (which is already incorporated by reference in the CFR) and the
2009 version of the ASHRAE 37 provisions incorporated by reference for
the furnace fan test procedure. The test procedure also establishes
calculations to derive the rating metric, fan energy rating (FER), for
each furnace fan basic model based on the results of testing per the
test method for furnace fans codified in appendix AA of subpart B of
part 430 of the CFR.
FER is the estimated annual electrical energy consumption of a
furnace fan normalized by: (a) The estimated total number of annual fan
operating hours (1,870); and (b) the airflow in the maximum airflow-
control setting. For the purposes of the furnace fan test procedure,
the estimated annual electrical energy consumption is the sum of the
furnace fan electrical input power (in Watts), measured separately for
multiple airflow-control settings at different external static
pressures (ESPs), multiplied by national average operating hours
associated with each setting. These ESPs are determined by a reference
system, based on operation at maximum airflow that represents national
average ductwork system characteristics. Table III.1 includes the
reference system ESP values by installation type that are specified by
the test procedure. In previous rulemaking documents for the furnace
fan test procedure and energy conservation standard rulemaking, DOE
used the term ``manufactured home furnace'' to be synonymous with
``mobile home furnace,'' as defined in the Code of Federal Regulation
(CFR). 10 CFR 430.2. DOE will use the term ``mobile home'' hereinafter
to be consistent with the CFR definition for ``mobile home furnace.''
All provisions and statements regarding mobile homes and mobile home
furnaces are applicable to manufactured homes and manufactured home
furnaces.
Table III.1--Required Reference System Criteria (i.e., ESP at Maximum
Airflow) by Furnace Fan Installation Type
------------------------------------------------------------------------
ESP at maximum
Installation type airflow (in.
wc)
------------------------------------------------------------------------
Units with an internal evaporator coil.................. 0.50
Units designed to be paired with an evaporator coil..... 0.65
Units designed to be installed in a mobile home \12\.... 0.30
------------------------------------------------------------------------
The test procedure requires measurements for the airflow-control
settings that correspond to fan operation while performing the cooling
function (which DOE finds is predominantly associated with the maximum
airflow-control setting), heating function, and constant-circulation
function. Table III.2 describes the required airflow-control settings
by product type.
---------------------------------------------------------------------------
\12\ Mobile home external static pressure is much lower because
there is no return air ductwork in mobile homes. Also, the United
States Department of Housing and Urban Development (HUD)
requirements for mobile homes stipulate that the ductwork for
cooling should be designed for 0.3 in. water column (wc). 24 CFR
3280.715.
Table III.2--Airflow-Control Settings at Which Measurements Are Required for Each Product Type
----------------------------------------------------------------------------------------------------------------
Airflow-control Airflow-control
Product type setting 1 setting 2 Airflow-control setting 3
----------------------------------------------------------------------------------------------------------------
Single-stage Heating.............. Default constant- Default heat......... Absolute maximum.*
circulation.
Multi-stage or Modulating Heating. Default constant- Default low heat..... Absolute maximum.
circulation.
----------------------------------------------------------------------------------------------------------------
* For the purposes of the test procedure, ``absolute maximum'' airflow-control setting refers to the airflow-
control setting that achieves the maximum attainable airflow at the operating conditions specified by the test
procedure.
As shown in Table III.2, for products with single-stage heating, the
three airflow-control settings to be tested are: The default constant-
circulation setting; the default heating setting; and the absolute
maximum setting. For products with multi-stage heating or modulating
heating, the airflow-control settings to be tested are: The default
constant-circulation setting; the default low heating setting; and the
absolute maximum setting. The absolute lowest airflow-control setting
is used to represent constant circulation if a default constant-
circulation setting is not specified. DOE defines ``default airflow-
control settings'' as the airflow-control settings for installed use
specified by the manufacturer in the product literature shipped with
the product in which the furnace fan is integrated. See Section 2.2 of
Appendix AA to Subpart B of 10 CFR part 430. Manufacturers typically
provide detailed instructions for setting the default heating airflow-
control setting to ensure that the product in which the furnace fan is
integrated operates safely. In instances where a manufacturer specifies
multiple airflow-control settings for a given function to account for
varying installation scenarios, the highest airflow-control setting
specified for the given function shall be used for the DOE test
procedure. High heat and reduced heat shall be considered different
functions for multi-stage heating units. Manufacturer installation
guides also provide detailed instructions regarding compatible
thermostats and how to wire them to achieve the specified default
settings.
The Watt measurements for calculating FER are weighted using
designated annual operating hours for each function (i.e., cooling,
heating, and constant circulation) that represent national average
operation. Table III.3 shows the estimated national average operating
hours for each function.
[[Page 38138]]
Table III.3--Estimated National Average Operating Hour Values for Calculating FER
----------------------------------------------------------------------------------------------------------------
Multi-stage or
Operating mode Variable Single-stage modulating
(hours) (hours)
----------------------------------------------------------------------------------------------------------------
Heating......................................................... HH 830 830/HCR
Cooling......................................................... CH 640 640
Constant Circulation............................................ CCH 400 400
----------------------------------------------------------------------------------------------------------------
For multi-stage heating or modulating heating products, the
specified operating hours for the heating mode are divided by the
heating capacity ratio (HCR) to account for variation in time spent in
this mode associated with turndown of heating output. The HCR is the
ratio of the measured reduced heat input rate to the measured maximum
heat input rate.
The FER equation is:
[GRAPHIC] [TIFF OMITTED] TR03JY14.000
Where:
CH = annual furnace fan cooling operating hours;
EMax = furnace fan electrical consumption at maximum
airflow-control setting operating point;
HH = annual furnace fan heating operating hours;
EHeat = furnace fan electrical consumption at the default
heating airflow-control setting operating point for units with
single-stage heating or the default low-heating airflow control
setting operating point for units with multi-stage heating;
CHH = annual furnace fan constant circulation hours;
ECirc = furnace fan electrical consumption at the default
constant-circulation airflow-control setting operating point (or
minimum airflow-control setting operating point if a default
constant-circulation airflow-control setting is not specified);
QMax = airflow at maximum airflow-control setting
operating point; and
1000 = constant to put metric in terms of watts/1000cfm, which is
consistent with industry practice.
DOE received comments from interested parties regarding the furnace
fan test procedure in response to the furnace fan energy conservation
standard (ECS) NOPR. Interested parties' comments on the test procedure
are summarized below. DOE addressed many of these issues in the test
procedure final rule, published in the Federal Register on January 3,
2014. (79 FR 514). The publication of the test procedure final rule
occurred after the standards NOPR public meeting, held on December 3,
2013, but before the close of the standards NOPR comment period on
January 23, 2014. For comments that were addressed in the test
procedure final rule, a reference to the applicable discussion
contained in the test procedure final rule document is provided. DOE's
detailed response is provided in this document for comments that were
not addressed in the test procedure final rule document.
AHRI, Goodman, Morrison, Rheem, Southern Company, Johnson Controls,
and Ingersoll Rand commented that DOE's schedule for finalizing the
test procedure did not provide interested parties with sufficient time
to evaluate product performance in accordance with the final test
procedure in order to develop and submit substantive comments on the
standards proposed in the NOPR. (AHRI, No. 98 at p. 2, 3; Goodman, No.
102 at pp. 7, 8; Morrison, No. 108 at p. 3; Rheem, No. 83 at p. 1;
Southern Company, No. 85 at p. 2; Johnson Controls, No. 95 at p. 3;
Ingersoll Rand, No. 43 at p. 33) Ingersoll Rand added that the comments
they have submitted to date are based on the proposed test procedure,
not the final test procedure. (Ingersoll Rand, No. 107 at pp. 2, 10)
AGA and Allied Air agree and recommend that DOE delay promulgation of
standards to give interested parties and DOE more time to conduct
analyses using the final test procedure. (AGA, No. 110 at pp. 3, 4;
Allied Air, Public Meeting Transcript, No. 43 at p. 48) Goodman
recommended a delay of three months for this type of product and
testing. (Goodman, No. 102 at p. 3) Prior to publication of the test
procedure final rule, EEI expressed support for DOE issuing a
supplemental notice of proposed rulemaking (SNOPR) for the standard if
changes were made to the test procedure final rule that had significant
impacts on DOE's analyses results. (EEI, No. 87 at p. 3) APGA and
Southern Company also recommended that DOE publish a standards SNOPR.
(APGA, No. 90 at p. 2; Southern Company, No. 43 at p. 37)
DOE recognizes that interested parties need sufficient time to
collect and evaluate relevant fan performance data in order to submit
meaningful comments on the proposed energy conservation standard for
furnace fans. Thus, on December 24, 2013, DOE posted a pre-publication
test procedure final rule notice to regulations.gov and issued a 30-day
extension of the standards NOPR comment period to provide interested
parties with time to evaluate DOE's proposed standards using the final
test procedure.
AHRI, Johnson Controls, and Morrison stated that, even with the
comment period extension, the 20 days between the publication of the
test procedure final rule on January 3, 2014 and the close of the
standards NOPR comment period on January 23, 2014 did not provide
interested parties with sufficient time to assess the energy
conservation standards NOPR based on the provisions within the final
test procedure. AHRI added that DOE was obligated to issue the NOPR on
the proposed energy conservation standards after the issuance of the
final rule on the furnace fan test procedures per Section 7(c) of
Appendix A to Subpart C of 10 CFR part 430. (AHRI, No. 98 at pp. 2, 3;
Johnson Controls, No. 95 at p. 3; Morrison, No. 108 at p. 3) Mortex
stated that they were not able to test any of their products according
to the final test procedure by the time the energy conservation
standard NOPR comment period closed. (Mortex, No. 104 at p. 2)
Ingersoll Rand commented that DOE's standards NOPR analyses are invalid
because they were not based on the test procedure final rule.
(Ingersoll Rand, No. 107 at p. 2, 10). NEEA and NPCC provided there is
a need for product testing using the final test procedure, and a re-
assessment of the derivation of the proposed FER equations and standard
levels. NEEA and NPCC added that they do not support a decision on
[[Page 38139]]
standards before there is sufficient data with which to verify that the
proposed FER values will not disqualify from compliance the majority of
the very products upon which they are founded, and for which DOE's
economic analyses are valid. (NEEA and NPCC, No. 96 at p. 2)
DOE disagrees with AHRI and Morrison that the extended comment
period was insufficient. DOE issued a test procedure SNOPR for furnace
fans on April 2, 2013. 78 FR 19606. DOE did not make changes to the
test procedure between the SNOPR and final rule that would
significantly alter FER values for most products. Interested parties
that conducted testing in accordance with the test procedure SNOPR
proposal should not have to retest most furnace models to derive an FER
value that is consistent with the final test procedure. For most
furnaces, the FER value should not change or the FER value can be
recalculated per the final test procedure requirements using the raw
data measured according to the SNOPR test method. Therefore,
notwithstanding the 20 days between the test procedure final rule and
the close of the standards NOPR comment period, interested parties
still had over nine months between the publication of the test
procedure SNOPR and the close of the standards NOPR comment period to
collect and evaluate fan performance data that is relevant to DOE's
proposed standards. DOE received data that could be used to derive FER
values that meet the final test procedure requirements from multiple
manufacturers during this period.
DOE agrees with NEEA and NPCC that its proposed standards should be
assessed based on FER values that are reflective of performance as
measured by the final test procedure. For the reasons stated above, DOE
was able to use much of the FER data it has collected in previous
phases of this rulemaking to generate FER values that meet the
requirements of the final test procedure. DOE also conducted testing
prior to and during the development of the test procedure final rule
that generated a broad set of results to enable DOE to derive FER
values that are consistent with the requirements of the final test
procedure. In addition, DOE continued to collect and use data from
publicly-available product literature. DOE relied on the mathematical
methods outlined in the test procedure NOPR for using this data to
model fan performance and estimate FER values that meet the final test
procedure requirements. 77 FR 28690 (May 15, 2012). DOE recognizes that
this method is not identical to the final test procedure method.
However, DOE believes the FER values generated in this manner are still
relevant because the final test method is similar to the test method
proposed by AHRI (with support from Goodman, Ingersoll Rand, Lennox,
and Morrison) in response to the test procedure NOPR, which they argued
would result in accurate and repeatable FER values that are comparable
to the FER values resulting from the methods proposed in the NOPR.
(AHRI, No. 16 at p. 3; Goodman, No. 17 at p. 4; Ingersoll Rand, No. 14
at p. 1; Morrison, No. 21 at p. 3.) For these reasons, Ingersoll Rand's
comment stating that DOE's standards NOPR analyses are invalid because
they are not based on the test procedure final rule is inaccurate. The
standards proposed in the NOPR and those established by this final rule
are based on relevant FER data.
Goodman stated that DOE's modifications to the test procedure since
the April 2013 test procedure SNOPR will have a significant impact on
FER. Goodman referred specifically to the modification in the test
procedure that specifies that airflow be calculated based on firing the
product in the absolute maximum airflow-control setting if that setting
is a default heating setting. According to Goodman, most furnaces allow
heating operation at the highest airflow setting. Thus, instead of
heating airflow setting being a mid-range temperature rise as typically
set by factory default, it will now be a low-range temperature rise at
a much higher and less efficient setting for FER calculation (and a
setting that will not be typical of a field installation). (Goodman,
No. 102 at p. 7) Ingersoll Rand echoed Goodman's statement, adding that
the modification would also result in higher watts in heating mode and
a higher FER value than would have resulted using the procedure in the
SNOPR for a majority of furnaces. (Ingersoll Rand, No. 107 at pp. 2,
10).
DOE disagrees with Goodman's and Ingersoll Rand's comments. DOE
expects that both interested parties have misinterpreted the test
procedure requirement. DOE recognizes that product controls can be
altered from factory settings to allow heating in the absolute maximum
airflow-control setting. The test procedure does not allow for this
practice. The test procedure only requires testing in factory-set
configurations. Specific to the modification in question, the test
procedure requires heating in the absolute maximum airflow-control
setting only if that setting is a default heat setting. See Section
8.6.1.2 of Appendix AA to Subpart B of 10 CFR part 430. By definition,
as outlined in the test procedure, a default heating airflow-control
setting is factory-set and specified for installed-use as a heat
setting by the manufacturer. See Section 2.2 of Appendix AA to Subpart
B of 10 CFR part 430. Consequently, the resulting temperature rise is
also factory-set by the manufacturer, and the measured performance will
be representative of field use. In addition, the test procedure SNOPR
and final rule requirements for EHeat (the watts in heating
mode input for FER) are consistent and the measured values for this
input should not change. The impacts of the modification in question
are explained in more detail in the test procedure final rule. 79 FR
514 (January 3, 2014).
AHRI commented that in the final test procedure that was published
on January 3, 2014, DOE introduced a change within the test procedure
that increases the measured FER. AHRI stated that DOE decided not to
implement AHRI's recommendation that a furnace be fired at the maximum
airflow rate to calculate the maximum airflow. Instead, according to
AHRI, the final rule specifies that the maximum airflow is determined
by applying the airflow equation for a heating setting and adjusting to
the maximum setting based on pressure measurements. AHRI claims that
this approach results in an increase of the measured FER and was not
accounted within the analyses associated with the energy conservation
standards NOPR TSD that was issued on October 25, 2013. AHRI recommends
that DOE reevaluate the analyses within the entire TSD due to this
single change. (AHRI, No. 98 at p. 3, 4)
DOE introduced the change referred to by AHRI in the April 2, 2013
test procedure SNOPR. A detailed discussion of DOE's reasoning for that
change are provided in that notice. 78 FR 19616. DOE made additional
changes to this provision in the test procedure final rule by requiring
that the product under test be fired at the maximum airflow rate to
calculate the maximum airflow for furnaces for which the maximum
airflow-control setting is a default heat setting (consistent with
AHRI's recommendation). See Section 8.6.1.2 of Appendix AA to Subpart B
of 10 CFR part 430. DOE disagrees with AHRI that the change in question
will result in higher FER values. DOE fan performance tests, including
tests following the final test procedure, show that the maximum airflow
calculated when firing the product under test in the maximum airflow
control setting is typically lower than when applying the airflow
equation for a heating setting
[[Page 38140]]
and adjusting to the maximum setting based on pressure measurements.
Consequently, FER values would be lower if they were derived using
airflow values calculated when firing in the maximum airflow-control
setting. AHRI did not provide data to the contrary. As stated above,
DOE's proposed standards and the standards established by this document
are valid because they are based on FER values that are consistent with
the final test procedure (to include FER values employing the airflow
adjustment method in question).
AHRI, Morrison, and Ingersoll Rand commented that they are opposed
to DOE eliminating the HCR from the denominator of the FER equation.
According to AHRI, DOE did not provide a sound technical justification
for such a modification and unnecessarily penalized the FER values
associated with multi-stage and modulating units. (AHRI, No. 98 at p.
2, 3; Morrison, No. 108 at p. 3, 4; Ingersoll Rand, No. 107 at p. 2,
10)
As discussed in the test procedure final rule, DOE found that
including HCR in the denominator of the FER equation resulted in
percent reductions in estimated annual energy consumption, as
calculated for FER, of 15 percent. 79 FR 515 (January 3, 2014).
Further, DOE found percent reductions in FER of approximately 30
percent when comparing single-stage products using constant-torque
brushless permanent magnet (BPM) motors to multi-stage products using
constant-torque BPM motors. DOE eliminated HCR from the FER equation
because, as a result, percent reductions in FER dropped to 15 percent
on average, which is consistent with percent reduction in estimated
annual energy consumption. 79 FR 515 (January 3, 2014). DOE did not
receive any new FER values for products that use a constant-torque BPM
motor and multi-stage heating. DOE was also unable to find data in the
public domain with which to calculate new FER values to represent such
products. In the absence of new data, DOE used the raw airflow, ESP,
and fan electrical energy consumption data for single-stage furnaces
with constant-torque BPM motors to generate FER values reflecting the
addition of theoretical multi-stage heating capabilities. Single-stage
furnaces using constant-torque BPM motors typically have additional
airflow-control settings that provide less airflow than the factory-set
heating airflow-control setting. Theoretically, these airflow-control
settings could be used for a low heat setting in a multi-stage heating
configuration. DOE identified as many models as possible that meet this
criterion and for which DOE has sufficient data to calculate
theoretical FER values for a multi-stage configuration. For each model,
DOE first calculated the temperature rise in the default heating
setting based on the airflow, thermal efficiency and input heat rating
in that setting. Next, DOE used a variation of the same relationship
between these parameters to calculate the theoretical low input
capacity that would achieve the same temperature rise for each
available airflow-control setting below the heat setting. DOE then
evaluated the HCR for each of the lower airflow-control settings based
on the theoretical input capacity of the lower setting and the rated
input capacity of the default heat setting. DOE selected the low
airflow-control setting that produced an HCR between 0.4 and 0.9 that
was closest to 0.7 to represent the theoretical low heating setting.
DOE chose these criteria based on investigation of typical HCR values
observed in currently available products. Finally, DOE calculated
estimated annual energy consumption and an FER value using the single-
stage model's data for the absolute maximum and constant circulation
airflow-control settings and the data for the theoretical low heating
setting for the heating airflow-control setting. DOE's new data shows
that multi-staging reduces estimated annual energy consumption by an
average of 14 percent and FER by an average of 12 percent. These
findings are consistent with DOE's previous findings and support its
decision to eliminate HCR from the denominator of the FER calculation.
Ingersoll Rand stated that the final test procedure reduces the
estimated savings associated with BPM motors. Ingersoll Rand commented
that BPM motors consume more power as static pressure increases than
permanent-split capacitor (PSC) motors. (Ingersoll Rand, No. 107 at p.
2, 10)
DOE addressed this issue in the energy conservation standards NOPR.
78 FR 64084 (October 25, 2013). While BPM motors consume more power as
static pressure increases, they also provide more airflow. FER is
normalized by airflow to account for this difference in behavior
between BPM and PSC motors. In addition, the standards established in
this document are a function of airflow. BPM motor-driven fan
performance is evaluated relative to PSC motor-driven fans that provide
the same amount of airflow at the same reference system static pressure
as a result. Interested parties did not provide any evidence that these
methods are inappropriate for evaluating relative fan performance.
China WTO commented that FER includes factors, such as HCR, to
account for multi-stage heating but does not include analogous factors
for multi-stage cooling. (China WTO, No. 92 at p. 1)
DOE considered accounting for fan performance during multi-stage
cooling operation for the test procedure NOPR. 77 FR 28680. DOE did not
include factors for multi-stage cooling in the final test procedure
because the presence and capacity of low-stage cooling is dependent on
the cooling system with which a product containing a furnace fan is
paired. DOE found in its review of publicly-available product
literature that detailed characteristics of the cooling system are not
typically provided. Consequently, entities performing the DOE furnace
fan test procedure cannot identify the airflow-control setting that
would be designated for low-stage cooling operation. In addition,
multi-stage heating is not necessarily associated with multi-stage
cooling capability (e.g., multi-stage cooling equipment is much less
common than multi-stage heating equipment).
China WTO stated that the final test procedure does not provide a
method for calculating the maximum airflow when the maximum airflow-
control setting is only designated for cooling. (China WTO, No. 92 at
p. 1)
The method for calculating the maximum airflow when the maximum
airflow-control setting is only designated for cooling is provided in
the final rule and in Section 9 of appendix AA of subpart B of part 430
of the CFR. 79 FR 524 (January 3, 2014).
The California Investor Owned Utilities (CA IOU) commented that
they observed a potential error in the calculation of airflow in the
final test procedure. Specifically, CA IOU recommended that DOE include
the humidity ratio in pounds water vapor per pounds dry air. CA IOU
submits that this addition will increase the accuracy of the
calculation of specific volume of test room air in cubic feet per pound
of dry air to calculate airflow. (CA IOU, No. 106 at p. 4)
The equation for calculating airflow in the final test procedure
already includes the humidity ratio in pounds water vapor per pounds
dry air as codified in Section 9 of appendix AA of subpart B of part
430 of the CFR.
CA IOU recommended that in addition to reporting FER, which is the
basis for the performance standard, DOE require manufacturers to report
individual mode electrical energy consumption values (e.g.,
EHeat, EMax, and ECirc). According to
CA IOU,
[[Page 38141]]
reporting these values would greatly facilitate the development of more
targeted energy efficiency incentive programs, and manufacturers
already have to measure and perform these calculations for the
composite FER. CA IOU recognizes that EMax could represent
fan electrical energy consumption in either heating or cooling mode
depending on the product. Nonetheless, CA IOU also recommends that DOE
require manufacturers to report fan electrical energy consumption in
cooling mode even if not included in FER because having it as an
additional data point could be useful for the development of utility
programs across the country. CA IOU stated that energy efficiency
incentive programs typically require a rigorous level of review and
justification for implementation. Gaps in performance data of
commercially available equipment is one of the main limiting factors in
program development, contributing to the lengthy and resource-intensive
data collection and verification processes. In the case of this
rulemaking, manufacturers will already be required to test their
products in heating, cooling, and constant circulation modes. CA IOU
believes that the minimal extra effort required by manufacturers to
report these values would be outweighed by the opportunity for
utilities and other public agencies to develop incentive programs using
these performance metrics, which in turn would positively impact
manufacturers of high performing products. For these reasons, CA IOU
strongly urge DOE to require manufacturers to report tested and
calculated metrics that feed into a composite metric for the standard.
ASAP, ASE, NCLC, and NRDC, hereinafter referred to as ASAP, et al.,
agree. (ASAP, et al., No. 105 at p. 3)
At this time, DOE is declining to adopt reporting requirements for
individual mode electrical consumption values as the CA IOU suggests.
While DOE is open to considering additional reporting metrics in the
future, DOE believes that establishing a Federal test procedure and
metric (i.e., FER) will provide utility programs with a basis for
establishing meaningful incentive programs as the CA IOUs desire.
Further, DOE believes that reporting the aggregated electrical
consumption (i.e., the FER metric) will provide market differentiation
amongst currently- available models, thereby allowing the utility
programs to set voluntary levels for incentive programs at meaningful
levels to obtain energy savings. If data and analyses are provided,
which show the disaggregated levels are necessary for the proper
execution of utility incentive programs, DOE will consider modifying
the certification requirements for furnace fans.
Unico pointed out that DOE presents the required minimum reference
system ESP values inconsistently across rulemaking documents. Unico
noticed that in some documents DOE presents these values as a range for
each installation type, and in other rulemaking documents DOE presents
only the lower value within each range with an asterisk. (Unico, No. 93
at p. 6)
As explained in the test procedure final rule, DOE's test
experience confirms manufacturer concerns that specific ESP values are
difficult to achieve and maintain when measuring airflow. The final
test procedure specifies that products maintain an ESP level between
the minimum reference system value and 0.05 in. wc. above that minimum
value to allow for slight variations. 79 FR 508 (January 3, 2014).
Consequently, DOE presents the minimum required ESP values as a range
in Section 8.6.1.2 in appendix AA of subpart B of part 430 in the CFR
or as the minimum value with an asterisk accompanied by the explanation
above in other DOE documents.
AHRI commented that DOE should provide the option of employing an
alternative efficiency determination method (AEDM) to determine FER.
AHRI insists that an AEDM is critical for manufacturers to implement
new requirements on a timely basis while minimizing burden. AHRI
believes that the number of furnace fan basic models will be greater
than the number of furnace basic models. According to AHRI, the
pressure drop due to the gas heat exchanger will require that each
furnace basic model also be considered as a furnace fan basic model.
AHRI added that additional furnace fan basic models would be created in
order to account for the type of installation. AHRI also pointed out
that many furnace fan manufacturers also produce several other DOE
regulated products. AHRI submits that rather than requiring
manufacturers to spend valuable resources on conducting several tests,
DOE should recognize that those resources could be better spent on
innovating more efficient products. (AHRI, No. 98 at p. 13)
DOE provided a detailed discussion of this issue in the test
procedure final rule. 79 FR 513 (January 3, 2014). DOE currently does
not allow the use of AEDMs for residential products, with the exception
of central air conditioners and heat pumps due to the uniquely large
number of combinations of split-system air conditioners and heat pumps
that are rated. DOE recognizes that the number of furnace fan basic
models may outnumber furnace basic models for the reasons AHRI lists.
Even so, DOE expects the number of basic models of furnace fans to be
significantly less than the number of basic models of residential
central air conditioners and heat pumps (CAC and HP) for which
alternative rating methods are currently allowed. DOE has not found the
residential furnace fan market to be highly customized (i.e.,
containing many unique built-to-order designs) and expects that
manufacturers will be able to group similar individual furnace fan
types into basic models to reduce testing burden. DOE notes that it
currently has over 1 million CAC combinations certified in the
Compliance Certification Management System (CCMS) compared to
approximately 12,500 certified furnace basic models. Consequently, DOE
does not agree with AHRI's assertion that an alternative rating method
needs to be considered at this time. Should AHRI or the industry
provide additional data or substantiation for its requests
demonstrating why testing furnace fans are unique, as compared to the
majority of other residential products for which AEDMs are not allowed,
then DOE may consider such requests in a separate rulemaking.
B. Product Classes and Scope of Coverage
Although the title of 42 U.S.C. 6295(f) refers to ``furnaces and
boilers,'' DOE notes that 42 U.S.C. 6295(f)(4)(D) was written using
notably broader language than the other provisions within the same
section. Specifically, that statutory provision directs DOE to
``consider and prescribe energy conservation standards or energy use
standards for electricity used for purposes of circulating air through
duct work.'' Such language could be interpreted as encompassing
electrically-powered devices used in any residential HVAC product to
circulate air through duct work, not just furnaces, and DOE has
received numerous comments on both sides of this issue. However, in
this rulemaking, DOE is only covering those circulation fans that are
used in furnaces and modular blowers. DOE is using the term ``modular
blower'' to refer to HVAC products powered by single-phase electricity
that comprise an encased circulation blower that is intended to be the
principal air-circulation source for the living space of a residence. A
modular blower is not contained within the same cabinet as a
residential furnace, CAC, or heat pump. Instead,
[[Page 38142]]
modular blowers are designed to be paired with separate residential
HVAC products that provide heating and cooling, typically a separate
CAC/HP coil-only unit. DOE finds that modular blowers and electric
furnaces are very similar in design. In many cases, the only difference
between a modular blower and electric furnace is the presence of an
electric resistance heating kit. DOE is aware that some modular blower
manufacturers offer electric resistance heating kits to be installed in
their modular blower models so that the modular blowers can be
converted to stand-alone electric furnaces. In addition, FER values for
modular blowers can be easily calculated using the final test
procedure. DOE addresses the furnace fans used in modular blowers in
this rulemaking for these reasons. As a result of the extent of the
current rulemaking, DOE is not addressing public comments that pertain
to fans in other types of HVAC products.
When evaluating and establishing energy conservation standards, DOE
divides covered products into product classes by the type of energy
used or by capacity or other performance-related features that justify
a different standard. In making a determination whether a performance-
related feature justifies a different standard, DOE must consider such
factors as the utility to the consumer of the feature and other factors
DOE determines are appropriate. (42 U.S.C. 6295(q)) For this
rulemaking, DOE differentiates between product classes based on
internal structure and application-specific design differences that
impact furnace fan energy consumption. Details regarding how internal
structure and application-specific design differences that impact
furnace fan energy consumption are included in chapter 3 of the final
rule technical support document (TSD). DOE includes the following
product classes for this rulemaking.
Non-Weatherized, Non-Condensing Gas Furnace Fan (NWG-NC)
Non-Weatherized, Condensing Gas Furnace Fan (NWG-C)
Weatherized Non-Condensing Gas Furnace Fan (WG-NC)
Non-Weatherized, Non-Condensing Oil Furnace Fan (NWO-NC)
Non-Weatherized Electric Furnace/Modular Blower Fan (NWEF/
NWMB)
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan
(MH-NWG-NC)
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan (MH-
NWG-C)
Mobile Home Electric Furnace/Modular Blower Fan (MH-EF/MB)
Mobile Home Weatherized Gas Furnace Fan (MH-WG)
Mobile Home Non-Weatherized Oil Furnace Fan (MH-NWO)
Each product class title includes descriptors that indicate the
application-specific design and internal structure of its included
products. ``Weatherized'' and ``non-weatherized'' are descriptors that
indicate whether the HVAC product is installed outdoors or indoors,
respectively. Weatherized products also include an internal evaporator
coil, while non-weatherized products are not shipped with an evaporator
coil but may be designed to be paired with one. ``Condensing'' refers
to the presence of a secondary, condensing heat exchanger in addition
to the primary combustion heat exchanger in certain furnaces. The
presence of an evaporator coil or secondary heat exchanger
significantly impacts the internal structure of an HVAC product, and in
turn, the energy performance of the furnace fan integrated in that HVAC
product. ``Mobile home'' products meet certain design requirements that
allow them to be installed in mobile homes (e.g., a more compact
cabinet size). Descriptors for ``gas,'' ``oil,'' or ``electric''
indicate the type of fuel that the HVAC product uses to produce heat,
which determines the type and geometry of the primary heat exchanger
used in the HVAC product.
C. Technological Feasibility
1. General
In each energy conservation standards rulemaking, DOE conducts a
screening analysis based on information gathered on all current
technology options and prototype designs that could improve the
efficiency of the products or equipment that are the subject of the
rulemaking. As the first step in such an analysis, DOE develops a list
of technology options for consideration in consultation with
manufacturers, design engineers, and other interested parties. DOE then
determines which of those means for improving efficiency are
technologically feasible. DOE considers technologies incorporated in
commercially-available products or in working prototypes to be
technologically feasible. 10 CFR part 430, subpart C, appendix A,
Section 4(a)(4)(i).
After DOE has determined that particular technology options are
technologically feasible, it further evaluates each technology option
in light of the following additional screening criteria: (1)
Practicability to manufacture, install, and service; (2) adverse
impacts on product utility or availability; and (3) adverse impacts on
health or safety. 10 CFR part 430, subpart C, appendix A, Section
4(a)(4)(ii)-(iv). Additionally, it is DOE policy not to include in its
analysis any proprietary technology that is a unique pathway to
achieving a certain efficiency level. Section IV.B of this document
discusses the results of the screening analysis for residential furnace
fans, particularly the designs DOE considered, those it screened out,
and those that are the basis for the tcrial standard levels (TSLs) in
this rulemaking. For further details on the screening analysis for this
rulemaking, see chapter 4 of the final rule TSD.
2. Maximum Technologically Feasible Levels
When DOE proposes to adopt a new standard for a type or class of
covered product, it must determine the maximum improvement in energy
efficiency or maximum reduction in energy use that is technologically
feasible for such product. (42 U.S.C. 6295(p)(1)) Accordingly, in the
engineering analysis, DOE determined the maximum technologically
feasible (``max-tech'') improvements in energy efficiency for
residential furnace fans, using the design parameters for the most-
efficient products available on the market or in working prototypes.
The max-tech levels that DOE determined for this rulemaking are
described in section IV.C of this final rule and in chapter 5 of the
final rule TSD.
D. Energy Savings
1. Determination of Savings
For each TSL, DOE projected energy savings from the products that
are the subjects of this rulemaking purchased during a 30-year period
that begins in the year of compliance with amended standards (2019-
2048).\13\ The savings are measured over the entire lifetime of
products purchased in the 30-year period.\14\ DOE used the NIA model to
estimate the NES for products purchased over the above period. The
model forecasts total energy use over the analysis period for each
representative product class at efficiency levels set by each of the
considered TSLs. DOE then
[[Page 38143]]
compares the aggregated energy use at each TSL to the base-case energy
use to obtain the NES. The NIA model is described in section IV. H of
this document and in chapter 10 of the final rule TSD.
---------------------------------------------------------------------------
\13\ DOE also presents a sensitivity analysis that considers
impacts for products shipped in a 9-year period.
\14\ In the past, DOE presented energy savings results for only
the 30-year period that begins in the year of compliance. In the
calculation of economic impacts, however, DOE considered operating
cost savings measured over the entire lifetime of products purchased
during the 30-year period. DOE has chosen to modify its presentation
of national energy savings to be consistent with the approach used
for its national economic analysis.
---------------------------------------------------------------------------
DOE used its NIA spreadsheet model to estimate energy savings from
amended standards for the products that are the subject of this
rulemaking. The NIA spreadsheet model (described in section IV. H of
this notice) calculates energy savings in site energy, which is the
energy directly consumed by products at the locations where they are
used. For electricity, DOE reports national energy savings in terms of
the primary (source) energy savings, which are the savings in the
energy that is used to generate and transmit the site electricity. To
convert site energy to primary energy, DOE derives annual conversion
factors from the model used to prepare the Energy Information
Administration's (EIA) Annual Energy Outlook 2013 (AEO 2013).
DOE also has begun to estimate full-fuel-cycle energy savings. 76
FR 51282 (August 18, 2011), as amended at 77 FR 49701 (August 17,
2012). The full-fuel-cycle (FFC) metric includes the energy consumed in
extracting, processing, and transporting primary fuels (i.e., coal,
natural gas, petroleum fuels), and thus presents a more complete
picture of the impacts of energy efficiency standards. DOE's evaluation
of FFC savings is driven in part by the National Academy of Science's
(NAS) report on FFC measurement approaches for DOE's Appliance
Standards Program.\15\ The NAS report discusses that FFC was primarily
intended for energy efficiency standards rulemakings where multiple
fuels may be used by a particular product. In the case of this
rulemaking pertaining to residential furnace fans, only a single fuel--
electricity--is consumed by the product. DOE's approach is based on the
calculation of an FFC multiplier for each of the energy types used by
covered products. Although the addition of FFC energy savings in the
rulemakings is consistent with the recommendations, the methodology for
estimating FFC does not project how fuel markets would respond to this
particular standards rulemaking. The FFC methodology simply estimates
how much additional energy, and in turn how many tons of emissions, may
be displaced if the estimated fuel were not consumed by the products
covered in this rulemaking. It should be noted that inclusion of FFC
savings has not affected DOE's choice of the energy conservation
standards adopted in today's final rule. For more information on FFC
energy savings, see section IV. H.2.
---------------------------------------------------------------------------
\15\ ``Review of Site (Point-of-Use) and Full-Fuel-Cycle
Measurement Approaches to DOE/EERE Building Appliance Energy-
Efficiency Standards,'' (Academy report) was completed in May 2009
and included five recommendations. A copy of the study can be
downloaded at: https://www.nap.edu/catalog.php?record_id=12670.
---------------------------------------------------------------------------
2. Significance of Savings
EPCA prohibits DOE from adopting a standard for a covered product
that would not result in significant energy savings. (42 U.S.C.
6295(o)(3)(B)) Although the term ``significant'' is not defined in
EPCA, the U.S. Court of Appeals for the District of Columbia, in
Natural Resources Defense Council v. Herrington, 768 F.2d 1355, 1373
(D.C. Cir. 1985), opined that Congress intended ``significant'' energy
savings in this context to be savings that were not ``genuinely
trivial.'' The energy savings for today's standards (presented in
section V of this notice) are nontrivial, and, therefore, DOE considers
them ``significant'' within the meaning of section 325 of EPCA.
E. Economic Justification
1. Specific Criteria
As discussed in section II.A, EPCA provides seven factors to be
evaluated in determining whether a potential energy conservation
standard is economically justified. (42 U.S.C. 6295(o)(2)(B)(i)(I)-
(VII)) The following sections generally discuss how DOE is addressing
each of those seven factors in this rulemaking. For further details and
the results of DOE's analyses pertaining to economic justification, see
sections IV and V of today's document.
Economic Impact on Manufacturers and Commercial Customers
In determining the impacts of a potential new or amended energy
conservation standard on manufacturers, DOE conducts a manufacturer
impact analysis (MIA), as discussed in section IV.J. DOE first
determines a potential standard's quantitative impacts using an annual
cash flow approach. This step includes both a short-term assessment
(based on the cost and capital requirements associated with new or
amended standards during the period between the announcement of a
regulation and the compliance date of the regulation) and a long-term
assessment (based on the costs and marginal impacts over the 30-year
analysis period). The impacts analyzed include: (1) Industry net
present value (INPV) (which values the industry based on expected
future cash flows); (2) cash flows by year; (3) changes in revenue and
income; and (4) other measures of impact, as appropriate. Second, DOE
analyzes and reports the potential impacts on different types of
manufacturers, paying particular attention to impacts on small
manufacturers. Third, DOE considers the impact of new or amended
standards on domestic manufacturer employment and manufacturing
capacity, as well as the potential for new or amended standards to
result in plant closures and loss of capital investment, as discussed
in section IV.N. Finally, DOE takes into account cumulative impacts of
other DOE regulations and non-DOE regulatory requirements on
manufacturers.
For individual customers, measures of economic impact include the
changes in LCC and the PBP associated with new or amended standards.
These measures are discussed further in the following section. For
consumers in the aggregate, DOE also calculates the national net
present value of the economic impacts applicable to a particular
rulemaking. DOE also evaluates the LCC impacts of potential standards
on identifiable subgroups of consumers that may be affected
disproportionately by a national standard.
Savings in Operating Costs Compared to Increase in Price (Life-Cycle
Costs)
EPCA requires DOE to consider the savings in operating costs
throughout the estimated average life of the covered product compared
to any increase in the price of the covered product that are likely to
result from the standard. (42 U.S.C. 6295(o)(2)(B)(i)(II)) DOE conducts
this comparison in its LCC and PBP analysis.
The LCC is the sum of the purchase price of a product (including
the cost of its installation) and the operating costs (including
energy, maintenance, and repair costs) discounted over the lifetime of
the equipment. To account for uncertainty and variability in specific
inputs, such as product lifetime and discount rate, DOE uses a
distribution of values, with probabilities attached to each value. For
its analysis, DOE assumes that consumers will purchase the covered
product in the first year of compliance with new standards.
The LCC savings and the PBP for the considered efficiency levels
are calculated relative to a base-case scenario, which reflects likely
market trends in the absence of new or amended standards. DOE
identifies the percentage of consumers estimated to receive LCC savings
or experience an LCC increase, in addition to the average LCC savings
associated with a particular
[[Page 38144]]
standard level. DOE's LCC analysis is discussed in further detail in
section IV.F.
Energy Savings
Although significant conservation of energy is a separate statutory
requirement for adopting an energy conservation standard, EPCA also
requires DOE, in determining the economic justification of a standard,
to consider the total projected energy savings that are expected to
result directly from the standard. (42 U.S.C. 6295(o)(2)(B)(i)(III))
DOE uses NIA spreadsheet results in its consideration of total
projected savings. For the results of DOE's analyses related to the
potential energy savings, see section V.B of this notice and chapter 10
of the final rule TSD.
Lessening of Utility or Performance of Equipment
In establishing product classes, and in evaluating design options
and the impact of potential standard levels, DOE follows EPCA's
requirement to develop standards that would not lessen the utility or
performance of the products under consideration. (42 U.S.C.
6295(o)(2)(B)(i)(IV)) DOE has determined that none of the TSLs
presented in today's final rule would reduce the utility or performance
of the products under consideration in this rulemaking. During the
screening analysis, DOE eliminated from consideration any technology
that would adversely impact customer utility. See section IV.B of this
notice and chapter 4 of the final rule TSD for further details.
Impact of Any Lessening of Competition
EPCA requires DOE to consider any lessening of competition that is
likely to result from setting new or amended standards. It also directs
the Attorney General of the United States (Attorney General) to
determine the impact, if any, of any lessening of competition likely to
result from a proposed standard and to transmit such determination to
the Secretary within 60 days of the publication of a proposed rule,
together with an analysis of the nature and extent of the impact. (42
U.S.C. 6295(o)(2)(B)(i)(V) and (ii))
To assist the Department of Justice (DOJ) in making such a
determination, DOE provided DOJ with copies of both the NOPR and NOPR
TSD for review. In its assessment letter responding to DOE, DOJ
concluded that the proposed energy conservation standards for
residential furnace fans are unlikely to have a significant adverse
impact on competition. DOE is publishing the Attorney General's
assessment at the end of this final rule.
Need of the Nation To Conserve Energy
Another factor that DOE must consider in determining whether a new
or amended standard is economically justified is the need for national
energy and water conservation. (42 U.S.C. 6295(o)(2)(B)(i)(VI)) The
energy savings from new or amended standards are likely to provide
improvements to the security and reliability of the Nation's energy
system. Reductions in the demand for electricity may also result in
reduced costs for maintaining the reliability of the Nation's
electricity system. DOE conducts a utility impact analysis to estimate
how new or amended standards may affect the Nation's needed power
generation capacity, as discussed in section IV.M.
Energy savings from energy conservation standards are also likely
to result in environmental benefits in the form of reduced emissions of
air pollutants and greenhouse gases associated with energy production
(i.e., from power plants). For a discussion of the results of the
analyses relating to the potential environmental benefits of today's
standards, see sections IV.K, IV.L and V.B.6 of this notice. DOE
reports the expected environmental effects from today's standards, as
well as from each TSL it considered, in chapter 13 of the final rule
TSD. DOE also reports estimates of the economic value of emissions
reductions resulting from the considered TSLs in chapter 14 of the
final rule TSD.
Other Factors
EPCA allows the Secretary, in determining whether a new or amended
standard is economically justified, to consider any other factors that
the Secretary deems to be relevant. (42 U.S.C. 6295(o)(2)(B)(i)(VII))
There were no other factors considered for today's final rule.
2. Rebuttable Presumption
As set forth in 42 U.S.C. 6295(o)(2)(B)(iii), EPCA provides for a
rebuttable presumption that an energy conservation standard is
economically justified if the additional cost to the consumer of a
product that meets the new or amended standard is less than three times
the value of the first-year energy (and, as applicable, water) savings
resulting from the standard, as calculated under the applicable DOE
test procedure. DOE's LCC and PBP analyses generate values that
calculate the PBP for consumers of products subject to potential new
and amended energy conservation standards. These analyses include, but
are not limited to, the 3-year PBP contemplated under the rebuttable
presumption test. However, DOE routinely conducts an economic analysis
that considers the full range of impacts to consumers, manufacturers,
the Nation, and the environment, as required under 42 U.S.C.
6295(o)(2)(B)(i). The results of these analyses serve as the basis for
DOE's evaluation of the economic justification for a potential standard
level (thereby supporting or rebutting the results of any preliminary
determination of economic justification). The rebuttable presumption
payback calculation is discussed in section IV.F of this rulemaking and
chapter 8 of the final rule TSD.
IV. Methodology and Discussion
A. Market and Technology Assessment
DOE develops information that provides an overall picture of the
market for the products concerned, including the purpose of the
products, the industry structure, manufacturers, market
characteristics, and technologies used in the products. This activity
includes both quantitative and qualitative assessments, based primarily
on publicly-available information. The subjects addressed in the market
and technology assessment for this residential furnace fans rulemaking
include: (1) A determination of the scope of this rulemaking; (2)
product classes; (3) manufacturers; (4) quantities and types of
products sold and offered for sale; (5) retail market trends; (6)
regulatory and non-regulatory programs; and (7) technologies or design
options that could improve the energy efficiency of the product(s)
under examination. The key findings of DOE's market assessment are
summarized below. See chapter 3 of the final rule TSD for further
discussion of the market and technology assessment.
1. Definition and Scope of Coverage
EPCA provides DOE with the authority to consider and prescribe new
energy conservation standards for electricity used to circulate air
through duct work. (42 U.S.C. 6295(f)(4)(D)) DOE adopted the term
``furnace fan'' as shorthand to describe the range of products
encompassed by this statutory mandate. In the preliminary analysis, DOE
interpreted its statutory mandate by defining ``furnace fan'' to
include ``any electrically-powered device used in residential central
heating, ventilation, and air-conditioning (HVAC) systems for the
purpose of circulating air through duct work.'' 77 FR 40530, 40532
(July 10, 2012). DOE
[[Page 38145]]
considered a typical furnace fan as consisting of a fan motor and its
controls, an impeller, and a housing, all of which are components of an
HVAC product that includes additional components, including the
cabinet.
In response to the preliminary analysis, many interested parties
disagreed with DOE's definition of ``furnace fan'' and corresponding
approach to set component-level regulations, which they warned would
ignore system effects that could impact both fan and HVAC system energy
consumption. California investor-owned utilities CA IOUs suggested that
``furnace fan'' should be defined as a unit consisting of a fan motor,
its controls, an impeller, shroud, and cabinet that houses all of the
heat exchange material for the furnace. According to CA IOUs, their
suggested definition would reduce ambiguity and ensure that the
components in HVAC products that affect furnace fan energy consumption
are considered in this rulemaking. (CA IOUs, No. 56 at p. 1) Ingersoll
Rand went further and suggested a system-level regulatory approach,
where the entire duct and furnace system would be regulated,
maintaining that such approach would produce a more useful metric to
consumers when evaluating performance. (Ingersoll Rand, PA Public
Meeting Transcript, No. 43 at p. 42) Conversely, NEEP observed that by
regulating fan energy use separately, the individual efficiency of the
component is considered when it would otherwise be ignored by
manufacturers. (NEEP, No. 51 at p. 3) Rheem commented that some designs
require higher air velocity to improve heat transfer but also require
more electrical consumption to drive the blower at the higher velocity.
(Rheem, PA Public Meeting Transcript, No. 43 at p. 63) Rheem commented
that turbulent flow is considerably more efficient for heat transfer
than laminar flow,\16\ but more energy is required to move turbulent
air. (Rheem, No. 54 at p. 10) Similarly, Lennox and Morrison commented
that in order to improve heating and cooling efficiency, often a second
heating coil is added, but this also leads to higher electrical
consumption by the furnace fan. (Lennox, No. 43 at p. 64; Morrison, No.
43 at p. 64) Ingersoll Rand argued that as the efficiency of the
furnace fan motor increases, it dissipates less heat, and consequently,
the furnace will consume more gas to compensate and meet the desired
house heat load. (Ingersoll Rand, No. 43 at p. 66)
---------------------------------------------------------------------------
\16\ ``Laminar flow'' is as term to describe when all fluid
particles move in paths parallel to the overall flow direction
(i.e., in layers). Laminar flow may occur when the flow channel is
small and the speed is low. ``Turbulent flow'' is characterized by a
three-dimensional movement of the fluid particles superimposed on
the overall direction of motion. Turbulent flow may occur when the
flow speed is higher and when there are obstacles in the channel
that disrupt the flow profile. The turbulent flow intensifies the
heat transfer, thus resulting in more efficient heat exchange.
---------------------------------------------------------------------------
In the NOPR, DOE responded by explaining that DOE is required by
EPCA to consider and prescribe new energy conservation standards or
energy use standards for electricity used for purposes of circulating
air through duct work. (42 U.S.C. 6295(f)(4)(D)) Consequently, in the
context of furnace fans, DOE does not have latitude to apply only a
single standard for the larger HVAC product (which is already
regulated). Pursuant to this statutory mandate, DOE issued a NOPR which
proposed energy conservation standards for circulation fans used in
residential central HVAC systems (78 FR 64068 (Oct. 25, 2013)). DOE
added that it did not interpret its authority as including regulating
the duct work itself. DOE recognized that component-level regulations
could have system-level impacts. Accordingly, DOE conducted its NOPR
analyses and selected the standard levels proposed in the NOPR in such
a way that meets the statutory requirements set forth by EPCA without
ignoring system effects, which otherwise might compromise the thermal
performance of the HVAC products that incorporate furnace fans. For
example, the final test procedure codified in DOE's regulations at 10
CFR part 430, subpart B, appendix AA specifies that the furnace fan be
tested as factory-installed in the HVAC product, thereby enabling the
rating metric, FER, to account for system effects on airflow delivery
and, ultimately, energy performance. In addition, the product class
structure proposed in the NOPR allowed for differentiation of products
with designs that achieve higher thermal efficiency but may have lower
fan performance, such as condensing furnaces. 78 FR 64068, 64082 (Oct.
25, 2013).
In the January 3, 2014 test procedure final rule, DOE broadened its
definition of ``furnace fan'' to mean ``an electrically-powered device
used in a consumer product for the purpose of circulating air through
ductwork.'' 79 FR 500, 521.
In response to the NOPR, DOE did not receive comments from
interested parties regarding the definition of ``furnace fan''
established by the test procedure final rule. Consequently, in this
standards final rule, DOE is maintaining the definition for ``furnace
fan,'' codified at 10 CFR 430.2. However, DOE did receive comments on
its definitions for certain product types that include furnace fans.
DOE summarizes and responds to these comments later in this section of
the notice.
The scope of the preliminary analysis included furnace fans used in
furnaces, modular blowers, and hydronic air handlers. Even though DOE
has interpreted its authority as encompassing any electrically-powered
device used in residential HVAC products to circulate air through duct
work, the preliminary analysis scope excluded single-package central
air conditioners (CAC) and heat pumps (HP) and split-system CAC/HP
blower-coil units. At the time of the preliminary analysis, DOE
determined that it may consider these and other such products in a
future rulemaking as data and information to develop credible analyses
becomes available.
In response to the preliminary analysis, efficiency advocates
expressed concern at DOE's exclusion of packaged and split-system CAC
products because advocates believe current standards for these products
do not maximize the technologically feasible and economically justified
energy savings for the circulation fans integrated in these products.
ASAP and Adjuvant stated that the metric used for CAC products does not
accurately represent field conditions and requested that they be added
to the scope. 78 FR 64068, 64080 (Oct. 25, 2013).
In contrast, many manufacturers submitted comments in response to
the preliminary analysis that they believe that the scope of coverage
presented in the preliminary analysis exceeds the statutory authority
granted to DOE because the statutory language for this rulemaking is
found in 42 U.S.C 6295(f) under the title ``Standards for furnaces and
boilers.'' Consequently, manufacturers stated that DOE should not
include any non-furnace products such as central air conditioners, heat
pumps, or condensing unit-blower-coil combinations. Manufacturers also
claimed that the electricity used to circulate air through duct work is
already adequately accounted for in existing energy efficiency metrics
for CAC and HP products that use circulation fans. 78 FR 64068, 64080-
81 (Oct. 25, 2013).
In the October 25, 2013 furnace fan energy conservation standard
NOPR, DOE noted that, although the title of this statutory section
refers to ``furnaces and boilers,'' the applicable provision at 42
U.S.C. 6295(f)(4)(D) was written using notably broader language than
the other provisions within the same section. 78
[[Page 38146]]
FR 64068, 64081. Specifically, that statutory provision directs DOE to
``consider and prescribe energy conservation standards or energy use
standards for electricity used for purposes of circulating air through
duct work.'' Id. Such language could be interpreted as encompassing
electrically-powered devices used in any residential HVAC product to
circulate air through duct work, not just furnaces, and DOE has
received numerous comments on both sides of this issue. In the
standards NOPR, however, DOE only proposed energy conservation
standards for those circulation fans that are used in residential
furnaces and modular blowers (see discussion below). As a result, DOE
did not address public comments that pertain to fans in other types of
HVAC products (other than to clarify instances where there was
uncertainty as to whether a given product fits within the scope of the
current rulemaking). The following list describes the furnace fans
which DOE proposed to address in the standards NOPR.
Products addressed in this rulemaking: Furnace fans used
in weatherized and non-weatherized gas furnaces, oil furnaces, electric
furnaces, and modular blowers.
Products not addressed in this rulemaking: Furnace fans
used in other products, such as split-system CAC and heat pump indoor
units, through-the-wall indoor units, small-duct, high-velocity (SDHV)
indoor units, energy recovery ventilators (ERVs), heat recovery
ventilators (HRVs), draft inducer fans, exhaust fans, or hydronic air
handlers.
Id.
In the October 25, 2013 NOPR, DOE also maintained its proposal to
account for the electrical consumption of furnace fans while performing
all active mode functions (i.e., heating, cooling, and constant
circulation) because furnace fans are used not just for circulating air
through duct work during heating operation, but also for circulating
air during cooling and constant-circulation operation. In DOE's view,
in order to obtain a complete assessment of overall performance and a
metric that reflects the product's electrical energy consumption during
a representative average use cycle, the metric must account for
electrical consumption in a set of airflow-control settings that spans
all active mode functions. This would ensure a more accurate accounting
of the benefits of improved furnace fans. Id.
China WTO commented that DOE's definition for ``furnace fan'' and
the proposed scope show that residential furnace fans primarily perform
the heating function. For this reason, China WTO recommended that DOE
exclude fan performance for cooling operation to avoid unnecessary test
procedure burden. (China WTO, No. 92 at pp. 1-2).
For the reasons stated above, the energy conservation standards
established by this notice account for the electrical consumption of
furnace fans while performing all active mode functions (i.e., heating,
cooling, and constant circulation). The commenter did not dispute the
fact that fans will operate in cooling or constant-circulation mode,
often for non-trivial periods of time. Because the electrical energy
consumption of the fan may vary substantially depending on its mode of
operation, DOE has concluded that testing fan operation in all these
modes is necessary to reflect the product's energy consumption during a
representative use cycle and that such testing would not be unduly
burdensome to conduct.
Unico submitted comments regarding concerns with DOE's test
procedure and proposed standard levels as they apply to SDHV systems.
Unico explains that DOE proposed to exclude SDHV products from the
rulemaking but included modular blowers and electric furnaces,
resulting in a potential conflict. Unico added that most of their SDHV
air handlers are modular in construction. Unico also offers an add-on
electric furnace to provide secondary or backup heat, but very few
systems are installed as an electric furnace. As a result, Unico
expressed uncertainty whether this rule applies to SDHV modular blowers
and SDHV electric furnaces. Unico provided data showing that SDHV
blowers operate at different conditions compared to the products
proposed to be covered and cannot meet the proposed FER levels.
Ultimately, Unico expressed concerns that this rule could potentially
eliminate many SDHV products from the market if they are subject to
DOE's proposed standards. (Unico, No. 93 at pp.1-4)
In response to the comment, DOE clarifies that the furnace fan test
procedure and the energy conservation standards established by this
final rule do not apply to SDHV products, including SDHV modular
blowers and electric furnaces. DOE recognizes that these products
operate at different conditions which significantly impact their fan
performance, as compared to the products addressed in this rulemaking.
While DOE's regulations at 10 CFR 430.2 include a definition for
``small duct high velocity systems,'' it does not include a definition
for small duct high velocity modular blowers or SDHV electric furnaces.
Absent clarification, DOE realizes that confusion may result regarding
which products are and are not covered by today's standards.
Accordingly, DOE is adopting the following definition of ``small-duct
high-velocity (SDHV) modular blower,'' which has been drafted to be
consistent with the existing definition of ``SDHV system'' at 10 CFR
430.2:
Small-duct high-velocity (SDHV) modular blower means a product
that:
Meets the definition of ``modular blower,'' as set forth
in 10 CFR part 430, subpart B, appendix AA;
Is designed for, and produces, at least 1.2 inches of
external static pressure when operated at the certified air volume rate
of 220-350 CFM per rated ton of cooling in the highest default cooling
airflow-controls setting; and
When applied in the field, uses high velocity room outlets
generally greater than 1,000 fpm that have less than 6.0 square inches
of free area.
Similarly, DOE is adopting a definition for ``small-duct high-
velocity (SDHV) electric furnace'' to read as follows:
Small-duct high-velocity (SDHV) electric furnace means a product
that:
Meets the definition of ``electric furnace,'' as set forth
in 10 CFR 430.2;
Is designed for, and produces, at least 1.2 inches of
external static pressure when operated at the certified air volume rate
of 220-350 CFM per rated ton of cooling in the highest default cooling
airflow-control setting; and
When applied in the field, uses high velocity room outlets
generally greater than 1,000 fpm that have less than 6.0 square inches
of free area.
DOE has concluded that these amendments should eliminate any
confusion associated with DOE not addressing SDHV modular blowers and
SDHV electric furnaces in the present rulemaking. Unico also submitted
other SDHV-related concerns, but DOE need not discuss those issues
further because SDHV products are not addressed in this rulemaking.
AHRI, Morrison, Goodman, Johnson Controls, and Mortex stated that
modular blowers should be excluded from the scope of this rulemaking.
(AHRI, No. 98 at pp. 1, 2; Morrison, No. 108 at p. 1; Goodman, No. 102
at p. 5; Johnson Controls, No. 95 at p. 2; and Mortex, NOPR Public
Meeting Transcript, No. 91 at pp. 78-79). AHRI,
[[Page 38147]]
Morrison, and Johnson Controls continue to advance an interpretation of
42 USC 6295(f)(4)(D) as being only applicable to furnaces, and these
commenters argued that absent a legislative change, DOE has exceeded
its statutory authority in terms of the NOPR's proposed coverage of
modular blowers. (AHRI, No. 98 at pp. 1-2; Morrison, No. 108 at p. 1;
and Johnson Controls, No, 95 at p. 2). AHRI and Johnson Controls added
that some modular blowers in today's marketplace are not designed to
operate with electric resistance heat kits, rendering the final test
procedure insufficient for these products. (AHRI, No. 98 at pp. 1, 2;
and Johnson Controls, No. 95 at p. 3).
ASAP, et al., on the other hand, expressed support for the
inclusion of modular blowers in the scope of coverage. ASAP, et al.
stated that they understand that the strip heat used with electric
furnaces is often installed in the field, which means that an
``electric furnace'' is often sold by the manufacturer as a ``modular
blower.'' ASAP, et al. cite DOE's finding that non-weatherized and
mobile home electric furnace/modular blower furnace fans represent 10
percent of all furnace fan sales. According to ASAP, et al., excluding
modular blowers from the scope of coverage would not only reduce energy
savings from this rulemaking, but would also create a loophole--i.e.,
manufacturers would have an incentive to sell electric furnaces as
modular blowers (without strip heat installed) in order to avoid
compliance with the furnace fan energy conservation standards. (ASAP,
et al., No. 105 at pp. 1, 2)
As stated above, DOE maintains its interpretation that the relevant
statutory language at 42 U.S.C. 6295(f)(4)(D) is broader in its
applicability than just furnaces, and consequently, it provides DOE
authority to cover modular blowers in this rulemaking. These same
arguments were already addressed in some detail in the NOPR (see 78 FR
64068, 64081 (Oct. 25, 2013)). DOE also disagrees with the contention
of AHRI and Johnson Controls that the final test procedure is not
sufficient to address all modular blowers. All modular blower models of
which DOE is aware can be operated in conjunction with an electric
resistance heat kit, and commenters did not identify any models of
modular blowers that cannot. Even assuming arguendo that modular
blowers do exist that are not designed to operate with an electric
resistance heat kit, DOE expects that number of such models would be de
minimis and that manufacturers producing modular blowers that cannot be
operated in conjunction with an electric resistance heat kit would
apply for a waiver from the test procedure. DOE provides more details
regarding this issue in the January 3, 2014 test procedure final rule.
79 FR 504.
In its comments, Johnson Controls stated that DOE's use of the
phrase ``primary heat source'' is too ambiguous, especially when
certain products might be modified in the field. According to Johnson
Controls, DOE's characterizations of air handlers and modular blowers
when an air handler or modular blower is the primary heating source is
still confusing and brings uncertainty to the NOPR market assessment.
Johnson Controls commented that none of the residential air handlers,
modular blowers, or residential single-package finished good models
built by Johnson Controls includes factory-installed electric heat
kits. Therefore, according to the commenter, electric heat kits
installed in these products cannot be considered to be the primary
source for heat in their applications, and so none of these products
should be included in this rulemaking. Johnson Controls added that
while field-installed electric heat kits are available and used
frequently, the use of field kits is outside of the air handler or
modular blower manufacturer's control, unlike gas furnaces where the
application is known to usually be the primary heating source in the
vast number of situations. (Johnson Controls, No. 95 at p. 2) NEEA,
Mortex, and Daikin agreed that the contractor determines whether a CAC/
HP blower-coil unit with electric resistance heat is the principal
source of heating for a residence, rendering any such determination
speculative for other entities. (NEEA, NOPR Public Meeting Transcript,
No. 91 at pp. 64-65; Mortex, NOPR Public Meeting Transcript, No. 91 at
pp. 78-79; and Daikin, NOPR Public Meeting Transcript, No. 91 at pp.
75-76)
Modular blowers are not a source of heat per DOE's definition of
``modular blower'' as provided in 10 CFR part 430, subpart B, appendix
AA. Consequently, the ``principal heating source'' qualifier (per the
definition of ``furnace'' at 10 CFR 430.2) does not apply to modular
blowers, so this part of the ``furnace'' definition has the effect of
excluding modular blowers from that definition. However, the
``furnace'' definition is not the only factor in deciding whether
modular blowers are covered in this rulemaking, contrary to what
Johnson Controls suggests. If electric resistance heat is added to a
modular blower product, that product no longer meets DOE's definition
of a ``modular blower.'' Instead, DOE considers the modified product an
electric furnace, absent other design changes. Regardless of whether
the electric resistance heat is factory-installed, both product
variations are covered in the final test procedure and this energy
conservation standard.
DOE recognizes that interested parties may have trouble determining
whether a CAC/HP blower-coil unit with electric resistance heating is
considered an electric furnace and thereby covered by the energy
conservation standards established by this final rule. Strictly
following the DOE definition for ``electric furnace'' (which references
the DOE definition of ``furnace'') as set forth at 10 CFR 430.2,
coverage in this final rule of a CAC/HP blower-coil with electrical
resistance heating depends on whether the electric resistance heating
is the ``principal heating source for the residence.'' As Johnson
Controls points out, this is not as easily determined as for gas and
oil furnaces. DOE expects that in the significant majority of CAC/HP
blower-coil models that have electric resistance heat, the electric
resistance heat is supplemental in nature and not the principal heating
source for the residence. For this reason, DOE has decided that the
energy conservation standards established by this rule will not cover
CAC/HP blower-coil units, regardless of whether they include electric
resistance heat.
Lennox argued that including weatherized commercial products in
this rulemaking is unrealistic and improper. Specifically, Lennox
expressed concerns that DOE mischaracterizes single-package weatherized
products as ``residential'' when these products are offered with a
single-phase power source. The commenter stated that these products are
often used in commercial applications, explaining that single-phase
weatherized products are often designed to have higher duct static
pressure capability than a traditional residential furnace. Lennox
commented that they have single-phase belt-drive products that are
capable of operating up to 2 inches water column external static
pressure to meet commercial duct static requirements. According to
Lennox, BPM motors (including both constant-torque and constant-airflow
BPM motors) typically used in residential products cannot achieve the
high static pressures required in these commercial installations.
Therefore, Lennox recommended that DOE should exclude all products
marked not for residential use from standards coverage. (Lennox, No.
100 at p. 4).
DOE recognizes that industry may differentiate between residential
products and commercial equipment differently than DOE. The standards
[[Page 38148]]
established by this final rule do not cover all single-phase, single-
package HVAC products, only single-phase weatherized furnaces (i.e.,
single-phase, single-package HVAC products that include a ``furnace''
as defined at 10 CFR 430.2). Lennox did not identify, and after
additional research, DOE is not aware of any weatherized gas furnace
models that operate at the static pressures mentioned by the commenter.
DOE expects that the operating conditions mentioned by Lennox are
typical of single-package heat pump equipment, which is not covered by
this rule. DOE expects the number of models covered by this rule that
DOE defines as residential but are designed and operated in commercial
applications to be de minimis. Any manufacturer which can substantiate
its case that it would suffer serious hardship, gross inequity, and an
unfair distribution of burdens if required to comply with the furnace
fan standards may seek exception relief from DOE's Office of Hearings
and Appeals (OHA).\17\
---------------------------------------------------------------------------
\17\ For information about obtaining exception relief, see 10
CFR part 1003 (available at https://www.ecfr.gov/cgi-bin/text-idx?SID=d95bf6ed9cd849253fab734656f80c2e&node=10:4.0.3.5.3&rgn=div5).
---------------------------------------------------------------------------
ACEEE commented that if manufacturers offered air handlers as a
separate product, without the coil, the modified product would not be
inherently different than a modular blower. ACEEE stated that DOE
should cover CAC/HP blower-coil units following the same logic that DOE
used to justify covering modular blowers (i.e., because of their
similarities to electric furnaces). ACEEE also commented that the DOE
definition for ``modular blower'' is confusing because, in their
experience, all (or almost all) conventional indoor blower units--
whether furnaces, HP, or CAC--use a separate assembly (or field-
fabricated `plenum') to house the coil used as the evaporator (CAC) or
evaporator and condenser (HP). (ACEEE, No. 94 at pp. 1-2, 4).
DOE disagrees with ACEEE's assessment that a CAC/HP blower-coil
unit with the coil removed and an electric furnace are equally
comparable to a modular blower. For example, modular blowers are
typically designed to accommodate the addition of electric resistance
heating kits (after which DOE would consider them as electric furnaces)
without modifying the product envelope. Modular blower envelope
dimensions are similar, and in many cases identical, to electric
furnace dimensions as a result. In addition, the final test procedure
requires an electric resistance heat kit to be installed in modular
blowers to produce a temperature rise allowing for calculation of
airflow for the rating metric, FER. The test configurations for
electric furnaces and modular blowers are almost identical as a result.
In turn, the FER values for an electric furnace and modular blower with
no other design difference other than the presence of an electric
resistance heat kit are expected to be approximately equivalent. On the
other hand, the coils typically included in CAC/HP blower-coil units
are larger than heat resistance kits. Consequently, blower-coil unit
envelope dimensions are different than modular blower dimensions, which
impacts fan performance. CAC/HP blower-coil unit design, as it relates
to fan performance, cannot be compared to modular blower design for
this reason. The final test procedure does not include methods for
deriving an FER value for CAC/HP blower-coil units. Furthermore, the
coil and envelope dimension differences mentioned would preclude the
circulation fan performance of a CAC/HP blower-coil unit from being
deemed equivalent to an otherwise similarly-designed modular blower. In
addition, modular blowers and electric furnaces are product
configurations installed in the field. DOE doubts that a CAC/HP blower-
coil unit with the coil removed would be offered by manufacturers or
purchased and installed in the field. Regarding the criticism of its
definition of ``modular blower,'' DOE recognizes that the definition
for ``modular blower'' as set forth at 10 CFR part 430, subpart B,
appendix AA may be confusing because it does not explicitly state that
a modular blower does not include an indoor refrigerant coil, only that
it does not provide heating or cooling. An ``indoor unit,'' on the
other hand, is defined at 10 CFR 430.2 as containing a ``coil.'' This
notice modifies the definition of ``modular blower'' to explicitly
exclude products that contain an indoor refrigerant coil in order to
eliminate ambiguity between the two definitions.
ACEEE, Earthjustice, and CA IOU stated that DOE's decision to
exclude products such as CAC/HP and hydronic air handlers is
inappropriate and in conflict with DOE's interpretation of the
statutory language. These interested parties also commented that DOE
does not provide a justification for its decision to exclude products
for which DOE claims to have authority to set energy conservation
standards. (ACEEE, No. 94 at pp. 1-2, 4; and CA IOU, No. 106 at pp. 1,
2) According to Earthjustice, DOE's decision to exclude products for
which it claims authority to cover represents a failure to carry out
EPCA's command to adopt ``standards for electricity used for purposes
of circulating air through ductwork'' and does not comply with the
statute's requirement that standards ``shall be designed to achieve the
maximum improvement in energy efficiency'' that is ``technologically
feasible and economically justified.'' (42 U.S.C. 6295(o)(2)(A).
Earthjustice adds that EPCA authorizes DOE not to prescribe an amended
or new standard for a type or class of covered product in three
situations: (1) The standard will eliminate certain product features
from the market; (2) the standard will not result in significant
conservation of energy or is not technologically feasible or
economically justified; or (3) for certain products, test procedures
have not been established. (42 U.S.C. 6295(o)(3) and (4)). Earthjustice
states that DOE has failed to show that the products it is not
addressing in this rule meet those criteria. (Earthjustice, No. 101 at
p. 1).
ASAP, et al. encouraged DOE to adopt standards and/or test
procedure changes to drive improved efficiency of furnace fans that are
part of single-package and blower-coil central air conditioners and
heat pumps in the future. According to ASAP, et al., CA IOU and ACEEE,
the operating conditions and metrics used in the DOE test procedures
for CAC/HP (i.e., SEER and HSPF) are insufficient for representing
furnace fan performance in the field for those products. (ASAP, et al.,
No. 105 at pp. 2, 3; CA IOU, No. 106 at pp. 1, 2; and ACEEE, No. 94 at
pp. 1-2, 4). Further, ASAP, et al. are concerned that heat pump indoor
units will increasingly be installed and operated as electric furnaces
(without an outdoor unit) to avoid both the DOE standard for CAC/HP and
the standards established by this rule. ASAP, et al. added that
consumers will have greater incentive to install heat pump indoor units
to operate as electric furnaces if a heat pump indoor unit with a PSC
motor is less expensive than an electric furnace/modular blower with a
constant-torque BPM motor. (ASAP, et al., No. 105 at pp. 2, 3)
Earthjustice also identified CAC/HP blower-coil units installed without
an outdoor unit and operated as an electric furnace as a potential
loophole. (Earthjustice, No. 101 at p. 1) While ASAP, et al., stated
that they recognize that it may be too late to include furnace fans
that are part of single-package and blower-coil central air
conditioners and heat pumps in the scope of coverage in the current
rulemaking, they encourage
[[Page 38149]]
DOE to address furnace fan efficiency in these products in the future
through one of two options: (1) Amend the test procedures for central
air conditioners and heat pumps to incorporate more realistic external
static pressure values; or (2) include furnace fans that are part of
single-package and blower-coil central air conditioners and heat pumps
in a future rulemaking for furnace fans. ASAP, et al., submitted that
if DOE pursued the second option, changing the external static pressure
values in the central air conditioner and heat pump test procedures
would be less critical, because fan efficiency would be addressed
through standards for furnace fans. (ASAP, et al., No. 105 at pp. 2, 3)
CA IOU also expressed support for a separate, expedited rulemaking to
set energy conservation standards for products not addressed in this
rule. CA IOU claims that such a rule would ensure that the entire
market for furnace fans is regulated, thereby avoiding the negative
market impacts due to the prevalence of unregulated products. (CA IOU,
No. 106 at pp. 1, 2). NEEA and NPCC also expressed disappointment that
DOE is choosing to cover only two-thirds of furnace fan products by
excluding indoor blower/cool units used with split system heat pump and
air conditioning systems and hydronic air handlers, which leaves
substantial energy savings on the table. (NEEA and NPCC, No. 96 at p.
3). ACEEE estimated that approximately two quads of potential
cumulative energy savings are left uncaptured by DOE's decision to
exclude CAC/HP blower-coil units, which ACEEE claims could jeopardize
achievement of the Administration's goal of 3 billion tons of
CO2 avoided. (ACEEE, No. 94 at p. 1-2, 4). CA IOU cited
these potential energy savings as another reason that a separate,
expedited rulemaking is warranted. (CA IOU, No. 106 at pp. 1, 2).
Laclede, APGA, and AGA also recommended that DOE expand the scope of
this rule to include products such as split-system central air
conditioners, heat pump air handlers, through-the-wall air handlers,
and small-duct high-velocity air handlers that compete with the types
of natural gas furnaces covered by this rules. Each cited concerns that
DOE's decision to exclude fans used in these products could lead to
fuel switching. (Laclede, No. 89 at p. 2; APGA, No. 90 at p. 2; and
AGA, No. 110 at p. 2). Laclede believes the Department failed to
adequately explain why fans in heat pumps are excluded and to clearly
demonstrate how this exclusion serves the best interests of the
American public.
EEI, on the other hand, supports DOE's exclusion of CAC/HP blower-
coils and hydronic air handlers from this rulemaking. EEI commented
that the energy used by the fans operating in the cooling mode is part
of the calculation of SEER, EER, and HSPF. EEI explains that
manufacturers have already made design decisions that reduce the energy
usage of such fans for these systems to meet the higher air conditioner
and heat pump energy conservation standards (based on SEER and HSPF)
that took effect in 1992 and 2006, and will take effect in 2015. EEI
stated that including these fans in this rule would be a form of
``double regulation'' of the same product. (EEI, No. 87 at p. 3)
Southern Company agreed that CAC/HP fan energy is already covered by
the SEER and HSPF rating. (Southern Company, NOPR Public Meeting, No.
43 at p. 70).
As explained previously, DOE has noted the relatively broad scope
of the language of 42 U.S.C. 6295(f)(4)(D), which provides DOE
authority to regulate ``electricity used for purposes of circulating
air through duct work.'' At the present time, however, DOE is only
adopting energy conservation standards for those circulation fans that
are used in residential furnaces and modular blowers. The DOE test
procedure for furnace fans is not currently equipped to address fans
contained in central air conditioners, heat pumps, or other products,
as would be required for the adoption of standards under 42 U.S.C.
6295(o)(3). Consequently, DOE is not considering standard setting for
other products beyond the current scope of the rulemaking at this time.
2. Product Classes
DOE identified nine key product classes in the preliminary
analysis, each of which was assigned its own candidate energy
conservation standard and baseline FER. DOE identified twelve
additional product classes that represent significantly fewer shipments
and significantly less overall energy use. DOE grouped each non-key
product class with a key product class to which it is closely related
in application-specific design and internal structure (i.e., the
primary criteria used to differentiate between product classes). DOE
assigned the analytical results of each key product class to the non-
key product classes with which it is grouped because DOE expected the
energy use and incremental manufacturer production costs (MPCs) of
improving efficiency to be similar within each grouping. Table IV.1
lists the 21 preliminary analysis product classes.
Table IV.1--Preliminary Analysis Product Classes
------------------------------------------------------------------------
Key product class Additional product classes
------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas
Furnace Fan (NWG-NC).
Non-weatherized, Condensing Gas Furnace
Fan (NWG-C).
Weatherized Non-Condensing Gas Furnace Weatherized, Non-Condensing Oil
Fan (WG-NC). Furnace Fan (WO-NC).
Weatherized Electric Furnace/
Modular Blower Fan (WEF/WMB).
Mobile Home Weatherized Gas
Furnace Fan (MH-WG).
Mobile Home Weatherized Oil
Furnace Fan (MH-WO).
Mobile Home Weatherized
Electric Furnace/Modular
Blower Fan (MH-WEF/WMB).
Non-weatherized, Non-Condensing Oil Non-Weatherized, Condensing Oil
Furnace Fan (NWO-NC). Furnace Fan (NWO-C).
Mobile Home Non-Weatherized Oil
Furnace Fan (MH-NWO).
Non-weatherized Electric Furnace/
Modular Blower Fan (NWEF/NWMB).
Heat/Cool Hydronic Air Handler Fan (HAH- Heat-Only Hydronic Air Handler
HC). Fan (HAH-H).
Hydronic Air Handler Fan with
Coil (HAH-C).
Mobile Home Heat/Cool Hydronic
Air Handler Fan (MH-HAH-HC).
Mobile Home Heat-Only Hydronic
Air Handler Fan (MH-HAH-H).
Mobile Home Hydronic Air
Handler Fan with Coil (MH-HAH-
C).
Mobile Home Non-Weatherized, Non-
Condensing Gas Furnace Fan (MH-NWG-NC).
[[Page 38150]]
Mobile Home Non-Weatherized, Condensing
Gas Furnace Fan (MH-NWG-C).
Mobile Home Electric Furnace/Modular
Blower Fan (MH-EF/MB).
------------------------------------------------------------------------
Manufacturers agreed that the selected key product classes are an
accurate representation of the market. Some manufacturers disagreed
with DOE's approach to specify additional product classes within a key
product class, stating that shipment data indicates that the additional
product classes are too small to be covered.
In the NOPR, DOE agreed with manufacturers' assertion that the
additional non-key product classes represent products with few and in
many cases, no shipments. 78 FR 64082. Individual discussions with
manufacturers for the MIA confirmed this assertion. Additionally,
review of the AHRI appliance directory revealed that only two of the
additional non-key product classes have active models listed: (1)
Mobile home weatherized gas furnace fans (MH-WG) and (2) mobile home
non-weatherized oil furnace fans (MH-NWO). The number of active basic
models for MH-WG and MH-NWO are 4 and 16, respectively. For this
reason, DOE proposed in the NOPR to eliminate the additional non-key
product classes except for MH-WG and MH-NWO. Due to the limited number
of basic models for MH-WG and MH-NWO, DOE did not have data to directly
analyze and establish standards for these additional product classes.
As a result, DOE proposed to reserve space to establish standards for
MH-WG and MH-NWO furnace fans in the future as sufficient data become
available. DOE also proposed to exclude hydronic air handlers from
consideration in this rulemaking, thereby further reducing the number
of product classes addressed in the NOPR to 10. 78 FR 64082. Table IV.2
includes a list of the revised set of product classes for residential
furnace fans used in the NOPR.
DOE did not receive comment or additional information on the
proposed product classes, thus, DOE is not making changes to the
product classes in this Final Rule. Table IV.2 includes a list of the
product classes for residential furnace fans used in the Final Rule.
Table IV.2--Product Classes for Residential Furnace Fans
------------------------------------------------------------------------
Product class
-------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan (NWG-NC)
Non-Weatherized, Condensing Gas Furnace Fan (NWG-C)
Weatherized Non-Condensing Gas Furnace Fan (WG-NC)
Non-Weatherized, Non-Condensing Oil Furnace Fan (NWO-NC)
Non-Weatherized Electric Furnace/Modular Blower Fan (NWEF/NWMB)
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan (MH-NWG-NC)
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan (MH-NWG-C)
Mobile Home Electric Furnace/Modular Blower Fan (MH-EF/MB)
Mobile Home Weatherized Gas Furnace Fan (MH-WG)
Mobile Home Non-Weatherized Oil Furnace Fan (MH-NWO)
------------------------------------------------------------------------
3. Technology Options
In the preliminary analysis, DOE considered seven technology
options that would be expected to improve the energy efficiency of
furnace fans: (1) Fan housing and airflow path design modifications;
(2) high-efficiency fan motors (in some cases paired with multi-stage
or modulating heating controls); (3) inverter-driven permanent-split
capacitor (PSC) fan motors; (4) backward-inclined impellers; (5)
constant-airflow brushless permanent magnet (BPM) motor control relays;
(6) toroidal transformers; and (7) switching mode power supplies. In
the NOPR, DOE revised its proposed scope of coverage to no longer
address hydronic air handlers, the only furnace fan product class for
which standby mode and off mode energy consumption is not already fully
accounted for in the DOE energy conservation standards rulemakings for
residential furnaces and residential CAC and HPs. 76 FR 37408 (June 27,
2011); 76 FR 67037 (Oct. 31, 2011). Consequently, the standby mode and
off mode technology options (options 5 through 7 in the list above) are
no longer applicable. In addition, DOE found that multi-staging and
modulating heating controls can also improve FER, so DOE evaluated
multi-staging and modulating heating controls as a separate technology
option for the NOPR. 78 FR 64083.
DOE did not receive comment or additional information regarding the
evaluated technology options, so DOE did not make any changes to the
list of technology options identified in the NOPR. The resultant list
of technology options identified to be evaluated in the screening
analysis before consideration in the engineering analysis for the Final
Rule include: (1) Fan housing and airflow path design modifications;
(2) inverter-driven PSC fan motors; (3) high-efficiency fan motors; (4)
multi-staging and modulating heating controls; and (5) backward-
inclined impellers. Each identified technology option is discussed
below and in more detail in chapter 3 of the Final Rule TSD.
Fan Housing and Airflow Path Design Improvements
The preliminary analysis identified fan housing and airflow path
design modifications as potential technology options for improving the
energy efficiency of furnace fans. Optimizing the shape of the inlet
cone \18\ of the fan housing, minimizing gaps between the impeller and
fan housing inlet, and optimizing cut-off location and manufacturing
tolerances were identified as enhancements to a fan
[[Page 38151]]
housing that could improve efficiency. Separately, modification of
elements in the airflow path, such as the heat exchanger, could reduce
internal static pressure and as a result, reduce energy consumption.
Manufacturer input was requested to determine the use and
practicability of these potential technology options.
---------------------------------------------------------------------------
\18\ The inlet cone is the opening of the furnace fan housing
through which return air enters the housing. The inlet cone is
typically curved inward, forming a cone-like shape around the
perimeter of the opening, to provide a smooth surface to direct air
from outside the housing to inside the housing and into the
impeller.
---------------------------------------------------------------------------
Interested parties expressed support for DOE's consideration of the
aerodynamics of furnace fan cabinets in its initial analysis of
technology options. In particular, ASAP cited a 2003 GE study \19\ that
quantified energy savings produced by modifying fan housing as
justification for its inclusion as an option. ACEEE, et al. also cited
a Lawrence Berkeley National Laboratory (LBNL) study \20\ that linked
changes in efficiency to modifying the clearance between fan housing
and an air handler cabinet wall. Ingersoll Rand stated that there are
proprietary fan housing designs on the market that already improve
mechanical efficiency by 10-20 percent at a cost much lower than the
cost to implement high-efficiency motors or make changes to the
impeller and its tolerances. 78 FR 64083.
---------------------------------------------------------------------------
\19\ Wiegman, Herman, Final Report for the Variable Speed
Integrated Intelligent HVAC Blower (2003) (Available at: https://www.osti.gov/bridge/servlets/purl/835010-GyvYDi/native/835010.pdf).
\20\ Walker, I.S, State-of-the-art in Residential and Small
Commercial Air Handler Performance (2005) LBNL 57330 (Available at:
https://epb.lbl.gov/publications/pdf/lbnl-57330plus.pdf).
---------------------------------------------------------------------------
DOE is aware of the studies cited by ASAP and ACEEE, as well as the
proprietary housing design mentioned by Ingersoll Rand. For the NOPR,
DOE decided to include fan housing design modifications as a technology
to be evaluated further in the screening analysis because of these
indications that each could improve fan efficiency. 78 FR 64083.
Many interested parties requested that DOE keep airflow path design
as a technology option. Manufacturers stated that improving airflow
path design, like modifying fan housing, is highly cost-effective when
compared to other enhancements. Similar to the fan housing design
modifications, DOE decided to include airflow path design as a
technology option to be evaluated further in the screening analysis as
a result of these claims of potential fan efficiency improvement. 78 FR
64083. DOE believes including airflow path design is appropriate
because of its potential to impact fan efficiency. Airflow path design
will impact the rating metric, FER, because the DOE test procedure
requires the furnace fan to be tested as it is factory-installed in the
HVAC product.
DOE did not receive comment or additional information on fan
housing about including airflow path design improvements as a
technology option, thus, DOE is including these as technologies to be
evaluated further in the screening analysis. Chapter 3 of the Final
Rule TSD provides more technical detail regarding fan housing and
airflow path design modifications and how these measures could reduce
furnace fan energy consumption.
Inverter Controls for PSC Motors
In the preliminary analysis, DOE identified inverter-driven PSC
motors as a technology option. DOE is aware of a series of non-
weatherized gas furnaces with inverter-driven PSC furnace fan motors
that was once commercially available. DOE has determined that inverter
controls provide efficiency improvement by offering additional
intermediate airflow-control settings and a wider range of airflow-
control settings (i.e., lower turndown ratio) than conventional PSC
controls. The additional airflow-control settings and range enable the
furnace fan to better match demand. Publically-available performance
data for the series of furnaces using inverter-driven PSCs demonstrate
that the use of this technology results in reduced FER values compared
to baseline PSC furnace fans. Consequently, DOE considered inverter-
driven PSCs as a technologically feasible option for reducing furnace
fan energy consumption.
Manufacturers were opposed to listing inverter-driven PSCs as a
viable technology option. Manufacturers commented that there are
alternate, more cost-effective solutions to reduce energy consumption
for air-moving systems, such as airflow path design or ECM (referred to
herein by DOE as a ``constant-airflow BPM motor'') technology. 78 FR
64084.
For the NOPR analysis, DOE recognized manufacturers' concerns with
the cost-effectiveness of inverter-driven PSC fan motors. However, DOE
decided to include inverter-driven PSC motors as a technology option to
be evaluated further in the screening analysis due to their potential
to reduce furnace fan energy consumption. 78 FR 64084.
DOE did not receive comment or additional information on including
inverter controls for PSC motors as a technology option, thus, DOE is
including this technology option in the Final Rule. DOE evaluates in
the engineering analysis the cost-effectiveness of all energy-saving
technology options that are not screened out. Chapter 3 of the Final
Rule TSD provides a more detailed discussion of inverter-driven PSC
furnace fan motors.
High-Efficiency Motors
In the preliminary analysis, DOE identified four motor types that
are typically used in furnace fan assemblies: (1) PSC motors; (2) PSC
motors that have more than 3 airflow-control settings and sometimes
improved materials (hereinafter referred to as ``improved PSC''
motors); (3) constant-torque BPM motors (often referred to as ``X13
motors''); and (4) constant-airflow BPM motors (often referred to as
``ECMs'').\21\ DOE finds that furnace fans using high-efficiency motor
technology options operate more efficiently than furnace fans using
baseline PSC motors by:
---------------------------------------------------------------------------
\21\ ``ECM'' and ``X13'' refer to the constant-airflow and
constant torque (respectively) BPM offerings of a specific motor
manufacturer. Throughout this notice, DOE will refer to these
technologies using generic terms, which are introduced in the list
above. However, DOE's summaries of interested-party submitted
comments include the terminology used by the interested party when
referring to motor technologies.
---------------------------------------------------------------------------
Functioning more efficiently at a given operating
condition;
Maintaining efficiency throughout the expected operating
range; and
Achieving a lower turndown ratio \22\ (i.e., ratio of
airflow in lowest setting to airflow in highest setting).
---------------------------------------------------------------------------
\22\ A lower turndown ratio can significantly improve furnace
fan efficiency because fan input power has a cubic relationship with
airflow.
---------------------------------------------------------------------------
Ingersoll Rand commented that a PSC motor will use less energy at
higher static pressures, while an ECM increases energy use as static
pressure rises. Ingersoll Rand stated that as a result, understanding
the impact of switching to an ECM at higher static pressures may
confuse the consumer. (Ingersoll Rand, PA Public Meeting Transcript,
No. 43 at p. 67)
For the NOPR analysis, DOE stated that it is aware that consumers
may be confused when BPM motors (referred to as ECMs by Ingersoll Rand
above) consume more energy than PSC motors at higher static pressures,
because consumers expect BPM motors to consume less energy than PSC
motors under the same operating conditions. In general, input power to
the fan motor increases as static pressure increases to provide a given
airflow (i.e., the fan motor has to work harder in the face of
increased resistance to provide a desired amount of air).\23\ DOE
agreed with Ingersoll Rand that as static pressure increases, input
power to a PSC-driven furnace fan will decrease, which is
[[Page 38152]]
seemingly contradictory to the principle described above. DOE found
that input power to a PSC-driven furnace fan decreases because the
airflow provided by the fan decreases as static pressure rises (i.e.,
the fan does not have to work as hard in the face of increased
resistance because the fan is not providing as much air). 78 FR 64084.
Input power to a constant-airflow BPM motor-driven furnace fan, on the
other hand, will increase as static pressure rises because the BPM
motor-driven fan is designed to maintain the desired level of airflow.
Recognizing that this behavior could complicate comparing the relative
performance of these motor technologies, DOE's rating metric, FER, is
normalized by airflow to result in ratings that are in units of watts/
cfm. DOE believed that a comparison using a watts/cfm metric will
mitigate confusion by accurately reflecting that even though a
constant-airflow BPM motor is consuming more power at higher statics,
it is also providing more airflow, which is useful to the consumer.
---------------------------------------------------------------------------
\23\ See chapter 3 of the TSD for more details regarding fan
operation.
---------------------------------------------------------------------------
As detailed in the NOPR, interested parties recognized the benefits
provided by constant-torque and constant-airflow BPM motors. Interested
parties also agreed that the BPM motor variations (i.e., constant-
torque and constant-airflow) and inverter-driven PSC motors generally
have lower turndown ratios than a three-speed PSC motor. 78 FR 64084.
Table IV.3 contains the turndown ratio estimates supplied publicly by
interested parties. Manufacturers generally provided similar feedback
during interviews.
Table IV.3--Interested Party Estimated Fan Motor Turndown Ratios
----------------------------------------------------------------------------------------------------------------
Wave chopper Constant- Constant-
Interested party PSC controller PSC torque ECM airflow ECM
----------------------------------------------------------------------------------------------------------------
NMC (NMC, No. 60 at p. 1)....................... 0.45 0.36 0.45 0.20
Goodman (Goodman, No. 50 at p. 2)............... 0.70-0.75 .............. 0.40-0.50 0.25-0.35
Rheem (Rheem, No. 54 at p. 6)................... 0.60 .............. 0.30 0.20
----------------------------------------------------------------------------------------------------------------
Overall, comments regarding high-efficiency motor turndown ratio
validated DOE's expectation that lower turndowns are associated with
improved PSCs, inverter-driven PSCs, and BPM motor variations. These
motors consume significantly less energy over a typical residential
furnace fan operating range. DOE disagreed with Lennox that including
constant circulation as part of FER would ``artificially'' inflate the
performance of BPM motors compared to PSC motors, because DOE concluded
that there is non-trivial use of this mode by consumers. 78 FR 64085.
As part of the test procedure rulemaking, DOE estimated that on
average, consumers operate furnace fans in constant-circulation mode
400 hours annually. This estimate is used to weight fan constant-
circulation electrical energy consumption in FER. Excluding this mode
from the rating metric would underestimate the potential efficiency
improvements of technology options, such as BPM motors, that could
reduce fan electrical consumption while performing this function. A
detailed discussion of DOE's estimate for national average constant-
circulation furnace fan operating hours can be found in the test
procedure NOPR. 77 FR 28674, 28682 (May 15, 2012). DOE did not revise
these estimates in the test procedure Final Rule published on January
3, 2014. 79 FR 499.
DOE did not receive comment or additional information on including
high-efficiency motors as a technology option, thus, DOE is including
this technology option in the Final Rule. DOE evaluates in the
engineering analysis the cost-effectiveness of all energy-saving
technology options that are not screened out. Chapter 3 of the Final
Rule TSD provides a more detailed discussion of high-efficiency furnace
fan motors.
Multi-Stage or Modulating Heating Controls
In the preliminary analysis (77 FR 40530 (July 10, 2012)), DOE
identified two-stage and modulating heating controls (hereinafter
collectively referred to as ``multi-stage'' controls) as a method of
reducing residential furnace fan energy consumption. Multi-stage
furnaces typically operate at lower heat input rates and, in turn, a
lower airflow-control setting for extended periods of time compared to
single-stage furnaces to heat a residence.\24\ Due to the cubic
relationship between fan input power and airflow, operating at the
reduced airflow-control setting reduces overall fan electrical energy
consumption for heating despite the extended hours. In the preliminary
analysis, DOE analyzed multi-staging controls paired with use of a
constant-airflow BPM fan motor as one technology option, because DOE
found the two to be almost exclusively used together in commercially-
available products.
---------------------------------------------------------------------------
\24\ A further discussion of multi-stage heating controls is
found in chapter 3 of the preliminary analysis TSD, which can be
found at the following web address: https://www.regulations.gov/#!documentDetail;D=EERE-2010-BT-STD-0011-0037.
---------------------------------------------------------------------------
Interested parties encouraged DOE to consider X13-level motors
applied with multi-stage furnace controls as a technology option. 78 FR
64085. During interviews, manufacturers commented that multi-stage
heating controls can be and are used regardless of motor type.
Based on comments from manufacturers, DOE recognized that multi-
stage controls can be paired with other motor types, not just constant-
airflow BPM motors. DOE agreed with interested parties that
implementing multi-stage heating controls independent of motor type
could result in residential furnace fan efficiency improvements.
Consequently, DOE decided to de-couple multi-staging controls from the
constant-airflow BPM motor technology option. Accordingly, DOE
evaluated multi-staging controls as a separate technology option for
the NOPR. 78 FR 64085.
DOE did not receive comment or additional information on multi-
staging controls as a technology option, thus, DOE is including this
technology option in the Final Rule.
Backward-Inclined Impellers
DOE determined in the preliminary analysis that using backward-
inclined impellers could lead to possible residential furnace fan
energy savings. Although limited commercial data regarding backward-
inclined impeller performance were available, DOE cited research by
General Electric (GE) that showed large improvements in efficiency were
achievable under certain operating conditions.\25\
---------------------------------------------------------------------------
\25\ Wiegman, Herman, Final Report for the Variable Speed
Integrated Intelligent HVAC Blower (2003) (Available at: https://www.osti.gov/bridge/servlets/purl/835010-GyvYDi/native/835010.pdf).
---------------------------------------------------------------------------
Interested parties disagreed with the DOE's findings, stating that
literature indicates there are varying degrees of performance
improvement when
[[Page 38153]]
backward-inclined impellers are used in place of forward-curved
impellers. 78 FR 64085. Ebm-papst, a company that provides custom air-
movement products, offered a diverging opinion from most manufacturers
regarding the energy-saving potential of backward-inclined impellers.
That company retrofitted several HVAC products with furnace fan
assemblies that incorporated backward-inclined impellers without
increasing cabinet size and tested them. Depending on the application
and the external static pressure load (typically 0.5 in. w.c. to 1 in.
w.c.), ebm-papst found that the backward-inclined impeller achieved
input power reductions from 15-30 percent. (ebm-papst Inc., No. 52 at
p. 1).
DOE recognized that backward-inclined impellers may not be more
efficient than forward-curved impellers under all operating conditions
and that there may be considerable constraints to implementation.
However, the GE prototype and ebm-papst prototype both demonstrate that
significant energy consumption reduction is achievable at some points
within the range of residential furnace fan operation. For this reason,
DOE included backward-inclined impellers as a technology option in the
NOPR. 78 FR 64086.
DOE did not receive additional comment or information on including
backward-inclined impellers as a technology option. Thus, DOE included
backward-inclined impellers as a technology to be evaluated further in
the screening analysis for the Final Rule.
B. Screening Analysis
DOE uses the following four screening criteria to determine which
technology options are suitable for further consideration in an energy
conservation standards rulemaking:
1. Technological feasibility. Technologies that are not
incorporated in commercial products or in working prototypes will not
be considered further.
2. Practicability to manufacture, install, and service. If it is
determined that mass production and reliable installation and servicing
of a technology in commercial products could not be achieved on the
scale necessary to serve the relevant market at the time of the
compliance date of the standard, then that technology will not be
considered further.
3. Impacts on product utility or product availability. If it is
determined that a technology would have significant adverse impact on
the utility of the product to significant subgroups of consumers or
would result in the unavailability of any covered product type with
performance characteristics (including reliability), features, sizes,
capacities, and volumes that are substantially the same as products
generally available in the United States at the time, it will not be
considered further.
4. Adverse impacts on health or safety. If it is determined that a
technology would have significant adverse impacts on health or safety,
it will not be considered further.
(10 CFR part 430, subpart C, appendix A, 4(a)(4) and 5(b))
In sum, if DOE determines that a technology, or a combination of
technologies, fails to meet one or more of the above four criteria, it
will be screened out from further consideration in the engineering
analysis. The reasons for eliminating any technology are discussed
below.
The subsequent sections include comments from interested parties
pertinent to the screening criteria, DOE's evaluation of each
technology option against the screening analysis criteria, and whether
DOE determined that a technology option should be excluded (``screened
out'') based on the screening criteria.
1. Screened-Out Technologies
DOE screened out fan housing and airflow path design improvements
in the preliminary analysis. DOE had little quantitative data to
correlate specific fan housing alterations with efficiency
improvements. Additionally, DOE anticipated that any improvements to
airflow path design that would result in fan efficiency improvement
would require an increase in furnace fan cabinet size or negatively
impact heat exchanger performance, thereby compromising the
practicability to manufacture or reducing utility to consumers.
In response to the preliminary analysis, interested parties stated
many concerns associated with modifying airflow path designs to reduce
residential furnace fan electrical energy consumption, namely, that
airflow path design modifications would likely require increasing HVAC
product size. Manufacturers explained that increasing HVAC products
size would have adverse impacts on practicability to install and
consumer utility, because the furnace fan market is predominantly a
replacement market. 78 FR 64086.
For the NOPR, DOE did not receive or find additional quantitative
data that shows a measurable increase in fan efficiency as a result of
a specific fan housing or airflow path design modification. Even after
individual discussion with manufacturers, DOE was not able to identify
a case in which fan housing or airflow path design modifications could
lead to potential fan energy savings without increasing the size of the
HVAC product or compromising thermal performance or safety. DOE is
aware of the impacts on thermal efficiency and furnace fan performance
of the additional heat exchanger in condensing furnaces. As discussed
in section III.B, DOE accounted for these impacts in its criteria for
differentiating product classes. In addition, DOE concurs with
manufacturers' observations that an increase in envelope size would
adversely impact practicability to manufacture and install, as well as
product utility. Accordingly, DOE decided to screen out fan housing and
airflow path design modifications in the NOPR. 78 FR 64086.
DOE did not receive additional comment or information regarding fan
housing and airflow path design modifications in response to the NOPR.
Thus, DOE determined to screen out fan housing and airflow path design
modifications in the Final Rule.
2. Remaining Technologies
Through a review of each technology, DOE found that all of the
other identified technologies met all four screening criteria to be
examined further in DOE's analysis. 78 FR 64087. In summary, DOE did
not screen out the following technology options: (1) Inverter-driven
PSC fan motors; (2) high-efficiency fan motors; (3) multi-stage heating
controls; and (4) backward-inclined impellers. DOE understands that all
of these technology options are technologically feasible, given that
the evaluated technologies are being used (or have been used) in
commercially-available products or working prototypes. These
technologies all incorporate materials and components that are
commercially available in today's supply markets for the residential
furnace fans that are the subject of this Final Rule. Therefore, DOE
believes all of the efficiency levels evaluated in this notice are
technologically feasible. For additional details, please see chapter 4
of the Final Rule TSD.
Interested parties, however, voiced concerns regarding these
screening criteria as they apply to BPM fan motors and backward-
inclined impellers in previous phases of this rulemaking. DOE
summarizes and addresses these concerns in the sections immediately
below. DOE did not receive public comments relevant to the screening
[[Page 38154]]
analysis criteria for the other remaining technology options.
High-Efficiency Motors
In response to the preliminary analysis, manufacturers stated that
there are a limited number of ECM motor suppliers to furnace fan
manufacturers, and that it is a proprietary technology. Manufacturers
also stated that no alternative ECM exists at the scale of Regal Beloit
ECMs and that limiting PSC applicability would reduce product
flexibility.
Motor manufacturers disagreed with residential furnace fan
manufacturers, claiming that there is more than just a single motor
manufacturer offering ECM technology. Motor manufacturers also
supported DOE's assumption that after implementation of furnace fan
efficiency standards, brushless permanent magnet motor technologies
will become increasingly available over time. DOE discovered during
interviews with manufacturers that there are multiple suppliers of BPM
motors. DOE also found further evidence that some manufacturers
purchase BPM motors from multiple suppliers. EEI stated that the
expiration of Regal Beloit ECM patents around 2020 may increase the
availability of this motor type while decreasing cost. (EEI, PA Public
Meeting Transcript, No. 43 at p. 127)
In the preliminary analysis, DOE requested comment as to whether
manufacturers could alternatively develop BPM motor controls in-house
when using high-efficiency motors from other, non-Regal Beloit,
suppliers. Most furnace fan manufacturers claimed that development of
in-house controls for BPM motors is not an option. 78 FR 64087.
While DOE recognizes that Regal Beloit possesses a number of
patents in the BPM motor space, other motor manufacturers (e.g., Broad
Ocean, ebm-papbst, and NMC) also offer BPM models. Additionally, DOE is
aware that in years past, residential furnace fans paired with
constant-airflow BPM motors accounted for 30 percent of the market.
While DOE estimates that constant-airflow BPM motors represent only 10-
15 percent of the current furnace fan market, the manufacturing
capability to meet BPM motor demand exists. Thus, DOE continues to
expect that BPM motor technology is currently available from more than
one source and will become increasingly available to residential
furnace fan manufacturers. 78 FR 64087.
Also in response to the preliminary analysis, some fan
manufacturers expressed concern that high-efficiency motor reliance on
rare earth metals would impact supply. However, DOE is aware of high-
efficiency motors that do not contain rare earth materials. DOE is also
confident, after discussions with manufacturers, that if BPM motors are
adopted as a means to meet a future residential furnace fan energy
conservation standard, manufacturers would have a number of cost- and
performance-competitive suppliers from which to choose who have
available, or could rapidly develop, control systems independently of
the motor manufacturer. 78 FR 64087.
DOE did not receive additional comment or information in response
to the NOPR about high-efficiency motors related to the screening
criteria. Thus DOE included high-efficiency motors as a technology
option in the engineering analysis.
Backward-Inclined Impellers
In response to the preliminary analysis, furnace fan manufacturers
stated that backward-inclined impellers must have larger diameter and
operate at higher speed than forward-curve impellors in order to attain
equivalent performance (i.e., flow and pressure rise). However, ebm-
papst stated that they retrofitted existing equipment with backward-
inclined impellers, which only required making minor changes to the
airflow path within the equipment. 78 FR 64088.
Manufacturers were also concerned with the potential impacts that
backward-inclined impellers could have on heat exchanger temperatures.
Some commenters also argued that backward-inclined impellers may affect
furnace fan utility, because the noise produced by this impeller type
may limit product application. Utilities claimed that a backward-
inclined impeller, in combination with increased fan motor speeds to
achieve higher efficiency, leads to amplified noise levels. 78 FR
64088.
For the NOPR, DOE found that there are multiple approaches to
implementing backward-inclined impellers to reduce furnace fan energy
consumption. DOE recognized that one approach is to use a backward-
inclined impeller that is larger than a standard forward-curved
impeller, which may lead to larger HVAC products. Another approach is
to pair the backward-inclined impeller with a motor that operates at
increased RPM. Ebm-papst tests show a significant potential to reduce
fan electrical energy consumption for a backward-inclined impeller
assembly that uses existing motor technology at higher RPMs and is
implemented in existing HVAC products (i.e., no increase in product
size required). Ebm-papst does not believe that achieving higher RPMs
with existing motor technology is an obstacle for implementing this
technology. DOE believed that this prototype represented a backward-
inclined implementation approach that could achieve fan energy savings
while avoiding the negative impacts listed by manufacturers.
Consequently, DOE decided not to screen out the backward-inclined
impeller technology option in the NOPR. 78 FR 64088.
DOE did not receive additional comment or information about
backward-inclined impellers related to the screening criteria. Thus,
DOE decided not to screen out backward-inclined impellers in the Final
Rule.
C. Engineering Analysis
In the engineering analysis (corresponding to chapter 5 of the
Final Rule TSD), DOE establishes the relationship between the
manufacturer selling price (MSP) and improved residential furnace fan
efficiency. This relationship serves as the basis for cost-benefit
calculations for individual consumers, manufacturers, and the Nation.
DOE typically structures the engineering analysis using one of three
approaches: (1) Design option; (2) efficiency level; or (3) reverse
engineering (or cost-assessment). The design-option approach involves
adding the estimated cost and efficiency of various efficiency-
improving design changes to the baseline to model different levels of
efficiency. The efficiency-level approach uses estimates of cost and
efficiency at discrete levels of efficiency from publicly-available
information, and information gathered in manufacturer interviews that
is supplemented and verified through technology reviews. The reverse
engineering approach involves testing products for efficiency and
determining cost from a detailed bill of materials derived from reverse
engineering representative products. The efficiency values range from
that of a least-efficient furnace fan sold today (i.e., the baseline)
to the maximum technologically feasible efficiency level. For each
efficiency level examined, DOE determines the MSP; this relationship is
referred to as a cost-efficiency curve.
1. Efficiency Levels
In this rulemaking, DOE used an efficiency-level approach in
conjunction with a design-option approach to identify incremental
improvements in efficiency for each product class. An efficiency-level
approach enabled DOE to identify incremental improvements in efficiency
for efficiency-improving
[[Page 38155]]
technologies that furnace fan manufacturers already incorporate in
commercially-available models. A design-option approach enabled DOE to
model incremental improvements in efficiency for technologies that are
not commercially available in residential furnace fan applications. In
combination with these approaches, DOE used a cost-assessment approach
to determine the manufacturing production cost (MPC) at each efficiency
level identified for analysis. This methodology estimates the
incremental cost of increasing product efficiency. When analyzing the
cost of each efficiency level, the MPC is not for the entire HVAC
product, because furnace fans are a component of the HVAC product in
which they are integrated. The MPC includes costs only for the
components of the HVAC product that impact FER.
Baseline
During the preliminary analysis, DOE selected baseline units
typical of the least-efficient furnace fans used in commercially-
available, residential HVAC models that have a large number of annual
shipments. This sets the starting point for analyzing potential
technologies that provide energy efficiency improvements. Additional
details on the selection of baseline units may be found in chapter 5 of
the Final Rule TSD. DOE compared the FER at higher energy efficiency
levels to the FER of the baseline unit and compared baseline MPCs to
the MPCs at higher efficiency levels.
DOE reviewed FER values that it calculated using test data and
performance information from publicly-available product literature to
determine baseline FER ratings. Table IV.4 presents the baseline FER
values identified in the preliminary analysis for each product class.
Table IV.4--Preliminary Analysis Baseline FER
----------------------------------------------------------------------------------------------------------------
Product class FER (W/1,000 cfm)
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan............ 380
Non-Weatherized, Condensing Gas Furnace Fan................ 393
Weatherized, Non-Condensing Gas Furnace Fan................ 333
Non-Weatherized, Non-Condensing Oil Furnace Fan............ 333
Electric Furnace/Modular Blower Fan........................ 312
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan 295
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan.... 319
Mobile Home Electric Furnace/Modular Blower Fan............ 243
----------------------------------------------------------------------------------------------------------------
In response to the preliminary analysis, manufacturers asserted
that the baseline FER values presented were not representative of the
furnace fans in the least-efficient residential HVAC models offered for
sale today. Some manufacturers also requested that DOE alter FER to
better reflect unit capacity. Specifically, some manufacturers stated
that residential furnace fans having a larger capacity also have higher
FERs and recommended that DOE adjust baseline FER values to include the
largest-capacity fan within a product class. 78 FR 64089.
In the NOPR, DOE evaluated the feedback it received and used the
data provided by interested parties to generate new FER values and to
revise its baseline, intermediate efficiency levels, and max-tech FER
estimates. DOE's revisions included FER results for furnace fan models
that span the capacity range of residential products. After reviewing
all of the available FER values based on new data, DOE concluded that
FER can best be represented as a linear function of airflow capacity
(i.e., a first constant added to airflow multiplied by a second
constant). The slope of the linear fit characterizes the change in FER
for each unit of airflow capacity increase, and the y-intercept
represents where the FER line intersects the y-axis (where airflow
capacity is theoretically zero). For the NOPR, DOE proposed to use such
linear functions to represent FER for the different efficiency levels
of the different product classes. 78 FR 64089.
Table IV.5 shows the revised FER baseline efficiency levels
estimates that DOE used for the NOPR.
Table IV.5--NOPR Baseline FER Estimates
----------------------------------------------------------------------------------------------------------------
Product class FER* (W/1,000 cfm)
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan............ FER = 0.057 x QMax + 362.
Non-Weatherized, Condensing Gas Furnace Fan................ FER = 0.057 x QMax + 395.
Weatherized Non-Condensing Gas Furnace Fan................. FER = 0.057 x QMax + 271.
Non-Weatherized, Non-Condensing Oil Furnace Fan............ FER = 0.057 x QMax + 336.
Electric Furnace/Modular Blower Fan........................ FER = 0.057 x QMax + 331.
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan FER = 0.057 x QMax + 271.
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan.... FER = 0.057 x QMax + 293.
Mobile Home Electric Furnace/Modular Blower Fan............ FER = 0.057 x QMax + 211.
Mobile Home Weatherized Gas Furnace Fan.................... Reserved.
Mobile Home Non-Weatherized Oil Furnace Fan................ Reserved.
----------------------------------------------------------------------------------------------------------------
*QMax is the airflow, in cfm, at the maximum airflow-control setting measured using the proposed DOE test
procedure at the time of the ECS NOPR publication. 78 FR 19606, 19627 (April 2, 2013).
Manufacturers stated that the baseline FER values presented in the
NOPR need to be re-evaluated to determine the appropriate baseline.
Because the test procedure was not finalized at the time of the ECS
NOPR publication, Lennox believes that assumptions were made by DOE to
determine the baseline from other sources, leading to overstated energy
savings and misleading conclusions. (Lennox, No. 100 at p. 3) Goodman
believes that the NOPR
[[Page 38156]]
baseline values are too high. Goodman initially commented that baseline
values were too low for the preliminary analysis. Based on the product
testing per the April 2013 test procedure SNOPR, Goodman feels the
increased values for baseline FER are too high, and should be closer
(but still higher than) the original TSD estimated values. (Goodman,
No. 102 at p. 8) Morrison, NEEA, and NPPC also commented that because
there was no finalized test procedure at the time the ECS NOPR was
published, DOE should not be using test data from public literature to
generate FER values. (Morrison, No. 91 at p. 124; NEEA, NPCC, No. 96 at
p. 2) Ingersoll-Rand echoed Lennox's and Morrison's comments, stating
that it is difficult to get furnace fan power data from public
literature, and that DOE's baseline FER values are over-estimated.
(Ingersoll-Rand, No. 91 at pp. 110-111) Rheem and Lennox questioned
whether the efficiency levels are based off of FER or the average
annual auxiliary electrical energy consumption (Eae).
(Rheem, No. 83 at p. 4; Lennox, No. 100 at p. 3) Lennox and Ingersoll-
Rand also commented specifically about the baseline FER for weatherized
gas furnaces, citing a dramatic difference in DOE's baseline
performance level as compared to their product offerings. Additionally,
when the performance improvement factors are applied to DOE's baseline,
the result is a very aggressive mandated increase in performance.
(Lennox, No. 100 at p. 3; Ingersoll-Rand, No. 107 at p. 4) AHRI also
commented on the FER for weatherized gas furnaces, stating that the FER
values for weatherized gas furnace fans and non-weatherized condensing
gas furnace fans should be the same because the test procedure is the
same for both products, except for a difference in ESP. AHRI explained
the difference in ESP accounts for the cooling coil within the
weatherized gas furnace, therefore, in effect, the furnace fan
assemblies for weatherized and non-weatherized gas furnaces are subject
to the same ESP. (AHRI, No. 91 at pp. 127-129) Goodman agreed with AHRI
that weatherized gas furnace fans should have the save efficiency
levels as non-weatherized gas, non-condensing furnace fans. (Goodman,
No. 102 at p. 3)
DOE did not use Eae as an input for the engineering
analysis. All efficiency levels considered by DOE throughout this
rulemaking, including the baseline, are based on FER data, not
Eae. DOE used Eae as a proxy for FER to evaluate
market-wide energy performance of furnace fans in the market and
technology assessment only. Further description of this
characterization is found in chapter 3 of the Final Rule TSD. DOE
disagrees with Lennox, Morrison, NEEA, and NPPC that FER values that
DOE generated prior to the final test procedure or based on public
literature should not be considered in this Final Rule. DOE outlines in
detail in section III.A the reasons that FER data from previous stages
of the rulemaking and public literature are relevant. Section III.A
also explains how DOE's changes to the test procedure between the test
procedure SNOPR and final rule should not result in significant
differences in FER values for many covered products. Thus, DOE
disagrees with Ingersoll Rand, Lennox, Goodman, and Morrison's claims
that, in the absence of a final test procedure or because of changes in
the final test procedure, DOE used unreliable information to calculate
FER and model efficiency levels for the NOPR. Regardless, DOE agrees
with interested parties that DOE should re-update its NOPR baseline
equations based on new data. DOE received some baseline FER data from
interested parties in response to the NOPR. As discussed in section
III.A, DOE also conducted testing prior to and during the development
of the test procedure final rule that generated a broad enough set of
results to enable DOE to derive FER values that are consistent with the
requirements of the final test procedure. DOE used this new baseline
FER data to revise its baseline equations.
DOE investigated interested party claims that DOE's proposed
baseline equation for weatherized gas furnace fans did not match
manufacturer performance estimates. DOE did not receive additional
baseline FER data for weatherized gas furnace fans. However, DOE did
derive additional FER values from data from specification sheets and
testing of weatherized gas furnaces at higher efficiency levels (i.e.,
weatherized gas furnaces that use constant-torque and constant-airflow
BPM motors). DOE was able to collect more reliable FER data for more
efficient weatherized gas furnace fans than for baseline weatherized
gas furnace fans. Consequently, DOE estimated the weatherized gas
furnace fan baseline FER by multiplying the market and capacity
weighted FER value for weatherized gas furnace fans with constant-
airflow BPM motor and multi-staging by the expected percent increase in
FER (i.e., the inverse of the expected percent reduction in FER for
constant-airflow BPM and multi-staging). DOE then developed a
conversion factor from the non-weatherized, non-condensing gas furnace
fan baseline FER to generate a y-intercept for the weatherized non-
condensing gas furnace fan baseline FER equation. This approach
significantly increased DOE's estimated baseline FER for weatherized
non-condensing gas furnace fans to a level consistent with the revised
baseline for non-weatherized, condensing gas furnace fans. Even though
they are not identical, DOE concludes that the approach described is
appropriate based on interested party feedback. The airflow path design
of weatherized non-condensing gas and non-weatherized, condensing gas
furnaces are very different, which impacts furnace fan performance,
accounting for the slightly different FER equations.
DOE also received comments from interested parties regarding the
slopes in the NOPR FER equations. Rheem and Lennox commented that the
slope characterizing the relationship between FER and airflow capacity
is too flat, adding that higher-capacity models are space constrained,
and their FER values do not meet the proposed FER levels in the NOPR.
(Rheem, No. 83 at p. 8; Lennox, No. 100 at p. 6) Ingersoll-Rand
commented that for condensing furnaces and furnaces using improved PSC
motors and multi-staging controls, FER tends to decrease as capacity
increases, creating a negative slope. (Ingersoll-Rand, No. 91 at pp.
110-111; Ingersoll-Rand, No. 107 at pp. 3-4) Ingersoll-Rand also
commented that even though FER values for furnace fans with PSC motors
follow a linear trend, FER values for furnace fans that use BPM motor
technologies do not because they react differently to changes in static
pressure (Ingersoll-Rand, No. 107 at p. 5) ACEEE, Goodman, and Mortex
questioned whether a linear slope is the best way to characterize the
relationship between FER and airflow capacity. AHRI and Goodman added
that there is a cubic relationship between fan input power and airflow,
thus, a non-linear slope may be more appropriate. (ACEEE, No. 94 at p.
3; Goodman, No. 102 at p. 13; Mortex, No. 104 at p. 3; AHRI, No. 98 at
p. 3)
In response to interested party comments, DOE recalculated FER
versus airflow capacity slopes using new data from baseline series for
both non-weatherized, non-condensing gas furnace fans and non-
weatherized, condensing gas furnace fans. DOE found that the average
baseline slope increased dramatically from 0.057 to 0.081. DOE is aware
that some instances of furnace series models will not match DOE's slope
analysis results. The data, that DOE has, shows a positive slope when
characterizing the relationship between
[[Page 38157]]
FER and airflow capacity. Furthermore, DOE did not determine that a
linear fit was the best fit statistically. DOE believes a linear fit is
the best representation of furnace fan performance given the level of
data available. DOE finds that linear fits result in a distribution of
efficiency levels that match the distribution of furnace fan
performance by technology option used. Additionally, a cubic trend-line
does not account for changes in furnace envelope size, heat exchanger
size, furnace fan outlet size, and other factors the affect furnace fan
performance. Using a cubic trend-line would only be appropriate if
these other factors were held constant. DOE finds that input power to a
PSC-driven furnace fan decreases because the airflow provided by the
fan decreases as static pressure rises (i.e., the fan does not have to
work as hard in the face of increased resistance because the fan is not
providing as much air). Input power to a constant-airflow BPM motor-
driven furnace fan, on the other hand, will increase as static pressure
rises because the BPM motor-driven fan is designed to maintain the
desired level of airflow. Recognizing that this behavior could
complicate comparing the relative performance of these motor
technologies, DOE's rating metric, FER, is normalized by airflow to
result in ratings that are in units of watts/cfm.
Table IV.5 shows the revised FER baseline efficiency levels
estimates that DOE used for the Final Rule.
Table IV.6--Final Rule Baseline FER Estimates
----------------------------------------------------------------------------------------------------------------
Product class FER * (W/1,000 cfm)
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan............ FER = 0.081 x QMax + 335.
Non-Weatherized, Condensing Gas Furnace Fan................ FER = 0.081 x QMax + 358.
Weatherized Non-Condensing Gas Furnace Fan................. FER = 0.081 x QMax + 365.
Non-Weatherized, Non-Condensing Oil Furnace Fan............ FER = 0.081 x QMax + 433.
Electric Furnace/Modular Blower Fan........................ FER = 0.081 x QMax + 304.
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan FER = 0.081 x QMax + 252.
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan.... FER = 0.081 x QMax + 273.
Mobile Home Electric Furnace/Modular Blower Fan............ FER = 0.081 x QMax + 186.
Mobile Home Weatherized Gas Furnace Fan.................... Reserved.
Mobile Home Non-Weatherized Oil Furnace Fan................ Reserved.
----------------------------------------------------------------------------------------------------------------
* QMax is the airflow, in cfm, at the maximum airflow-control setting measured using the final DOE test
procedure. 79 FR 499, 524 (January 3, 2014).
Percent Reduction in FER
For the preliminary analysis, DOE determined average FER reductions
for each efficiency level for a subset of key product classes and
applied these reductions to all product classes. DOE found from
manufacturer feedback and its review of publically-available product
literature that manufacturers use similar furnace fan components and
follow a similar technology path to improving efficiency across all
product classes. DOE does not expect the percent reduction in FER
associated with each design option, whether commercially available or
prototype, to differ across product classes as a result. Table IV.7
includes DOE's preliminary analysis estimates for the percent reduction
in FER from baseline for each efficiency level.
Table IV.7--Preliminary Analysis Estimates for Percent Reduction in FER From Baseline for Each Efficiency Level
----------------------------------------------------------------------------------------------------------------
Percent
reduction in
Efficiency level (EL) Design option FER from
baseline
----------------------------------------------------------------------------------------------------------------
1............................................. Improved PSC.................................... 2
2............................................. Inverter-Driven PSC............................. 10
3............................................. Constant-Torque BPM Motor....................... 45
4............................................. Constant-Airflow BPM Motor + Multi-Staging...... 59
5............................................. Premium Constant-Airflow BPM Motor + Multi- * 63
Staging + Backward-Inclined Impeller.
----------------------------------------------------------------------------------------------------------------
* DOE estimates that implementing a backward-inclined impeller at EL 5 results in a 10% reduction in FER from EL
4. This is equivalent to a reduction of 4% percent of the baseline FER. The total percent reduction in FER
from baseline for EL 5 includes the 59% reduction from EL 4 and the 4% net reduction of the backward-inclined
impeller for a total percent reduction of 63% from baseline.
Interested parties questioned DOE's estimates for the FER reduction
for high-efficiency motors. Specifically, interested parties noted that
DOE underestimated the efficiency gain of improved PSC motors over
standard PSC motors, and overestimated the efficiency improvement of
BPM motor technology options. 78 FR 64090.
For the NOPR, DOE reviewed its estimates of percent reduction in
FER from baseline for each efficiency level based on interested party
feedback. In addition to the comments summarized above, interested
parties also provided FER values for higher-efficiency products in
manufacturer interviews. DOE used these data to revise its percent
reduction estimates. Table IV.8 shows DOE's revised estimates for the
percent reduction in FER for each efficiency level that DOE used in the
NOPR. For a given product class, DOE applied the percent reductions
below to both the slope and y-intercept of the baseline FER equation to
generate FER equations to represent each efficiency level above
baseline.
[[Page 38158]]
Table IV.8--NOPR Estimates for Percent Reduction in FER From Baseline for Each Efficiency Level
----------------------------------------------------------------------------------------------------------------
Percent
reduction in
Efficiency level (EL) Design option FER from
baseline
----------------------------------------------------------------------------------------------------------------
1............................................. Improved PSC.................................... 10
2............................................. Inverter-Driven PSC............................. 25
3............................................. Constant-Torque BPM Motor....................... 42
4............................................. Constant-Torque BPM Motor and Multi-Staging..... 50
5............................................. Constant-Airflow BPM Motor and Multi-Staging.... 53
6............................................. Premium Constant-Airflow BPM Motor and Multi- * 57
Staging + Backward-Inclined Impeller.
----------------------------------------------------------------------------------------------------------------
* DOE estimates that implementing a backward-inclined impeller at EL 6 results in a 10% reduction in FER from EL
5. This is equivalent to a 4% percent reduction in FER from baseline. The total percent reduction in FER from
baseline for EL 6 includes the 53% reduction from EL 5 and the 4% net reduction from the backward-inclined
impeller for a total percent reduction of 57% from baseline.
Note that EL 4 in the table above was a newly proposed efficiency
level in the NOPR. As discussed in section IV.A.3, DOE analyzed multi-
staging as a separate technology option. For the NOPR, DOE also
evaluated a separate efficiency level representing applying multi-
staging to a furnace fan with a constant-torque BPM motor. 78 FR 64091.
In response to the NOPR, AHRI asked if DOE considered pairing PSC
motors with multi-stage furnace controls in its analysis. (AHRI, No. 91
at p. 310) While DOE did gather data for and investigated PSC-driven
furnace fans in multi-stage products, DOE did not include this
combination as an efficiency level for the Final Rule. In the
engineering analysis, DOE assesses technology options in order of cost-
effectiveness. DOE finds that constant-torque BPM motors are more cost-
effective than PSC motors with multi-staging. While the cost of multi-
staging for each motor type is approximately the same, multi-staging
results in significantly less energy savings when used with a PSC
motor. DOE expects this is the result of a limited turndown ratio as
discussed in section III.A.4.
Interested parties commented on the NOPR percent reductions in FER
from the baseline and resulting efficiency level equations. Nidec
stated that the percent reductions do not reflect furnace fan
performance improvements when using higher-efficiency PSC motors.
(Nidec, No. 91 at p. 147) Many manufacturers stated that the proposed
efficiency levels are not consistent with product performance using the
varying design options. Rheem, Allied Air, Daikin, Lennox, and
Ingersoll-Rand stated that only their multi-staging furnace lines that
use constant-airflow BPM motors would meet the proposed standard level.
(Rheem, No, 83 at pp. 1-2; Allied Air, No. 91 at p. 105; Daikin, No. 91
at p. 105; Lennox, No. 100 at p. 5; Ingersoll-Rand, No. 91 at pp. 102-
103) Goodman and AHRI submitted similar comments stating that there are
existing products that use the design options specified within TSL 5
that will not even meet the proposed energy conservation standards.
(AHRI, No. 98 at p. 3; and Goodman, No 102 at pp. 4 and 7) In a joint
comment submitted by Appliance Standards Awareness Project (ASAP),
Alliance to Save Energy (ASE), National Consumer Law Center (NCLC), and
National Resources Defense Council (NRDC) and in a separate comment
submitted by California Investor-Owned Utilities (CA IOUs), interested
parties recommended that DOE conduct additional testing of furnace fans
with constant-torque BPM motors with multi-staging controls to verify
the accuracy of the proposed FER standard level equations, and to
ensure that the majority of products containing constant-torque BPM
motors with multi-staging controls meet the standard. (ASAP, et al.,
No. 105 at p. 2; CA IOU, No. 106 at p. 3)
DOE carefully considered the feedback received from interested
parties on the percent reductions in FER from baseline that the
Department proposed in the NOPR. DOE shares manufacturers' concerns
that their products are not meeting the levels proposed in the NOPR
despite those models using the technologies (or more efficient
technologies) on which those levels are based. DOE used data provided
by interested parties, conducted additional testing using the final DOE
test procedure, and gathered data from additional product specification
sheets to generate new FER values. DOE used this new FER data to revise
its estimates of percent reduction in FER from baseline for each
efficiency level. In response to Nidec, DOE did analyze an efficiency
level associated with improved PSC motors. However, DOE did not receive
and could not gather any new FER data with which to revise its
estimated percent reduction in FER from baseline for this technology.
Using the revised estimates of percent reduction in FER from baseline,
DOE revised its FER equations. Then, for the product classes with the
highest shipments, DOE assessed how many models for which DOE has an
FER value met the revised EL 4. DOE finds that over 90% of the non-
weatherized, non-condensing gas, non-weatherized, condensing gas and
weatherized non-condensing gas furnace fans for which DOE has FER
values that use constant-torque BPM motors and multi-staging meet the
revised EL 4. DOE finds that many models in those product classes for
which DOE has FER data that use constant-torque BPM motors without
multi-staging would also meet the revised EL 4. DOE feels that the
percentage of models that meet the revised EL 4 show that the Final
Rule efficiency levels are reflective of the performance of the
technologies on which they are based.
Ingersoll Rand stated that percent reduction in FER from the
baseline should not be constant across all capacities for products
using constant-torque BPM motor technologies. Specifically, Ingersoll-
Rand noted that efficiency improvements with this technology decrease
with increasing furnace capacity, and that at high airflow capacities,
there is little or no difference in FER values between furnace fans
using improved PSC motors and those using constant-torque BPM motors.
(Ingersoll-Rand, No. 107 at p. 5) Additionally, Ingersoll-Rand stated
that wider cabinets for furnaces with more cooling capacity but the
same heating input will have lower FERs. (Ingersoll-Rand, NOPR Public
Meeting Transcript, No. 91 at p. 94) Ingersoll-Rand and Mortex disagree
with DOE using the same slope for FER equations for both mobile home
furnaces as well as non-mobile home furnaces. These parties cite that
there are space constraints associated with mobile home applications,
and that it is more difficult to meet the proposed standard at higher
capacities because the cabinet
[[Page 38159]]
size must remain the same. (Ingersoll-Rand, No. 91 at pp. 116-117;
Mortex, No. 91 at pp. 129-131)
DOE recognizes that percent reduction in FER from baseline for a
given technology option varies with capacity. DOE's estimates of
percent reduction in FER from baseline are based on market-weighted
averages of FER values from across the entire range of furnace fan
airflow capacities to account for this variation. As discussed above,
DOE finds that constant percent reductions in FER from baseline result
in a distribution of efficiency levels that match the distribution of
furnace fan performance by technology option used across the entire
range of furnace fan airflow capacities. Thus, DOE believes that a
constant percent reduction in FER from baseline across all airflow
capacities is appropriate. DOE is also aware that in some instances FER
may decrease for furnaces with higher cooling capacities but the same
heating input. DOE's analysis includes FER data for furnace fans that
have differing heating capacity to cooling capacity ratios. DOE
recognizes that these ratios indicate design differences that impact
fan performance. However, a significant majority of the models for
which DOE has FER data are meeting the ELs associated with the
technologies that they use. Of the few models that do not, DOE observes
no pattern related to the ratio of heating capacity to cooling
capacity. DOE recognizes that mobile home products are more space-
constrained than the other products covered by this standard. DOE did
not receive mobile home FER data in response to the NOPR. Despite DOE
using the same slope for mobile home product classes to characterize
the relationship between FER and airflow capacity for all product
classes, the resulting ELs for mobile home furnace fans are less
stringent than those for non-mobile home furnaces at higher capacities.
EL 4 for MH-NWG-NC and NWG-NC both have slopes of 44 FER per 1000 cfm,
for example. Thus, for an increase in airflow capacity of 1000 cfm, EL
4 allows for an increase of 44 in FER for both classes. At 1,200 cfm,
EL 4 is represented by and FER of 235 for NWG-NC and 190 for MH-NWG-NC.
An increase of 44 in FER would represent an increase in FER of
approximately 18 percent for the NWG-NC furnace fan, but an increase in
FER of approximately 23% for the MH-NWG-NC furnace fan. Consequently,
the allowable increase in FER as capacity increases is more lenient for
mobile home furnaces. DOE believes this leniency is appropriate
considering the more rigid space constraints mobile home furnaces must
meet. DOE recognizes that the same variation in stringency occurs as a
result of DOE's method for establishing baseline FER equations using
conversion factors as described in more detail in chapter 5 of the
Final Rule TSD. However, the difference in FER values between mobile
home and non-mobile home furnace fans is much greater than the
difference between FER values amongst non-mobile home furnace fans. The
variation in stringency for non-mobile home products is minimal as a
result.
Table IV.9 shows DOE's revised estimates for the percent reduction
in FER for each efficiency level that DOE used in the Final Rule
analyses.
Table IV.9--Final Rule Estimates for Percent Reduction in FER from Baseline for Each Efficiency Level
----------------------------------------------------------------------------------------------------------------
Percent
reduction in
Efficiency level (EL) Design option FER from
baseline
----------------------------------------------------------------------------------------------------------------
1............................................. Improved PSC.................................... 12
2............................................. Inverter-Driven PSC............................. 25
3............................................. Constant-Torque BPM Motor....................... 41
4............................................. Constant-Torque BPM Motor and Multi-Staging..... 46
5............................................. Constant-Airflow BPM Motor and Multi-Staging.... 51
6............................................. Premium Constant-Airflow BPM Motor and Multi- * 56
Staging + Backward-Inclined Impeller.
----------------------------------------------------------------------------------------------------------------
* DOE estimates that implementing a backward-inclined impeller at EL 6 results in a 10% reduction in FER from EL
5. This is equivalent to a 5% percent reduction in FER from baseline. The total percent reduction in FER from
baseline for EL 6 includes the 51% reduction from EL 5 and the 5% net reduction from the backward-inclined
impeller for a total percent reduction of 56% from baseline.
Ingersoll Rand provided a significant amount of FER data in its
written comment to support its statements. (Ingersoll Rand, No. 107 at
pp. 3, 12-16) DOE appreciates this information and included these FER
values in its revision of the engineering analysis to account for the
furnace fan performance behaviors described by Ingersoll Rand.
2. Manufacturer Production Cost (MPC)
In the preliminary analysis, DOE estimated the manufacturer
production cost associated with each efficiency level to characterize
the cost-efficiency relationship of improving furnace fan performance.
The MPC estimates are not for the entire HVAC product because furnace
fans are a component of the HVAC product in which they are integrated.
The MPC estimates includes costs only for the components of the HVAC
product that impact FER, which DOE considered to be the:
Fan motor and integrated controls;
Primary control board (PCB);
Multi-staging components;
Impeller;
Fan housing; and
Components used to direct or guide airflow.
DOE separated the proposed product classes into high-volume and
low-volume product classes and generated high-volume and low-volume MPC
estimates to account for the increased purchasing power of high-volume
manufacturers.\26\
---------------------------------------------------------------------------
\26\ High-volume and low-volume product classes are discussed
further in chapter 5 of the Final Rule TSD.
---------------------------------------------------------------------------
Production Volume Impacts on MPC
In response to the preliminary analysis, manufacturers commented
that they use different manufacturing processes for high and low-volume
products. In the NOPR analysis, DOE found that 94 percent of the MPC
for furnace fans is attributed to materials (included purchased parts
like fan motors), which are not impacted by process differences. DOE's
estimates also already accounted for process differences between
manufacturers for high-volume and low-volume products. The products
that DOE evaluated to support calculation of MPC included furnace fans
from various manufacturers, including both high-volume and low-volume
models. Observed process differences are reflected in the bills of
materials for
[[Page 38160]]
those products. DOE believed that its approach to distinguish between
high-volume and low-volume product classes accounts for the expected
difference in MPC between high-volume and low-volume product classes.
78 FR 64091.
DOE did not receive comment or additional information on production
volume impacts on MPC, thus, DOE is taking the same approach to
distinguish between high-volume and low-volume product classes in the
Final Rule.
Inverter-Driven PSC Costs
In the preliminary analysis, DOE estimated that the MPC of inverter
control for a PSC motor is $10-$12, depending on production volume.
Interested parties commented that DOE was underestimating the cost of
adding an inverter to a PSC motor, and questioned if DOE's cost
estimate was for wave chopper technology and not inverters. In the
NOPR, DOE stated that the preliminary analysis estimate for the MPC of
an inverter-driven PSC was indeed based on a wave chopper drive. DOE
found that more sophisticated and costly inverters are required to
achieve the efficiencies reflected in DOE's analysis. Consequently, DOE
adjusted its cost estimate for PSC inverter technology. DOE gathered
more information about the cost of inverters that are suited for
improving furnace fan efficiency. In addition to receiving cost
estimates during manufacturer interviews, DOE also reviewed its cost
estimates for inverter drives used in other residential applications,
such as clothes washers. DOE found that $30 for high-volume products
and $42.29 for low-volume products are better estimates of the MPC for
inverters used to drive PSC furnace fan motors. Accordingly, DOE
updated those values for the NOPR. 78 FR 64091-64092.
DOE did not receive comment or additional information on cost
estimates for inverter-driven PSC motors, thus, DOE is not making
changes to the MPC estimates for inverters used to drive PSC furnace
fan motors in the Final Rule.
Furnace Fan Motor MPC
In response to the preliminary analysis, manufacturers stated that
DOE underestimated the incremental MPC to implement high-efficiency
motors in HVAC products, other than oil furnaces. Most manufacturers
stated that the cost increase to switch from PSCs to more-efficient
motor technologies was at least twice that of the DOE's estimate. Based
upon the input received from interested parties, DOE adjusted its motor
cost estimates in the NOPR analysis. In general, DOE increased its
estimates by approximately 10 to 15 percent, which is consistent with
the feedback DOE received. 78 FR 64092.
Goodman stated that DOE significantly underestimated the costs of
the increasing levels of fan motor cost. (Goodman, No. 102 at p. 9)
Lennox stated that DOE underestimated the total cost of furnace fans
with BPM motor technology by 10 to 30 percent, therefore, the
incremental costs are underestimated by 20 to 120 percent. (Lennox, No.
100 at p. 6) Conversely, ACEEE commented that DOE has a well-
established record of over-estimating the cost of complying with
standards, thus, DOE's cost estimates should be discounted to further
improve the economics of advanced technology options. (ACEEE, No. 94 at
p. 3) Rheem questioned if the DOE motor cost estimates included power
factor correction filters for BPM motors, as those can cost $10 to $20.
(Rheem, No. 91 at p. 165)
DOE recognizes that BPM motor use contributes to concerns regarding
total harmonic distortion. However, the use of power factor correction
filters for BPM motor technologies is currently not required under
federal regulations. The DOE cost estimates reflect what is currently
available on the market, thus, the added cost of filters for BPM motor
technologies is not included in DOE's MPC estimates for BPM motors. DOE
believes the motor MPC estimates presented in the NOPR are
representative of current motor costs. Thus, DOE is keeping the same
furnace fan motor cost estimates presented in the NOPR for the Final
Rule analysis. Details regarding DOE's MPC estimates are provided in
chapter 5 of the Final Rule TSD.
Motor Control Costs
In the preliminary analysis, DOE estimated that the MPC of the
primary control board (PCB) increases with each conversion to a more-
efficient motor type (i.e., from PSC to constant-torque BPM motor and
from constant-torque to constant-airflow BPM motor). Manufacturers
confirmed that higher-efficiency motors and modulating motors require
more sophisticated and costly controls. DOE also received feedback
regarding the cost of the PCBs associated with each motor type during
manufacturer interviews. In general, manufacturers commented that the
PCBs used with constant-torque BPM motors are more costly. However,
other manufacturer interview participants stated that the MPC of the
PCB used with these motors should be equivalent or even less expensive
than the PCBs used with PSC motors. 78 FR 64092.
In the NOPR, DOE agreed with interested parties that the MPC of the
PCB needed for a constant-airflow BPM motor is higher than for the PCB
paired with a PSC motor. DOE estimated that the MPC of a PCB paired
with a constant-airflow BPM motor is roughly twice as much as for a PCB
paired with a constant-torque BPM motor or PSC. DOE also agreed with
the interested parties that stated that the MPC for a PCB paired with a
constant-torque BPM motor is equivalent to that of a PCB needed for a
PSC motor. DOE revised its analysis to reflect this assumption in the
NOPR as a result.
DOE did not receive comment or additional information on motor
control costs, thus, DOE is not making changes to this in the Final
Rule.
Backward-Inclined Impeller MPC
Interested parties commented that DOE's preliminary analysis
estimate for the incremental MPC associated with implementing a
backward-inclined impeller, in combination with a premium constant-
airflow BPM motor and multi-staging, is too low. Manufacturers also
commented that tighter tolerances and increased impeller diameter lead
to increased material costs, as well as increased costs associated with
motor mount structure and reverse forming fabrication processes.
During the NOPR, DOE reviewed its manufacturer production cost
estimates for the backward-inclined impeller technology option based on
interested party comments. During manufacturer interviews, some
manufacturers reiterated or echoed that DOE's estimated MPC for
backward-inclined impellers is too low, but they did not provide
quantification of the total MPC of backward-inclined impellers or the
incremental MPC associated with the changes needed to implement them.
Other manufacturers did quantify the MPC of backward-inclined impeller
solutions and their estimates were consistent with DOE's preliminary
analysis estimate. Consequently, DOE did not modify its preliminary
analysis estimated MPC for backward-inclined impellers in the NOPR. 78
FR 64092.
In response to the NOPR, Mortex questioned whether the price
differential between backward-inclined impellers manufactured at high
volume and those manufactured at low volume should be greater than
DOE's estimate of 32 cents. (Mortex, No. 91 at p. 163)
DOE reviewed its manufacturer production cost estimates for the
backward-inclined impeller technology option based on interested party
comments. DOE did not receive any
[[Page 38161]]
quantification of the total MPC of backward-inclined impellers or the
incremental MPC associated with the changes needed to implement them.
Consequently, DOE did not modify its NOPR estimated MPC for backward-
inclined impellers in the Final Rule. Regardless, DOE finds that EL 6,
which represents use of a backward-inclined impeller, is not
economically justified. Modifying the MPC estimate for this technology
would not impact the standard set by this Final Rule as a result.
Other Components
In response to the MPCs presented in the NOPR, Goodman commented
that there are likely additional components for the furnace that may
need to be added if significant changes to the blower system are
implemented. For example, improving air moving efficiency may require
an increase in cabinet size, or the addition of internal baffling to
direct airflow over the heat exchanger. None of these additional
components or modifications were accounted for in the furnace fan MPC.
(Goodman, No. 102 at p. 13)
As discussed in section III.B.1 and chapter 4 of the Final Rule
TSD, DOE did not include housing design modifications in the
engineering analysis. Thus, DOE did not develop cost estimates for
housing design modifications. DOE recognizes that the airflow path
design of the HVAC product in which the furnace fan is integrated
impacts efficiency. DOE anticipates that modifying the size of the
cabinet and the geometry of the heat exchanger(s) would be the primary
considerations for improving airflow path design. Alterations to the
design and configuration of internal components, such as the heat
exchanger, could impact the thermal performance of the HVAC product,
potentially reducing or eliminating product availability for certain
applications. While DOE did not consider airflow path design as a
technology option, as described in section III.B.1, DOE did account for
the components used to direct or guide airflow in the MPC estimates.
D. Markups Analysis
DOE uses manufacturer-to-consumer markups to convert the
manufacturer selling price estimates from the engineering analysis to
consumer prices, which are then used in the LCC and PBP analysis and in
the manufacturer impact analysis. Before developing markups, DOE
defines key market participants and identifies distribution channels.
Generally, the furnace distribution chain (which is relevant to the
residential furnace fan distribution chain) includes distributors,
dealers, general contractors, mechanical contractors, installers, and
builders. For the markups analysis, DOE combined mechanical
contractors, dealers, and installers in a single category labeled
``mechanical contractors,'' because these terms are used
interchangeably by the industry. Because builders serve the same
function in the HVAC market as general contractors, DOE included
builders in the ``general contractors'' category.
DOE used the same distribution channels for furnace fans as it used
for furnaces in the recent energy conservation standards rulemaking for
those products. DOE believes that this is an appropriate approach,
because the vast majority of the furnace fans covered in this
rulemaking is a component of a furnace. Manufactured housing furnace
fans in new construction have a separate distribution channel in which
the furnace and fan go directly from the furnace manufacturer to the
producer of mobile homes. DOE has concluded that there is insufficient
evidence of a replacement market for furnace fans to establish a
separate distribution channel on that basis.
DOE develops baseline and incremental markups to transform the
manufacturer selling price into a consumer product price. DOE uses the
baseline markups, which cover all of a distributor's or contractor's
costs, to determine the sales price of baseline models. Incremental
markups are separate coefficients that DOE applies to reflect the
incremental cost of higher-efficiency models.
Ingersoll Rand stated that the incremental markup percentages do
not represent real life practices and are too low. It commented that
once the new rule goes into effect, the more expensive furnaces will
become the baseline and will need to be marked up appropriately for
manufacturers, distributors, and dealers to remain viable. (Ingersoll
Rand, No. 107 at p. 8) However, the commenter provided no data to
support its expectation of how the actors respond in terms of pricing
when confronted with more-stringent energy conservation standards.
DOE acknowledges that detailed information on actual distributor
and contractor practices would be helpful in evaluating their markups
on furnaces. In the absence of such information, DOE has concluded that
its approach, which is consistent with expected business behavior in
competitive markets, is reasonable to apply. If the cost of goods sold
increases due to efficiency standards, DOE continues to assume that
markups would decline slightly, leaving profit unchanged, and, thus, it
uses lower markups on the incremental costs of higher-efficiency
products.
Goodman stated that lower markups on incremental costs of higher-
efficiency products is an invalid practice because manufacturers will
attempt to have higher margin dollars to offset overall lower volumes.
(Goodman, No. 102 at p. 9) For the LCC and NIA analyses, DOE does not
use a lower markup on the incremental manufacturer selling price of
higher-efficiency products. Instead, it assumes that manufacturers are
able to maintain existing average markups in response to new standards.
The MIA considers different markup scenarios for manufacturers (see
section IV.J.2.b).
E. Energy Use Analysis
The purpose of the energy use analysis is to determine the annual
energy consumption of residential furnace fans in representative U.S.
homes and to assess the energy savings potential of increased furnace
fan efficiency. In general, DOE estimated the annual energy consumption
of furnace fans at specified energy efficiency levels across a range of
climate zones. The annual energy consumption includes the electricity
use by the fan, as well as the change in natural gas, liquid petroleum
gas (LPG), electricity, or oil use for heat production as result of the
change in the amount of useful heat provided to the conditioned space
as a result of the furnace fan. The annual energy consumption of
furnace fans is used in subsequent analyses, including the LCC and PBP
analysis and the national impact analysis.
DOE used the existing DOE test procedures for furnaces and air
conditioners to estimate heating and cooling mode operating hours for
the furnace fan. The power consumption of the furnace fan is determined
using the individual sample housing unit operating conditions (the
pressure and airflow) at which a particular furnace fan will operate
when performing heating, cooling, and constant-circulation functions.
The methodology and the data are fully described in chapter 7 of the
final rule TSD.
DOE used the Energy Information Administration's (EIA) Residential
Energy Consumption Survey (RECS) \27\ to establish a sample of
households using furnace fans for each furnace fan
[[Page 38162]]
product class. RECS data provide information on the age of furnaces
with furnace fans, as well as heating and cooling energy use in each
household. The survey also includes household characteristics such as
the physical characteristics of housing units, household demographics,
information about other heating and cooling products, fuels used,
energy consumption and expenditures, and other relevant data. DOE uses
the household samples not only to determine furnace fan annual energy
consumption, but also as the basis for conducting the LCC and PBP
analysis.
---------------------------------------------------------------------------
\27\ Energy Information Administration, 2009 Residential Energy
Consumption Survey (Available at: https://www.eia.gov/consumption/residential/data/2009/index.cfm?view=consumption).
---------------------------------------------------------------------------
DOE used RECS 2009 \28\ heating and cooling energy use data to
determine heating and cooling operating hours. DOE used data from RECS
2009, American Housing Survey (AHS) 2011,\29\ and the Census Bureau
\30\ to project household weights in 2019, which is the anticipated
compliance date of any new energy efficiency standard for residential
furnace fans. These adjustments account for housing market changes
since 2009, as well as for projected product and demographic changes.
---------------------------------------------------------------------------
\28\ See https://www.eia.gov/consumption/residential/data/2009/.
\29\ See https://www.census.gov/housing/ahs/data/national.html.
\30\ See https://www.census.gov/popest/.
---------------------------------------------------------------------------
The power consumption (and overall efficiency) of a furnace fan
depends on the speed at which the motor operates, the external static
pressure difference across the fan, and the airflow through the fan. To
calculate furnace fan electricity consumption, DOE determined the
operating conditions (the pressure and airflow) at which a particular
furnace fan will operate in each RECS housing unit when performing
heating, cooling, and constant-circulation functions. For the final
rule, DOE adjusted the furnace fan energy use estimated from RECS 2009
data to account for projected changes in heating and cooling loads due
to climate change (as projected by EIA in AEO 2013).
DOE gathered field data from available studies and research reports
to determine an appropriate distribution of external static pressure
(ESP) values. DOE compiled over 1,300 field ESP measurements from
several studies that included furnace fans in single-family and mobile
homes in different regions of the country. The average ESP value in the
cooling operating mode from these studies results in an average 0.65
in. w.c. for single-family households and 0.30 in. w.c. for mobile
homes.
Rheem stated that substitution of a BPM motor can increase the
conditioned air that is leaked to the atmosphere. (Rheem, No. 83 at p.
13) However, the commenter provided no data to support its view on
increased air leakage associated with BPM motors.
DOE agrees that if a BPM motor maintains flow in a high-resistance
duct system that has leakage, it may lead to higher duct leakage
compared to a PSC motor. However, in cases where the heating load can
be met with low air flow, the BPM motor may have lower air leakage.
Given that the magnitude of these effects is uncertain and may offset,
DOE did not include it in its analysis. DOE notes that the constant-
torque BPM motor, which meets the standards in today's final rule, may
not maintain the flow in leaky and overly-restrictive ducts, and, thus,
would be expected to have similar losses as a PSC motor.
NEEA stated that their field measurements of ESP for the past 40
years are consistent with DOE's analysis. (NEEA, No. 91 at p. 222)
Daikin stated that, from experience over the past 30 plus years, mobile
homes have higher external static pressure than the typical site-built
home in the preponderance of cases. (Daikin, No. 91 at p. 222)
The data that DOE has seen (described in appendix 7B of the final
rule TSD) do not indicate that mobile homes have higher external static
pressure. Furthermore, the HUD static pressure criteria for mobile
homes \31\ are supportive of DOE's assumptions regarding ESP.
Consequently, DOE has maintained its approach regarding ESP for this
final rule.
---------------------------------------------------------------------------
\31\ HUD for Mobile Home with comfort cooling certificate -0.3
inches WC at cooling airflow setting [Title 24 of the HUD code PART
3280--Mobile Home Construction and Safety Standards, Part
3280.715(a)(3)(ll)].
---------------------------------------------------------------------------
DOE determined furnace fan operating hours in heating mode by
calculating the furnace burner operating hours and adjusting them for
delay times between burner and fan operation. Burner operating hours
are a function of annual house heating load, furnace efficiency, and
furnace input capacity.
For the NOPR, to estimate use of constant circulation in the sample
homes, DOE evaluated the available studies, which include a 2010 survey
in Minnesota \32\ and a 2003 Wisconsin field monitoring of residential
furnaces.\33\ DOE did not use these data directly, however, because it
believes they are not representative of consumer practices for the U.S.
as a whole. In these northern States, many homes have low air
infiltration, and there is a high awareness of indoor air quality
issues, which could lead to significant use of constant circulation. To
develop appropriate assumptions for other regions, DOE modified the
data from these States using information from manufacturer product
literature (which suggests very little use in humid climates) and
consideration of climate conditions in other regions. For the NOPR, DOE
used the same assumptions for use of constant circulation as were used
in the proposed DOE test procedure for furnace fans. 77 FR 28674 (May
15, 2012). The average value that emerges is approximately 400 hours
per year. The shares of homes using the various constant-circulation
modes are presented in Table IV.10.
---------------------------------------------------------------------------
\32\ Provided in CEE, No. 22 at pp. 1-2.
\33\ Pigg, S., ``Electricity Use by New Furnaces: A Wisconsin
Field Study'' (October 2003) (Available at https://www.ecw.org/sites/default/files/230-1.pdf)
---------------------------------------------------------------------------
NEEA and NPCC commented that DOE's estimate of 400 hours per year
of continuous-circulation mode may be overly conservative, and they
disagree with stakeholders who suggest that 400 hours per year is too
high. (NEEA, NPCC, No. 32 at p. 5)
For the final rule, DOE examined a newly-released proprietary
survey that broadly evaluates the use of continuous circulation across
the U.S.\34\ This survey shows a higher number of continuous-
circulation hours than DOE used for the NOPR. DOE has concerns about
the representativeness of the data, however, because the survey only
included homeowners who had been involved in the purchase of central
HVAC equipment in the past two years. The practices of these consumers
may not accurately portray the use of continuous circulation across the
entire stock of homes with central HVAC equipment. Given the
uncertainty regarding the survey data, DOE decided that it would not be
appropriate to change the continuous-circulation hours for the final
rule.
---------------------------------------------------------------------------
\34\ Decision Analysts, 2013 American Home Comfort Study (2013)
(Available at: https://www.decisionanalyst.com/Syndicated/HomeComfort.dai).
---------------------------------------------------------------------------
Southern Company stated that if DOE is assuming a greater
percentage of variable speed fans in the future, the need for constant
circulation will be reduced. (Southern Company, No. 91 at p. 233) DOE
accounted for the reduced hours of operation during constant-
circulation mode when variable speed motors are applied (see appendix
7-C). Variable speed fans tend to increase the operating hours in
heating and cooling modes, which would result in a smaller fraction of
time in continuous-fan mode.
[[Page 38163]]
DOE also performed a sensitivity analysis to estimate the effect on
the LCC results if it assumed half as much use of constant circulation.
These results are discussed in section V.B.1 of this document.
Table IV.10--Constant-Circulation Test Procedure Assumptions Used for Furnace Fans Standards Analysis
----------------------------------------------------------------------------------------------------------------
Estimated
Assumed share of homes Estimated
average in north and share of homes
Constant-circulation fan use number of south-hot dry in south-hot
hours regions humid region
(percent) (percent)
----------------------------------------------------------------------------------------------------------------
No constant fan................................................. 0 84 97
Year-round...................................................... 7290 7 1
During heating season........................................... 1097 2 0.4
During cooling season........................................... 541 2 0.4
Other (some constant fan)....................................... 365 5 1
-----------------------------------------------
Total....................................................... .............. 100 100
----------------------------------------------------------------------------------------------------------------
Morrison stated that not all the energy used in circulation is
wasted heat because the energy consumed for circulation during the
heating season is useful energy. Morrison recommended that for a more
accurate analysis of energy use in circulation mode, DOE should split
heating and cooling hours. (Morrison, No. 108 at p. 2) DOE adjusted its
analysis so that heat generated by constant-circulation fan operation
reduces furnace heating energy use in the heating season, and in the
cooling season, it adds to the operating hours of the air conditioner.
In the NOPR, DOE recognized that the energy savings in cooling mode
from higher-efficiency furnace fans used in some higher-efficiency CAC
and heat pumps was already accounted for in the analysis related to the
energy conservation standards for those products. To avoid double-
counting, the analysis for furnace fans did not include furnace fan
electricity savings that were counted in DOE's rulemaking for CAC and
heat pump products.\35\
---------------------------------------------------------------------------
\35\ U.S. Department of Energy--Energy Efficiency & Renewable
Energy, Final Rule Technical Support Document: Energy Efficiency
Standards for Consumer Products: Central Air Conditioners, Heat
Pumps, and Furnaces (2011) (Available at: https://www.regulations.gov/#!documentDetail;D=EERE-2011-BT-STD-0011-0012).
---------------------------------------------------------------------------
Several stakeholders stated that DOE may be double-counting energy
savings in cooling mode in this rulemaking by accounting for the
central air conditioner blower output used for calculating SEER. (JCI,
No. 95 at pp. 4-5; Morrison, No. 108 at p. 2; AHRI, No. 98 at p.6;
Goodman, No. 102 at p. 5) EEI stated that a large share of the
estimated furnace fan energy savings are a result of the air
conditioner and heat pump energy efficiency standards, so some or all
of these estimated energy savings should be removed from the furnace
fan analyses. (EEI, No. 87 at p. 5)
DOE's rulemaking analysis for CAC and heat pump products included
savings from those households purchasing a CAC or heat pump at SEER 15
or above that would need to have a BPM motor-driven fan in the furnace
to achieve that efficiency level. The base-case efficiency distribution
of fans used in the current analysis includes the presence of those BPM
motor-driven fans in homes with the higher-efficiency CAC or heat
pumps. Because the energy savings from the considered fan efficiency
levels are measured relative to the base-case efficiencies, any savings
reported here for furnace fans are over and above those counted in the
CAC and heat pump rulemaking.
Morrison stated that any reduction in energy use by the fan from
this rulemaking would be a de facto improvement in SEER and an unlawful
change to the current SEER regulations. It noted that if there is no
change to SEER, then there will be no energy savings when operated in
the cooling mode. (Morrison, No. 108 at p. 2)
A reduction in energy use by the furnace fan resulting from this
rulemaking would improve the CAC operating efficiency (for homes with
both furnace and CAC), but DOE is not increasing the energy
conservation standard for CAC or requiring a change to the reported
current SEER ratings for CAC. DOE has clear and explicit statutory
authority to regulate furnace fans under 42 U.S.C. 6295(f)(4)(D), and
any related improvements to CAC efficiency would simply be an added
benefit.
Recognizing the possibility of consumers using higher-efficiency
furnace fans more than baseline furnace fans, DOE included a rebound
effect in its preliminary analysis. DOE used a 2009 program evaluation
report from Wisconsin \36\ to estimate the extent to which increased
use of constant circulation under a standard requiring BPM furnace fans
is likely to cancel out some of the savings from such a fan. The
specific assumptions are described in chapter 7 of the final rule TSD.
---------------------------------------------------------------------------
\36\ State of Wisconsin, Public Service Commission of Wisconsin,
Focus on Energy Evaluation Semiannual Report, Final (April 8, 2009)
(Available at: https://focusonenergy.com/sites/default/files/semiannualreport18monthcontractperiodfinalrevisedoctober192009_evaluationreport.pdf).
---------------------------------------------------------------------------
Commenting on the average energy use estimates reported in the
final rule TSD, EEI stated that the baseline energy use values seem to
be overstated, because baseline values reported in the market and
technology assessment are lower than what was used in following
analyses. Consequently, the estimated energy savings and energy cost
savings are overstated as well, because they are shown in the NOPR as
percentage savings based on the design options. (EEI, No. 87 at pp. 4-
5) Goodman believes that the calculated baseline values, and thus the
projected energy savings, are too high based on product testing for the
April 2013 test procedure SNOPR. (Goodman, No. 102 at p. 8)
The baseline values reported in the market and technology
assessment are based on the test procedure. The energy use analysis is
not based on test procedure conditions, but instead reflects actual
usage in the field, which is more appropriate for estimating the
impacts of higher furnace fan efficiency on consumers. Therefore, the
estimated energy savings and energy cost savings are not overstated.
JCI and AHRI stated that DOE needs to ensure that it avoids double-
counting energy consumption associated with standby mode, noting that
there is no standby mode and off mode energy use associated with
furnace fans that would
[[Page 38164]]
not already be measured by the established test procedures, because
they are integrated in the electrical systems of the HVAC products in
which they are used. (JCI, No. 95 at p. 5; AHRI, No. 98 at p. 6)
The proposed furnace fan energy rating metric would not account for
the electrical energy consumption in standby mode and off mode, because
energy consumption in those modes is already accounted for in the
energy conservation standards for residential furnaces and residential
CAC and HP. Accordingly, DOE did not include standby mode and off mode
energy use associated with furnace fans in the present analysis.
Consequently, there should not be any problems associated with double-
counting of standby mode and off mode energy consumption.
F. Life-Cycle Cost and Payback Period Analysis
In determining whether an energy conservation standard is
economically justified, DOE considers the economic impact of potential
standards on consumers. The effect of new or amended energy
conservation standards on individual consumers usually involves a
reduction in operating cost and an increase in purchase cost. DOE uses
the following two metrics to measure consumer impacts:
Life-cycle cost (LCC) is the total consumer cost of an
appliance or product, generally over the life of the appliance or
product. The LCC calculation includes total installed cost (equipment
manufacturer selling price, distribution chain markups, sales tax and
installation cost), operating costs (energy, repair, and maintenance
costs), equipment lifetime, and discount rate. Future operating costs
are discounted to the time of purchase and summed over the lifetime of
the product.
Payback period (PBP) measures the amount of time it takes
consumers to recover the assumed higher purchase price of a more
energy-efficient product through reduced operating costs. Inputs to the
payback period calculation include the installed cost to the consumer
and first-year operating costs.
DOE analyzed the net effect of potential residential furnace fan
standards on consumers by calculating the LCC and PBP for each
efficiency level for each sample household. DOE performed the LCC and
PBP analyses using a spreadsheet model combined with Crystal Ball (a
commercially-available software program used to conduct stochastic
analysis using Monte Carlo simulation and probability distributions) to
account for uncertainty and variability among the input variables
(e.g., energy prices, installation costs, and repair and maintenance
costs). It uses weighting factors to account for distributions of
shipments to different building types and States to generate LCC
savings by efficiency level. Each Monte Carlo simulation consists of
10,000 LCC and PBP calculations. The model performs each calculation
using input values that are either sampled from probability
distributions and household samples or characterized with single-point
values. The analytical results include a distribution of points showing
the range of LCC savings and PBPs for a given efficiency level relative
to the base-case efficiency forecast. The results of DOE's LCC and PBP
analysis are summarized in section IV.F and described in detail in
chapter 8 of the final rule TSD.
1. Installed Cost
The installed cost at each efficiency level is based on the product
price, distribution chain markups, sales tax, and installation cost.
The current product price comes from the engineering analysis. DOE
believes that price trends for integral horsepower electric motors are
a reasonable proxy for trends in prices of furnace fans, and for the
NOPR DOE evaluated the historic real (i.e., adjusted for inflation)
producer price index (PPI) of such motors. DOE found that this index
has been decreasing except for the last few years, when it started to
increase (see appendix 10-C of the final rule TSD). Given the
uncertainty about whether the recent trend will continue or instead
revert to the historical mean, DOE elected to use constant prices at
the most recent level as the default price assumption to project future
prices of furnace fans. 78 FR 64068, 64096 (Oct. 25, 2013).
Morrison stated that motor prices have remained flat in the last
decade because production of motors moved offshore and foreign
competitors entered the marketplace. It stated that in the coming
decades, motor prices will increase at the rate of long run prices for
commodities (e.g. copper, steel, aluminum). (Morrison, No. 108 at p. 2)
Goodman believes that it is incorrect to use constant prices at the
most recent level of motor cost, which has shown a recent increasing
trend, as the default price assumption to project future prices of
furnace fans. (Goodman, No. 102 at p. 9)
DOE continues to believe that it is unclear whether the increasing
trend in motor prices since 2004 will continue in the future. Part of
the recent growth in prices of commodities used in motors was due to
strong demand from China. Current projections envision slower growth in
China, which would likely dampen commodity prices. Given the
uncertainty, DOE continued to use constant prices at the most recent
level as the default price assumption for the final rule. For the NIA,
DOE also conducted sensitivity analysis using alternative price growth
assumptions.
Because furnace fans are installed in furnaces in the factory,
there is generally no additional installation cost at the home.
However, furnace fans that employ a constant-airflow BPM design may
require additional installation costs. DOE assumed that all constant-
airflow BPM furnace fan installations will require extra labor at
startup to check and adjust airflow.
Goodman stated that it is acceptable for relative product cost
comparison to include costs only for the components of the HVAC product
that impact FER in the manufacturing cost, but it disagrees with using
the cost of only the furnace fan portion of the furnace in the LCC,
GRIM, and other aspects of the financial analysis. The real upfront
costs for the consumer will be significantly higher (likely two to four
times more) than DOE has included in the analysis using only the
furnace fan portion. (Goodman, No. 102 at p. 9) DOE believes that the
commenter is claiming that the consumer will face higher costs when
buying a furnace because the proposed furnace fan standards would
require changes in furnace design. As discussed in section IV.B.1, DOE
screened out fan housing and airflow path design modifications from
further analysis. Accordingly, it is unlikely that significant changes
in furnace design would be required to accommodate furnace fans that
meet today's standards. Therefore, DOE concludes that using the
incremental costs of the furnace fan portion is reasonable.
2. Operating Costs
To estimate the annual energy costs for operating furnace fans at
different efficiency levels, DOE used the annual energy use results
from the energy use analysis and projections of residential energy
prices. DOE derived average monthly energy prices for a number of
geographic areas in the United States using the latest data from EIA
\37\ and monthly energy price factors that it
[[Page 38165]]
developed. Electricity and natural gas prices were adjusted using
seasonal marginal price factors to come up with monthly marginal
electricity and natural gas prices. DOE assigned an appropriate price
to each household in the sample, depending on its location.
---------------------------------------------------------------------------
\37\ U.S. Department of Energy--Energy Information
Administration, Form EIA-826 Database Monthly Electric Utility Sales
and Revenue Data, 2013. https://www.eia.doe.gov/cneaf/electricity/page/eia826.html; U.S. Department of Energy--Energy Information
Administration, Natural Gas Navigator. 2013. https://tonto.eia.doe.gov/dnav/ng/ng_pri_sum_dcu_nus_m.htm.
---------------------------------------------------------------------------
Laclede stated that using average utility rates leads to
significantly overstating consumer savings. DOE should use marginal
energy rates in its consumer energy savings calculations. (Laclede, No.
86 at p. 4) As described above, DOE did derive marginal electricity and
natural gas prices based on recent data. (For a discussion of the
development of marginal energy price factors, see appendix 8-C of the
final rule TSD). To arrive at marginal prices in future years, DOE
multiplied the current marginal prices by values in the Reference case
projection of annual average residential electricity and natural gas
price changes in EIA's AEO 2013. The price trends projected in the AEO
2013 Reference case are shown in chapter 8 of the final rule TSD. For
electricity prices, which are primarily of interest in this rulemaking,
the AEO 2013 projection shows the average residential price growing
from 0.119 $/kWh in 2020 to 0.122 $/kWh in 2030 and 0.131 $/kWh in 2040
(constant dollars).
To estimate annual maintenance costs, DOE derived labor hours and
costs for annual maintenance from RS Means data.\38\ The frequency with
which the maintenance occurs was derived from a consumer survey \39\ on
the frequency with which owners of different types of furnaces perform
maintenance.
---------------------------------------------------------------------------
\38\ RS Means Company Inc., Means Facilities Maintenance &
Repair Cost Data. 2012. Kingston, MA.
\39\ Decision Analysts, 2008 American Home Comfort Study: Online
Database Tool, 2009. Arlington, Texas. https://www.decisionanalyst.com/Syndicated/HomeComfort.dai.
---------------------------------------------------------------------------
For the NOPR, DOE used the same maintenance costs for furnace fans
at different efficiency levels. 78 FR 64096. Goodman stated that it is
invalid to assume that the maintenance costs for all efficiency levels
are the same regardless of technology, as higher technology products
will take a higher skill level of technician, and will require more
costly equipment for service than baseline products. (Goodman, No. 102
at p. 9) Allied Air stated that in shifting from a primarily single-
stage PSC market to multistage constant torque, the maintenance cost
could be two to three times current costs. (Allied Air, No. 43 at pp.
252-253)
DOE understands that furnace fans require very little maintenance,
and it did not find any evidence that there is any additional
maintenance cost associated with higher efficiency equipment. It seems
likely that the commenters are including repair costs under the term
``maintenance.'' DOE's treatment of repair costs is discussed below.
The most important element of repair costs for furnace fans is
replacement of the fan motor. For the NOPR, to estimate rates of fan
motor failure, DOE developed a distribution of fan motor lifetime
(expressed in operating hours) by motor size using data developed for
DOE's small electric motors final rule. 75 FR 10874 (March 9, 2010).
DOE then paired these data with the calculated number of annual
operating hours for each sample furnace, including constant circulation
as appropriate. DOE did not have a firm basis for quantifying whether
constant-torque BPM motors and constant-airflow BPM motors have
different failure rates than PSC motors. Thus, it used the same motor
lifetime for each fan efficiency level in terms of total operating
hours (the lifetime in terms of years is lower for constant-torque BPM
and constant-airflow BPM motors because they are more frequently used
in multi-stage heating mode). 78 FR 64097.
Rheem stated that DOE did not justify the assumption that furnace
fan motor lifetimes are equal to furnace lifetimes. (Rheem, No. 83 at
p. 4) DOE modeled overall furnace fan lifetime based on furnace
lifetimes (see discussion below), but it used the approach described
above for furnace fan motor lifetime.
Morrison stated that multi-staged BPM assemblies will have longer
operating times within a given period (to account for lower fire rates
and heat output) and therefore, all else being equal, will have a
shorter life expectancy. (Morrison, No. 108 at p. 5) DOE's approach is
consistent with the comment; a multi-staged BPM motor has a shorter
lifetime measured in years.
A number of stakeholders stated that failure rates are higher for
BPM motors than for PSC motors, leading to shorter lifetime. Rheem
stated that the PSC motor life, which it estimated to be 15 years, is
much longer than the BPM motor life. (Rheem, No. 83 at pp. 2 and 13)
Mortex stated that, based on their experience, BPM lifetime is half
that of PSC motors. (Mortex, No. 104 at p. 2) Lennox estimated that
constant-airflow BPM motors have failure rates that are 50% higher than
PSC motors at 5 and 10 years, and furnaces with constant-torque BPM
motors have failure rates that are 385% higher than PSC motors at 5 and
10 years. (Lennox, No. 100 at p. 8) Ingersoll Rand stated that its data
indicate that BPM motors fail at 2.3 times the rate of PSC motors in
the 5 to 10 year time frame. (Ingersoll Rand, No. 107 at pp. 6-7) AHRI
stated that the failure rate for a high efficiency motor is typically
higher than that of a PSC motor because the electronics added to a high
efficiency motor introduce additional failure modes associated with the
life of electronic controls in damp, very cold and very hot conditions.
AHRI has collected data from manufacturers that show that the failure
rates associated with constant-torque BPM and constant-airflow BPM
technologies are higher than PSC motors over an extended time period.
(AHRI, No. 98 at p. 7) Morrison and Ingersoll Rand cited recent data
from an AHRI survey of manufacturers that indicate failure rates at 1,
5 and 10 years are 24%, 87% and 165% greater for BPM motors than PSC
ones. (Morrison, No. 108 at p. 5, Ingersoll Rand, No. 107 at p. 6) JCI
stated that, based on an analysis of JCI's residential warranty data,
failure rates associated with constant-torque BPM and constant-airflow
BPM technologies are significantly higher than those experienced by
standard PSC motors due to the added electronic controls that are
required as part of the BPM motor designs, which are more susceptible
to failure due to power fluctuations and other factors. (JCI, No. 95 at
p. 7) Ingersoll Rand stated that repair of the electronics is not
possible for the constant-torque BPM motors available today, so an
electronics failure will result in a complete motor replacement.
(Ingersoll Rand, No. 107 at pp. 7-8)
In contrast, NEEA and NPCC believe that the NOPR analysis
assumptions may unfairly penalize BPM motors, as the Department has
insufficient data to properly estimate the frequency and nature of BPM
motor repair. (NEEA, NPCC, No. 96 at p. 5)
DOE notes that BPM motors had higher level of failure in the late
1990s and early 2000s when the electronics technologies went through
major renovations. The comments from furnace manufacturers may reflect
this past experience. For example, the cited data from an AHRI survey
of manufacturers would reflect BPM technology in the early 2000s. For
the final rule, DOE searched for more information on the lifetime of
BPM and PSC motors. This information (discussed in appendix 8-E)
suggests that BPM and PSC motors have similar lifetimes, as BPM designs
have improved over the years. While BPM motor designs could have
additional failures due to the additional controls or
[[Page 38166]]
electronics, furnace fan motor manufacturers claim longer mechanical
life for BPM designs due to better bearings and less heat generated by
inefficiency. Between now and the compliance date, future BPM motor
enhancements could further strengthen product reliability and reduce
failures. In this analysis, DOE assumes higher failures for BPM designs
due to longer operating hours (because of multi-stage operating at more
hours and more constant circulation operation of BPM motors), as well
as additional control failures. For example, DOE estimates that 43% for
BPM constant torque multi-stage designs experience failure during the
lifetime of the furnace, compared to 35% of PSC designs.
Recognizing that there exists some uncertainty regarding the
lifetime of BPM motors, DOE conducted a sensitivity analysis using
alternative assumptions, as requested in a comment by Mortex. (Mortex,
No. 43 at pp. 264-265) This analysis is described in appendix 8-E of
the final rule TSD.
For the NOPR, the replacement motor costs were based on costs
developed in the engineering analysis for each motor type, and the
labor time and unit costs were based on RS Means data.\40\ 78 FR 64097.
DOE included additional labor hours to repair constant-torque BPM and
constant-airflow BPM motors, as well as higher equipment cost for the
BPM motors. DOE assumed that when replacement is necessary, consumers
replace the failed motor with the same type of motor.
---------------------------------------------------------------------------
\40\ RS Means Company Inc., RS Means Residential Cost Data
(2012); RS Means Company Inc., Facilities Maintenance & Repair Cost
Data (2012).
---------------------------------------------------------------------------
A number of stakeholders stated that the replacement cost of BPM
motors is higher than the cost DOE used in its analysis. (Morrison, No.
108 at p. 2; Goodman, No 102 at p. 8; APGA, No. 110 at p. 3) Mortex
stated that DOE substantially underestimated BPM replacement costs,
which in its experience are 2-3 times that of a PSC. (Mortex, No. 104
at p. 2) Ingersoll Rand stated that replacement costs are significantly
underestimated for constant-torque BPM and constant-airflow BPM motors.
It added that the difference between PSC motor replacement and
constant-torque BPM motor replacement should be at least $225, and the
PSC to constant-airflow BPM difference should be at least $295.
(Ingersoll Rand, No. 107 at pp. 7-8) JCI stated that outside the
warranty periods (typically 10 years for parts), ECM motors can cost 3
to 5 times the replacement costs of PSC motors due to the complexity of
those motors and the electronic controls required to use them. (JCI,
No. 95 at p. 6)
The replacement equipment cost of BPM and PSC motors used in DOE's
LCC analysis is based on costs derived in the engineering analysis,
which DOE believes are accurate. It is possible that the stakeholders
believe that the higher BPM replacement costs are largely due to extra
labor charges by contractors. DOE determined that for a constant torque
BPM motor any such extra charges would be minimal. In the analysis for
today's final rule, on average the replacement cost is $407 for a
constant torque multi-stage BPM (EL 4) and $356 for the PSC design (EL
0).
Several stakeholders stated that the replacement cost of an
aftermarket furnace fan is 2-3 times higher than DOE's estimated
manufacturer production costs for low-volume product classes. They
added that DOE's material cost estimate of $0.00 for furnace fan
replacements is incorrect. (JCI, No. 95 at p. 6; Morrison, No. 108 at
p. 5; AHRI, No. 98 at p. 8; Lennox, No. 100 at p. 8; Unico, No. 93 at
p. 5)
DOE believes that the first comment above refers to a replacement
motor. DOE applies markups to the motor MPC, such that the cost to the
consumer is two to three times higher than the MPC. The material cost
is listed as $0.00 in the cited tables because these tables refer to
labor costs only (as stated in the table captions).
Ingersoll Rand stated that motors that fail in-warranty are not
free, as standard product warranties in the HVAC industry cover parts
only, and do not typically include labor charges, which the homeowner
must pay. (Ingersoll Rand, No. 107 at p. 7) DOE excluded labor charges
only if the consumer has a service contract or if the motor fails the
first year (which is rare).
Southern Company stated that DOE unrealistically considered
component failures as independent events rather than interdependent
ones. It stated that in actual consumer settings, rather than a lab, it
is likely that a capacitor failure will not be detected until it
results in a motor failure. (Southern Company, No. 85 at p. 3)
Undetected capacitor failure that leads to motor failure (as may occur
for PSC motors) is reflected in DOE's distribution of motor lifetimes.
3. Furnace Fan Lifetime
DOE used the same modeling for furnace fan lifetime (meaning the
life of the overall equipment not including the motor) as in the
NOPR.78 FR 64097. Chapter 8 of the final rule TSD describes the
approach. DOE used the same lifetime for furnace fans at different
efficiency levels because there are no data that indicate variation of
lifetime with efficiency. For the NOPR analysis, DOE assumed that the
lifetime for the fans installed in electric furnaces and gas furnaces
is the same.
Rheem stated that the lifetime of a residential furnace fan is
limited by the lifetime of the electronic control, and advanced
controls may shorten the lifetime of the product. (Rheem, No. 83 at pp.
6, 13) JCI stated that the repair costs for furnace fans are generally
the cost of replacing the motors used, as there are very few failures
of fan components other than the motor. (JCI, No. 95 at p. 6)
DOE believes that with current technology there are few failures of
the electronic control, as stated by JCI. DOE also expects that the
reliability of the electronic controls is likely to increase as the
technology matures. Nonetheless, DOE accounts for failure of capacitors
and motor electronic controls in its repair cost analysis.
APGA stated that 23.6 years lifetime for gas-fired furnace fans in
the LCC analysis is unrealistic, and DOE should employ more realistic
furnace fan lives based on documented motor lives. (APGA, No. 110 at p.
3) It would appear that APGA misinterpreted DOE's approach. Motor
failure, which occurs on average at around 15 years, is counted as a
repair cost. However, DOE believes that the rest of the furnace fan
would last as long as the furnace itself.
Southern Company stated that because the analysis shows at least
50% greater shipments of furnace fans than furnaces, the data seems to
indicate a shorter lifetime for furnace fans than furnaces. (Southern
Company, No. 85 at p. 3) DOE did not calculate the shipments of furnace
fans. Since furnace fans are a component of furnaces, the shipments in
the NIA analysis are limited to furnace shipments only.
4. Discount Rates
For the NOPR, DOE used distributions of discount rates based on a
variety of financial data. 78 FR 64097. For replacement furnaces, the
average rate was 5.0 percent.
Miller stated that, based on a literature review of consumer
discount rates for energy-using durables, the 3-percent and 7-percent
discount rates used in the analysis only represent high-income
households; other consumers may use much higher discount rates.
Consumers with higher discount rates--including median-income
Americans, low-income Americans, and the elderly--are much less likely
to benefit from higher efficiency furnace fans. (Miller, No. 79 at pp.
10-13)
[[Page 38167]]
DOE uses 3-percent and 7-percent discount rates to measure net
consumer benefits from energy efficiency standards from a national
perspective (see section IV.H). DOE recognizes that a wide range of
discount rates may be appropriate for consumers, and thus it uses
distributions of discount rates when it evaluates consumer impacts in
the LCC analysis. For the final rule, DOE developed specific
distributions of discount rates for each of six consumer income groups.
Chapter 8 of the final rule TSD describes the approach. The estimated
impacts of today's standards on low-income households are discussed in
section V.B.1.\41\
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\41\ The comment refers to high discount rates based on studies
of implicit consumer discount rates using the purchase of energy-
using durables (such as air conditioners, dishwashers, and
refrigerators) to measure consumer time preferences. While these
studies of implicit consumer discount rates provide a way of
characterizing consumer behavior, they do not necessarily measure
consumer time preferences. What appears to be low valuation of
future energy cost savings from higher-efficiency appliances instead
may be partially a result of lack of information on the magnitude of
savings or inability to evaluate the available information.
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5. Compliance Date
In the NOPR, DOE proposed a 5-year compliance date for residential
furnace fan standards. 78 FR 64103. A number of stakeholders encouraged
DOE to adopt a three-year period between the final rule publication and
the compliance date rather than the five years proposed in the NOPR.
(ACEEE, No. 94 p. 6; NEEP, No. 109 at p. 2; Earthjustice, No. 101 at p.
3; CA IOU, No. 106 at p. 3; Joint Advocates, No. 105 at p. 4; NEEA,
NPCC, No. 96 at p. 3) ACEEE, CA IOU, the Joint Advocates, and NEEA and
NPCC stated that the technologies assumed to be required to meet TSL 4
are well-established in the market and commercially available. (ACEEE,
No. 94 at p. 6; CA IOU, No. 106 at p. 3; Joint Advocates, No. 105 at p.
4; NEEA, NPCC, No. 96 at p. 3) NEEP stated that three years should
provide adequate time for manufacturers to adjust product lines. (NEEP,
No. 109 at p. 2) The Joint Advocates stated that constant-torque BPM
motors are essentially drop-in replacements for PSC motors, and capital
conversion costs are not required. (Joint Advocates, No. 105 at p. 4)
NEEA and NPCC believe that three years of lead time should be
sufficient to allow a ramping up of motor manufacturing capacity and a
gradual shift of air handler manufacturing lines to incorporate them.
The technology required to meet the TSL 4 standards requires little
more than expansion of current production capacity for these models,
which mostly means buying different furnace fan motors and the
associated controls. (NEEA, NPCC, No. 96 at p. 3) Earthjustice stated
that DOE must choose a compliance date based on an assessment that
includes a consideration of factors beyond the impact on manufacturers.
(Earthjustice, No. 101 at p. 3)
JCI, Morrison, AHRI, Lennox, and HARDI support the five-year period
between the final rule publication and the compliance date as proposed
in the NOPR. (JCI, No. 95 at p. 2; Morrison, No. 108 at p. 2; AHRI, No.
98 at p. 2; Lennox, No. 100 at p. 4; HARDI, No. 103 at p. 2) JCI, AHRI,
and Lennox stated that to comply with the proposed standard,
manufacturers would not only have to alter the designs and fabrication
processes for the furnace fan assembly but also modify the broader
product design of the furnaces, air handlers, modular blowers, and
residential single package units that include those furnace fans. (JCI,
No. 95 at p. 2; AHRI, No. 98 at p. 2; Lennox, No. 100 at pp. 4-5) AHRI
stated that similar products that require similar actions for
compliance typically have lead times of five years. (AHRI, No. 98 at p
2) Ingersoll Rand agrees with AHRI's comments. (Ingersoll Rand, No. 107
at p. 11)
DOE continues to believe a 5-year lead time is appropriate. Since
EPCA does not mandate a specific lead time for furnace fan standards,
DOE considered the actions required by manufacturers to comply with
today's standards. As discussed in the NOPR, during manufacturer
interviews, DOE found that standards would result in manufacturers'
extending R&D beyond the furnace fan assembly to understand the impacts
on the design and performance of the furnace or modular blower in which
the furnace fan is integrated. 78 FR 64103. To comply with the
standards, manufacturers may have to alter not only the designs and
fabrication processes for the furnace fan assembly, but also for the
furnace or modular blower into which the furnace fan is integrated.
Similar products that require similar actions for compliance typically
have lead times of five years. For these reasons, DOE selected a 5-year
lead time, which would place the compliance date in 2019. For the
purposes of the LCC and PBP analysis, DOE assumed that all relevant
consumers purchase a furnace fan in 2019.
6. Base-Case Efficiency Distribution
To estimate the share of consumers that would be affected by an
energy conservation standard at a particular efficiency level, DOE's
LCC and PBP analysis considers the projected distribution (i.e., market
shares) of product efficiencies in the first compliance year under the
base case (i.e., the case without new or amended energy conservation
standards).
For the NOPR, DOE reviewed the information provided by the
manufacturers and estimated that the combined market share of constant-
torque BPM fans and constant-airflow BPM fans will be 35 percent in
2019. The shares are 13 percent for constant-torque BPM fans and 22
percent for constant-airflow BPM fans. DOE estimated separate shares
for replacement and new home applications.78 FR 64097.
The market shares of efficiency levels within the constant-torque
BPM motor and constant-airflow BPM motor categories were derived from
AHRI data on number of models.\42\ No such data were available for the
PSC fan efficiency levels, so DOE used the number of models it tested
or could measure using product literature to estimate that 40 percent
of shipments are at the baseline level and 60 percent are improved PSC
fans. There are currently no models of PSC with a controls design, so
DOE assumed zero market share for such units. Id
---------------------------------------------------------------------------
\42\ DOE used the AHRI Directory of Certified Furnace Equipment
(Available at: https://www.ahridirectory.org/ahridirectory/pages/home.aspx) as well as manufacturer product literature.
---------------------------------------------------------------------------
No comments were received on the base case efficiency distribution,
and DOE retained the NOPR assumptions for the final rule. The details
of DOE's approach are described in chapter 8 of the final rule TSD.
7. Payback Period
To calculate PBPs for the considered efficiency levels, DOE uses
the same inputs as for LCC analysis, except that discount rates are not
required.
Goodman stated that not including repair costs from later years in
the PBP does not provide a realistic picture of what most consumers
will face. It noted that while repair costs later in the product life
cycle may allow the initial investment to balance out faster, the
overall life-cycle costs can be very negatively impacted by such
repairs. (Goodman, No 102 at p. 10)
DOE recognizes that the PBP metric does not provide a complete
assessment of all costs that consumers may face, but it has found that
the results are of interest in standards rulemakings. The LCC analysis
does include all costs, and in part for this reason, DOE expresses the
share of consumers who benefit
[[Page 38168]]
from standards in terms of the change in LCC.
As discussed in section III.E.2, EPCA provides that a rebuttable
presumption is established that an energy conservation standard is
economically justified if the additional cost to the consumer of a
product that meets the standard is less than three times the value of
the first year's energy savings resulting from the standard, as
calculated under the applicable DOE test procedure. (42 U.S.C.
6295(o)(2)(B)(i)) The calculation of this so-called rebuttable
presumption payback period uses the same inputs as the calculation of
the regular PBP for each sample household, but it uses average values
instead of distributions, and the derivation of energy consumption and
savings only uses the parameters specified by the proposed DOE test
procedure for furnace fans rather than the method applied in the energy
use analysis (described in section IV.E), which considers the
characteristics of each sample household.
DOE's LCC and PBP analyses generate values that calculate the
payback period for consumers of potential energy conservation
standards, which includes, but is not limited to, the three-year
payback period contemplated under the rebuttable presumption test
discussed above. However, DOE routinely conducts a full economic
analysis that considers the full range of impacts, including those to
the consumer, manufacturer, Nation, and environment, as required under
42 U.S.C. 6295(o)(2)(B)(i). The results of this analysis serve as the
basis for DOE to definitively evaluate the economic justification for a
potential standard level (thereby supporting or rebutting the results
of any preliminary determination of economic justification).
G. Shipments Analysis
DOE uses forecasts of product shipments to calculate the national
impacts of standards on energy use, NPV, and future manufacturer cash
flows. DOE develops shipment projections based on historical data and
an analysis of key market drivers for each product.
The vast majority of furnace fans are shipped installed in
furnaces, so DOE estimated furnace fan shipments by projecting furnace
shipments in three market segments: (1) Replacements; (2) new housing;
and (3) new owners in buildings that did not previously have a central
furnace.
To project furnace replacement shipments, DOE developed retirement
functions for furnaces from the lifetime estimates and applied them to
the existing products in the housing stock. The existing stock of
products is tracked by vintage and developed from historical shipments
data. The shipments analysis uses a distribution of furnace lifetimes
to estimate furnace replacement shipments.
To project shipments to the new housing market, DOE utilized
projected new housing construction and historic saturation rates of
various furnace and cooling product types in new housing. For the final
rule, DOE used AEO 2013 for projections of new housing. Furnace
saturation rates in new housing are provided by the U.S. Census
Bureau's Characteristics of New Housing.\43\
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\43\ Available at: https://www.census.gov/construction/chars/.
---------------------------------------------------------------------------
DOE also included a small market segment consisting of households
that become ``new owners'' of a gas furnace. This segment consists of
households that have central air conditioning and non-central heating
or central air conditioning and electric heating and choose to install
a gas furnace.
Lennox stated that the shipment projections do not appear to be
supported by the record or recent sales figures, as historical
shipments data from AHRI for gas and oil warm air furnaces show a
downward trend in shipments. (Lennox, No. 100 at pp. 6-7) AHRI stated
that DOE's shipment projections are inaccurate and the projected
numbers significantly skew the national energy savings estimates.
(AHRI, No. 98 at pp. 4-5)
DOE's shipments projections are based on replacement of furnaces
installed over the past few decades and furnaces installed in future
new homes. Most of the recent downward trend in shipments is due to
lower new construction in the wake of the financial crisis. DOE updated
historical shipments with 2013 data, which shows a growth in gas
furnace shipments. DOE also updated the new construction forecast based
on AEO 2013 projections, which reflect improving economic conditions
and a future increase of the new construction market. In addition, the
replacements reflect an updated furnace retirement function based on
the latest furnace lifetime data. Oil furnace shipments are projected
to continue to drop in the future.
JCI and AHRI stated that the projected shipments should account for
an echo effect loss in replacement sales for the furnaces that were not
sold in the years 2008-2012. (JCI, No. 95 at p. 10; AHRI, No. 98 at pp.
4-5) The projection for today's final rule shows a lower level of
replacement shipments in the 2025-2030 period, which is a consequence
(i.e., an echo) of the decline in historical shipments in 2006-2009.
JCI believes that the shipment projections for furnaces are too
optimistic. It noted that during the years prior to 2006, demand for
large homes with multiple furnace systems was more common than it is
today. (JCI, No. 95 at pp. 9-10) Mortex stated that forecasts of future
shipments are unrealistically high because new homes are smaller and
less likely to have two furnaces. (Mortex, No. 104 at p. 3) In DOE's
final rule analysis, DOE assumed that new homes would not have multiple
furnaces.
It is reasonable to expect that energy conservation standards for
residential furnace fans that result in higher furnace prices would
have some dampening effect on sales. Some consumers might choose to
repair their existing furnace rather than purchase a new one, or
perhaps install an alternative space heating product. To estimate the
impact on shipments of the price increase for the considered efficiency
levels, DOE used a relative price elasticity approach. This approach
also gives some weight to the operating cost savings from higher-
efficiency products.
Ingersoll Rand stated that the shipment projections do not account
for a drop off in sales due to higher furnace prices that will result
from using more expensive components. (Ingersoll Rand, No. 107 at p. 9)
The comment is incorrect; the relative price elasticity approach does
estimate the impact on shipments of the price increase for the
considered efficiency levels for the NOPR and the final rule.
Several stakeholders raised issues with DOE's relative price
elasticity approach. They stated that the household income data and
data used to derive the elasticity are outdated and do not reflect
current trends, and the household appliances used to derive the
relative price elasticity (refrigerators, clothes washers and
dishwashers) are inappropriate for this rulemaking. (JCI, No. 95 at p.
10; Morrison, No. 108 at p. 8; AHRI, No. 98 at pp. 12-13; Goodman, No.
102 at p. 13) Rheem expressed similar concerns. (Rheem, No. 83 at p.
12)
In response, DOE notes that there are very few estimates of
consumer demand elasticity for durable goods. Although the data that
DOE used to estimate relative price elasticity are not current, and the
analysis focused on products that differ from furnaces, DOE believes
that consumer behavior with respect to the impact of higher appliance
price on
[[Page 38169]]
demand is not likely to have changed significantly. One recent paper
suggests that demand elasticity for air conditioners is inelastic--
holding efficiency constant, a 10% rise in price leads to a 1.4%
decline in sales.\44\ This is a lower elasticity than DOE uses in its
analysis. Therefore, DOE believes that it is reasonable to use the
relative price elasticity approach for today's final rule. See chapter
9 in the final rule TSD for a description of the method.
---------------------------------------------------------------------------
\44\ David Rapson. Durable Goods and Long-Run Electricity
Demand: Evidence from Air Conditioner Purchase Behavior. Department
of Economics, University of California, Davis. Available at:
www.econ.ucdavis.edu/faculty/dsrapson/Rapson_LR_electricity.pdf.
---------------------------------------------------------------------------
Mortex stated that a big increase in the installed cost of a new
furnace under the proposed energy conservation standards will lead many
consumers to repair rather than replace with a new furnace. (Mortex,
No. 104 at p. 3) In terms of the overall cost of a new furnace, the
increase attributable to using a more energy-efficient furnace fan is
relatively small--less than 10 percent--for fans meeting today's
standards. In any case, the price elasticity approach described above
captures the potential consumer response to higher furnace prices,
which often would consist of choosing to repair an existing furnace
rather than replace it with a new furnace.
AGA urged the Department to include a robust fuel switching
analysis, including the competing economics of natural gas furnaces
versus both electric furnaces and heat pumps. (AGA, No. 110 at p. 3)
There is a possibility that for some consumers considering replacement
of a non-condensing gas furnace, the higher price of a gas furnace due
to today's standards could lead to some switching to heat pumps.
However, this switching would only occur if the CAC is replaced at the
same time as the furnace. Furthermore, switching to a heat pump would
require additional cost to install backup electric resistance heating
elements. Based on the above considerations, DOE believes that any
switching to heat pumps due to today's standards would be minimal. The
standards would not create any incentive to switch to electric furnaces
because electric furnaces are subject to the furnace fan standard and
would see a similar incremental cost as a gas furnace.
H. National Impact Analysis
The NIA assesses the NES and the NPV from a national perspective of
total consumer costs and savings expected to result from new or amended
energy conservation standards at specific efficiency levels. DOE
determined the NPV and NES for the potential standard levels considered
for the furnace fan product classes analyzed. To make the analysis more
accessible and transparent to all interested parties, DOE prepared a
computer spreadsheet that uses typical values (as opposed to
probability distributions) as inputs. To assess the effect of input
uncertainty on NES and NPV results, DOE has developed its spreadsheet
model to conduct sensitivity analyses by running scenarios on specific
input variables.
Analyzing impacts of potential energy conservation standards for
residential furnace fans requires comparing projections of U.S. energy
consumption with new or amended energy conservation standards against
projections of energy consumption without the standards. The forecasts
include projections of annual appliance shipments, the annual energy
consumption of new appliances, and the purchase price of new
appliances.
A key component of DOE's NIA analysis is the energy efficiencies
projected over time for the base case (without new standards) and each
of the standards cases. The projected efficiencies represent the annual
shipment-weighted energy efficiency of the products under consideration
during the shipments projection period (i.e., from the assumed
compliance date of a new standard to 30 years after compliance is
required).
For the NOPR, DOE reviewed the information provided by the
manufacturers and modified its estimate of the long-run trend in market
shares of constant-torque BPM and constant-airflow BPM motor furnace
fans. The NOPR analysis assumes a long-run trend that results in market
share of the constant-torque BPM and constant-airflow BPM furnace fans
reaching 45 percent in 2048. 78 FR 64099. No comments were received on
this issue and DOE retained the same approach for the final rule.
For the NOPR, DOE used a roll-up scenario for estimating the
impacts of the potential energy conservation standards for residential
furnace fans. Under the roll-up scenario, DOE assumes: (1) Products
with efficiencies in the base case that do not meet the standard level
under consideration would roll up to meet the new standard level; and
(2) products with efficiencies above the standard level under
consideration would not be affected. Id.
Rheem stated that DOE's assumption that the sale of premium
products above the standard level will be unaffected is unreasonable.
(Rheem, No. 83 at p. 3) DOE acknowledges that the market shares of fans
with efficiency levels above a given standard level could change after
compliance with the new standards is required. Estimating how
manufacturers will respond to new standards with regard to their
marketing strategy for ``above-standard'' products is very difficult,
however. Rather than speculate, DOE believes that it is preferable to
retain a roll-up scenario for today's final rule.
For the standards cases, the assumed efficiency trend after the
compliance year varies depending on the particular standard. For the
case with today's standards, the overall BPM motor market share goes to
100 percent in 2019 and remains at that level. The shares of the
specific BPM motor designs (i.e., constant-torque BPM, constant-torque
BPM motor + multi-stage, constant-airflow BPM motor + multi-stage, and
constant-airflow BPM motor + multi-stage + backward-inclined impeller)
remain at the levels of 2019. The details are provided in chapter 10 of
the final rule TSD.
1. National Energy Savings Analysis
The national energy savings analysis involves a comparison of
national energy consumption of the considered products in each
potential standards case (TSL) with consumption in the base case with
no new or amended energy conservation standards. DOE calculated the
national energy consumption by multiplying the number of units (stock)
of each product (by vintage or age) by the unit energy consumption
(also by vintage). Vintage represents the age of the product. DOE
calculated annual NES based on the difference in national energy
consumption for the base case (without new efficiency standards) and
for each higher efficiency standard. DOE estimated energy consumption
and savings based on site energy and converted the electricity
consumption and savings to primary energy. Cumulative energy savings
are the sum of the NES for each year over the timeframe of the
analysis.
DOE calculates primary energy savings (power plant consumption)
from site electricity savings by applying a factor to account for
losses associated with the generation, transmission, and distribution
of electricity. For the NOPR, DOE derived marginal site-to-power plant
factors based on the version of the National Energy Modeling System
(NEMS) that corresponds to AEO 2012. 78 FR 64099. The factors change
over time in response to projected changes in the types of power plants
projected to provide electricity to the country.
[[Page 38170]]
Commenting on DOE's approach, AGA stated that it is highly unlikely
and unrealistic that all of the projected changes in types of power
plant used to generate electricity in this country will occur between
2019 and 2021 and that essentially no change will occur from 2031
through 2048. AGA stated that realistic trend lines to 2048 including a
linear forecast of declining site-to-power plant energy use should be
provided. (AGA, No. 110 at p. 3)
For the final rule, DOE derived site-to-power plant factors based
on the version of NEMS that corresponds to AEO 2013. As shown in Figure
10.3.1 in the final rule TSD, the factor (expressed as primary energy
per site kWh) declines through 2030 as more efficient power plants gain
share in power generation. After 2035, there is an increase due to
lower projected share of highly-efficient combined-cycle power plants.
DOE acknowledges that projections after 2035 are uncertain, but it
believes that NEMS provides a reasonable projection.
DOE has historically presented NES in terms of primary energy
savings. In response to the recommendations of a committee on ``Point-
of-Use and Full-Fuel-Cycle Measurement Approaches to Energy Efficiency
Standards'' appointed by the National Academy of Science, DOE announced
its intention to use full-fuel-cycle (FFC) measures of energy use and
greenhouse gas and other emissions in the national impact analyses and
emissions analyses included in future energy conservation standards
rulemakings. 76 FR 51281 (August 18, 2011). After evaluating the
approaches discussed in the August 18, 2011 notice, DOE published a
statement of amended policy in the Federal Register in which DOE
explained its determination that NEMS is the most appropriate tool for
its FFC analysis and its intention to use NEMS for that purpose. 77 FR
49701 (August 17, 2012). The approach used for today's final rule is
described in appendix 10-C of the final rule TSD.
JCI and AHRI stated that, for cooling mode, the NIA spreadsheet
model does not indicate how DOE used the average annual electricity use
values from the energy use analysis to determine national energy
savings. (JCI, No. 95 at pp. 4-5; AHRI, No. 98 at p. 6) In the NIA
spreadsheet, the LCC Inputs worksheet shows how the average annual
electricity use values are used over the analysis period.
Several stakeholders questioned the accuracy of the doubling in FFC
energy savings from TSL 3 to TSL 4 from an incremental efficiency level
improvement of 8 percent for five of the product classes from adding
the multi-staging option. (JCI, No. 95 at p 4; EEI, No. 91 at pp. 307,
309; Morrison, No. 108 at p. 4; AHRI, No. 98 at pp. 4-5; Lennox, No.
100 at p. 2; Ingersoll Rand, No. 107 at p. 9) Similarly, AHRI stated
that if the effect of multi-staging was indeed prominent enough to
nearly double the estimated FFC energy savings between TSLs 3 and 4,
DOE should have evaluated this effect for PSC motors as well. (AHRI,
No. 98 at p. 5) Morrison stated that for non-weatherized gas furnace
fans, it is inconsistent that TSL 4 could produce a very large increase
in FFC energy savings over TSL 3 while TSL 2 and 3 have the same
national energy savings; compared to the difference in energy use
between TSL 2 and TSL 3, TSL 4 has a much lower incremental average
electricity savings and higher additional fuel use compared to TSL 3.
(Morrison, No. 108 at p. 4)
For the final rule, DOE incorporated new test data on the fan
efficiency levels that were included in TSL 3 (constant torque BPM
motors) and TSL 4 (constant torque BPM motors (multi-stage)). These
data contributed to a decrease in efficiency for TSL 4 (see section
IV.C.1) With this change, the increase in savings from TSL 3 to TSL 4
is now smaller than in the NOPR. The NIA results are presented in
section V.B.3.
Several stakeholders stated that it is implausible that the furnace
fan standard will save about as much energy as the 2006 13 SEER
rulemaking (76 FR 7185) or the 2013/2015 90% AFUE furnace and 14 SEER
rulemaking (76 FR 37412). (AHRI, No. 98 at p. 6; Ingersoll Rand, No.
107 at p. 9; Lennox, No. 100 at p. 2; Goodman, No. 102 at p. 6)
Ingersoll Rand stated that the energy savings from the proposed rule
claim to be greater than savings from the 13 SEER rule, but the energy
savings of a furnace switching from a PSC motor to a constant torque
BPM is nearly an order of magnitude less than the energy use of the
furnace or heat pump. (Ingersoll Rand, No. 107 at p. 9)
DOE reviewed the methodology used to assess the energy savings
estimated for the proposed standards, as discussed in previous parts of
this notice, and believes that the energy savings estimated for the
considered TSLs are reasonable. Comparison with other rules must be
done with caution, as the savings in those rules depends on both the
stringency of the standards and the base case that was chosen in the
analysis. The fact that the energy savings of a furnace switching from
a PSC motor to a constant torque BPM is much less than the energy use
of the furnace or heat pump is not relevant to the energy savings
associated with standards for furnaces or heat pumps.
2. Net Present Value Analysis
The inputs for determining NPV are: (1) Total annual installed
cost; (2) total annual savings in operating costs; (3) a discount
factor to calculate the present value of costs and savings; (4) present
value of costs; and (5) present value of savings. DOE calculated net
savings each year as the difference between the base case and each
standards case in terms of total savings in operating costs versus
total increases in installed costs. DOE calculated savings over the
lifetime of products shipped in the forecast period. DOE calculated NPV
as the difference between the present value of operating cost savings
and the present value of total installed costs. DOE used a discount
factor based on real discount rates of 3 and 7 percent to discount
future costs and savings to present values.
For the NPV analysis, DOE calculates increases in total installed
costs as the difference in total installed cost between the base case
and standards case (i.e., once the standards take effect).
DOE assumed no change in residential furnace fan prices over the
2019-2048 period. In addition, DOE conducted a sensitivity analysis
using alternative price trends, specifically one in which prices
decline over time, and another in which prices rise. These price trends
are described in appendix 10-C of the final rule TSD.
DOE expresses savings in operating costs as decreases associated
with the lower energy consumption of products bought in the standards
case compared to the base efficiency case. Total savings in operating
costs are the product of savings per unit and the number of units of
each vintage that survive in a given year.
DOE estimates the NPV of consumer benefits using both a 3-percent
and a 7-percent real discount rate. DOE uses these discount rates in
accordance with guidance provided by the Office of Management and
Budget (OMB) to Federal agencies on the development of regulatory
analysis.\45\ The NPV results for the residential furnace fan TSLs are
presented in section V.B.3 of this document.
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\45\ OMB Circular A-4 (Sept. 17, 2003), section E, ``Identifying
and Measuring Benefits and Costs.''
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I. Consumer Subgroup Analysis
A consumer subgroup comprises a subset of the population that may
be affected disproportionately by new or revised energy conservation
standards (e.g., low-income consumers, seniors).
[[Page 38171]]
The purpose of a consumer subgroup analysis is to determine the extent
of any such disproportional impacts.
For today's final rule, DOE evaluated impacts of potential
standards on two subgroups: (1) Senior-only households and (2) low-
income households. DOE identified these households in the RECS sample
and used the LCC spreadsheet model to estimate the impacts of the
considered efficiency levels on these subgroups. The consumer subgroup
results for the residential furnace fan TSLs are presented in section
V.B.1 of this document.
J. Manufacturer Impact Analysis
1. Overview
DOE performed an MIA to estimate the financial impact of new energy
conservation standards on manufacturers of residential furnace fans and
to calculate the potential impact of such standards on employment and
manufacturing capacity. The MIA has both quantitative and qualitative
aspects. The quantitative part of the MIA primarily relies on the
Government Regulatory Impact Model (GRIM), an industry cash-flow model
with inputs specific to this rulemaking. The key GRIM inputs are data
on the industry cost structure, product costs, shipments, and
assumptions about markups and conversion expenditures. The key output
is the industry net present value (INPV). Different sets of assumptions
(markup scenarios) will produce different results. The qualitative part
of the MIA addresses factors such as product characteristics, impacts
on particular subgroups of firms, and important market and product
trends. The complete MIA is outlined in chapter 12 of the final rule
TSD.
For this rulemaking, DOE considers the ``furnace fan industry'' to
consist of manufacturers who assemble furnace fans as a component of
the HVAC products addressed in this rulemaking.
DOE conducted the MIA for this rulemaking in three phases. In Phase
1 of the MIA, DOE prepared a profile of the residential furnace fans
industry that includes a top-down cost analysis of manufacturers used
to derive preliminary financial inputs for the GRIM (e.g., sales,
general, and administration (SG&A) expenses; research and development
(R&D) expenses; and tax rates). DOE used public sources of information,
including company SEC 10-K filings,\46\ corporate annual reports, the
U.S. Census Bureau's Economic Census,\47\ and Hoover's reports.\48\
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\46\ U.S. Securities and Exchange Commission, Annual 10-K
Reports (Various Years) (Available at: https://sec.gov).
\47\ U.S. Census Bureau, Annual Survey of Manufacturers: General
Statistics: Statistics for Industry Groups and Industries (Available
at: https://factfinder2.census.gov/faces/nav/jsf/pages/searchresults.xhtml?refresh=t).
\48\ Hoovers Inc. Company Profiles (Various Companies)
(Available at: https://www.hoovers.com).
---------------------------------------------------------------------------
In Phase 2 of the MIA, DOE prepared an industry cash-flow analysis
to quantify the potential impacts of a new energy conservation
standard. In general, energy conservation standards can affect
manufacturer cash flow in three distinct ways: (1) Create a need for
increased investment; (2) raise production costs per unit; and (3)
alter revenue due to higher per-unit prices and possible changes in
sales volumes.
In Phase 3 of the MIA, DOE conducted structured, detailed
interviews with a representative cross-section of manufacturers. During
these interviews, DOE discussed engineering, manufacturing,
procurement, and financial topics to validate assumptions used in the
GRIM and to identify key issues or concerns. Section IV.J.4 of the NOPR
contains a description of the key issues manufacturers raised during
the interviews. 78 FR 64068, 64104-05 (Oct. 25, 2013).
Additionally, in Phase 3, DOE evaluated subgroups of manufacturers
that may be disproportionately impacted by new standards or that may
not be accurately represented by the average cost assumptions used to
develop the industry cash-flow analysis. For example, small
manufacturers, niche players, or manufacturers exhibiting a cost
structure that largely differs from the industry average could be more
negatively affected. DOE identified one subgroup (i.e., small
manufacturers) for a separate impact analysis.
DOE applied the small business size standards published by the
Small Business Administration (SBA) to determine whether a company is
considered a small business. 65 FR 30836, 30848 (May 15, 2000), as
amended at 65 FR 53533, 53544 (Sept. 5, 2000) and codified at 13 CFR
part 121. To be categorized as a small business under North American
Industry Classification System (NAICS) code 333415, ``Air-Conditioning
and Warm Air Heating Equipment and Commercial and Industrial
Refrigeration Equipment Manufacturing,'' a residential furnace fan
manufacturer and its affiliates may employ a maximum of 750 employees.
The 750-employee threshold includes all employees in a business's
parent company and any other subsidiaries. Based on this
classification, DOE identified 15 residential furnace fan manufacturers
that qualify as small businesses. The residential furnace fan small
manufacturer subgroup is discussed in chapter 12 of the final rule TSD
and in section V.B.2.d of this document.
2. Government Regulatory Impact Model
DOE uses the GRIM to quantify the changes in cash flow due to new
standards that result in a higher or lower industry value. The GRIM
analysis uses a standard, annual cash-flow analysis that incorporates
manufacturer costs, markups, shipments, and industry financial
information as inputs. The GRIM model changes in costs, distribution of
shipments, investments, and manufacturer margins that could result from
new energy conservation standards. The GRIM spreadsheet uses the inputs
to arrive at a series of annual cash flows, beginning in 2014 and
continuing to 2048. DOE calculated INPVs by summing the stream of
annual discounted cash flows during this period. For residential
furnace fan manufacturers, DOE used a real discount rate of 7.8
percent, which was derived from industry financials and then modified
according to feedback received during manufacturer interviews.
The GRIM calculates cash flows using standard accounting principles
and compares changes in INPV between a base case and each standards
case. The difference in INPV between the base case and a standards case
represents the financial impact of the new energy conservation standard
on manufacturers. As discussed previously, DOE collected this
information on the critical GRIM inputs from a number of sources,
including publicly-available data and interviews with a number of
manufacturers (described in the next section). The GRIM results are
shown in section V.B.2.a. Additional details about the GRIM, the
discount rate, and other financial parameters can be found in chapter
12 of the final rule TSD.
a. Government Regulatory Impact Model Key Inputs
Manufacturer Production Costs
Manufacturing a higher-efficiency product is typically more
expensive than manufacturing a baseline product due to the use of more
complex components, which are typically more costly than baseline
components. The changes in the MPCs of the analyzed products can affect
the revenues, gross
[[Page 38172]]
margins, and cash flow of the industry, making these product cost data
key GRIM inputs for DOE's analysis.
In the MIA, DOE used the MPCs for each considered efficiency level
calculated in the engineering analysis, as described in section IV.C
and further detailed in chapter 5 of the final rule TSD. In addition,
DOE used information from its teardown analysis, described in chapter 5
of the TSD, to disaggregate the MPCs into material, labor, and overhead
costs. To calculate the MPCs for equipment above the baseline, DOE
added the incremental material, labor, and overhead costs from the
engineering cost-efficiency curves to the baseline MPCs. These cost
breakdowns and product markups were validated and revised with
manufacturers during manufacturer interviews.
Shipments Forecast
The GRIM estimates manufacturer revenues based on total unit
shipment forecasts and the distribution of these values by efficiency
level. Changes in sales volumes and efficiency mix over time can
significantly affect manufacturer finances. For this analysis, the GRIM
uses the NIA's annual shipment forecasts derived from the shipments
analysis from 2014 (the base year) to 2048 (the end year of the
analysis period). See chapter 9 of the final rule TSD for additional
details.
Product and Capital Conversion Costs
New energy conservation standards would cause manufacturers to
incur one-time conversion costs to bring their production facilities
and product designs into compliance. DOE evaluated the level of
conversion-related expenditures that would be needed to comply with
each considered efficiency level in each product class. For the MIA,
DOE classified these conversion costs into two major groups: (1)
Product conversion costs; and (2) capital conversion costs. Product
conversion costs are one-time investments in research, development,
testing, marketing, and other non-capitalized costs necessary to make
product designs comply with the new energy conservation standard.
Capital conversion costs are one-time investments in property, plant,
and equipment necessary to adapt or change existing production
facilities such that new product designs can be fabricated and
assembled.
To evaluate the level of capital conversion expenditures
manufacturers would likely incur to comply with new energy conservation
standards, DOE used manufacturer interviews to gather data on the
anticipated level of capital investment that would be required at each
efficiency level. DOE validated manufacturer comments through estimates
of capital expenditure requirements derived from the product teardown
analysis and engineering analysis described in chapter 5 of the TSD.
DOE assessed the product conversion costs at each considered
efficiency level by integrating data from quantitative and qualitative
sources. DOE considered market-share-weighted feedback regarding the
potential costs of each efficiency level from multiple manufacturers to
determine conversion costs such as R&D expenditures and certification
costs. Manufacturer data were aggregated to better reflect the industry
as a whole and to protect confidential information.
In general, DOE assumes that all conversion-related investments
occur between the year of publication of the final rule and the year by
which manufacturers must comply with the new standard. The investment
figures used in the GRIM can be found in section IV.J.2 of this notice.
For additional information on the estimated product and capital
conversion costs, see chapter 12 of the final rule TSD.
b. Government Regulatory Impact Model Scenarios
Shipment Scenarios
In the NIA, DOE modeled shipments with a roll-up scenario to
represent possible standards-case efficiency distributions for the
years beginning 2019 (the year that compliance with new standards would
be required) through 2048 (the end of the analysis period). The roll-up
scenario represents the case in which all shipments in the base case
that do not meet the new standard would roll up to meet the new
standard level, with the efficiency of products already at the new
standard level remaining unchanged. Consumers in the base case who
purchase products above the standard level are not affected as they are
assumed to continue to purchase the same product in the standards case.
See chapter 9 of the final rule TSD for more information.
Markup Scenarios
As discussed above, MSPs include direct manufacturing production
costs (i.e., labor, materials, and overhead estimated in DOE's MPCs)
and all non-production costs (i.e., SG&A, R&D, and interest), along
with profit. To calculate the MSPs in the GRIM, DOE applied non-
production cost markups to the MPCs estimated in the engineering
analysis for each product class and efficiency level. Modifying these
markups in the standards case yields different sets of impacts on
manufacturers. For the MIA, DOE modeled two standards-case markup
scenarios to represent the uncertainty regarding the potential impacts
on prices and profitability for manufacturers following the
implementation of new energy conservation standards: (1) A preservation
of gross margin percentage markup scenario; and (2) a preservation of
per unit operating profit markup scenario. These scenarios lead to
different markups values that, when applied to the inputted MPCs,
result in varying revenue and cash flow impacts.
Under the preservation of gross margin percentage scenario, DOE
applied a single uniform ``gross margin percentage'' markup across all
efficiency levels, which assumes that manufacturers would be able to
maintain the same amount of profit as a percentage of revenues at all
efficiency levels within a product class. As production costs increase
with efficiency, this scenario implies that the absolute dollar markup
will increase as well. Based on publicly-available financial
information for manufacturers of residential furnace fans and comments
from manufacturer interviews, DOE assumed the non-production cost
markup--which includes SG&A expenses, R&D expenses, interest, and
profit--to be the following for each residential furnace fan product
class:
Table IV.11--Manufacturer Markup by Residential Furnace Fan Product
Class
------------------------------------------------------------------------
Product class Markup
------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan (NWG-NC)... 1.30
Non-Weatherized, Condensing Gas Furnace Fan (NWG-C)........ 1.31
Weatherized, Non-condensing Gas Furnace Fan (WG-NC)........ 1.27
Non-Weatherized, Non-condensing Oil Furnace Fan (NWO-NC)... 1.35
Electric Furnace/Modular Blower Fan (EF/MB)................ 1.19
[[Page 38173]]
Mobile Home Non-Weatherized, Non-condensing Gas Furnace Fan 1.25
(MH-NWG-NC)...............................................
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan (MH- 1.25
NWG-C)....................................................
Mobile Home Electric Furnace/Modular Blower Fan (MH-EF/MB). 1.15
------------------------------------------------------------------------
Because this markup scenario assumes that manufacturers would be
able to maintain their gross margin percentage markups as production
costs increase in response to a new energy conservation standard, it
represents a high bound to industry profitability.
In the preservation of per unit operating profit scenario,
manufacturer markups are set so that operating profit one year after
the compliance date of the new energy conservation standard is the same
as in the base case on a per unit basis. Under this scenario, as the
costs of production increase under a standards case, manufacturers are
generally required to reduce their markups to a level that maintains
base-case operating profit per unit. The implicit assumption behind
this markup scenario is that the industry can only maintain its
operating profit in absolute dollars per unit after compliance with the
new standard is required. Therefore, operating margin in percentage
terms is squeezed (reduced) between the base case and standards case.
DOE adjusted the manufacturer markups in the GRIM at each TSL to yield
approximately the same earnings before interest and taxes in the
standards case as in the base case. This markup scenario represents a
low bound to industry profitability under a new energy conservation
standard.
3. Discussion of Comments
During the NOPR public meeting, interested parties commented on the
assumptions and results of the NOPR analysis TSD. Oral and written
comments addressed several topics, including conversion costs,
cumulative regulatory burdens, scope of MIA coverage, markups analysis,
employment impacts, consumer utility impacts, and impacts on small
businesses.
a. Conversion Costs
Several manufacturers expressed concern regarding the DOE's
estimates of the capital and product conversion costs, including costs
relating to testing and certification.
Regarding capital conversion costs associated with a furnace fans
standard, Goodman commented that DOE's estimate of zero capital
conversion costs at TSL 4 does not properly reflect feedback from
manufacturer interviews. (Goodman, No. 102 at p. 10) AHRI stated that
the technology option associated with TSL 4 would necessitate changes
in manufacturers' assembly and subassembly production lines, including
the modification and/or elimination of current fan housings, heat
exchanger types, and furnace cabinet sizes, at a cost of $103 million
for the industry. (AHRI, No. 98 at p. 10) Johnson Controls commented
that compliance with the proposed standard would likely require them to
make a capital investment ranging from $2.8 million to $4 million.
(JCI, No. 95 at p. 2)
In the engineering analysis, most of the technology options being
considered require only a change in the type of motor used. At the NOPR
stage, DOE tentatively concluded that TSLs 1 through 5 would not
require manufacturers to incur capital expenditures for new tooling or
equipment. However, in response to the above-mentioned public comments
received during the NOPR period, DOE has revised its methodology for
estimating capital conversion costs at all TSLs for the final rule. DOE
incorporated all capital conversion cost values submitted by
manufacturers during the course of MIA interviews and used a product
listing weighted-average of feedback (based on basic model listings in
the AHRI directory) to determine conversion costs for the industry. As
a result, capital conversion costs were revised upward at all TSLs, as
shown in Table IV.12.
Table IV.12--Final Rule Capital Conversion Costs (CCC)
----------------------------------------------------------------------------------------------------------------
TSL 1 TSL 2 TSL 3 TSL 4 TSL 5 TSL 6
----------------------------------------------------------------------------------------------------------------
Total Industry CCCs ($ millions)........ 8.8 11.1 11.8 15.1 15.7 134.7
----------------------------------------------------------------------------------------------------------------
DOE notes that the conversion costs submitted by AHRI and Johnson
Controls are generally consistent with DOE's estimates of conversion
costs at TSL 6 in the final rule. However, without a more detailed
breakdown of the conversion costs by TSL from those stakeholders, it
was not feasible for DOE to determine the discrepancies in capital
conversion cost values or to incorporate their feedback into the GRIM
model.
With regards to product conversion costs, including costs
associated with compliance, certification, and enforcement (CC&E), both
Trane and Johnson Controls provided their own estimates in support of
the notion that there will be significant testing burden associated
with standards compliance. (Trane, No. 107 at pp. 2, 6, and JCI, No. 95
at p. 8) Goodman also stated that investments in additional testing
equipment may be required in order to keep pace with current and future
testing requirements. (Goodman, No. 102 at p. 11) AHRI and multiple
manufacturers commented that the performance standard associated with
TSL 4 would require total industry product conversion costs of $6.2
million. (AHRI, No. 98 at p. 10)
DOE acknowledges manufacturers' concerns regarding product
conversion cost estimates, including those relating to testing and
certification. Similar to the capital conversion cost analysis, DOE
refined its final rule modeling of product conversion costs to better
reflect information received during manufacturer interviews. DOE used a
product listing weighted-average (based on basic model listings in the
AHRI directory) to extrapolate individual manufacturer feedback to an
industry value for each efficiency level and for each product class.
Additionally, for the final rule, DOE explicitly incorporated
certification costs into the product conversion cost estimates used in
the GRIM. These certification costs occur in the base case and apply in
the standards cases. DOE modeled testing and certification costs under
the assumption
[[Page 38174]]
that larger manufacturers have would conduct all FER testing in-house,
while small manufacturers would outsource all certification testing.
DOE assumed a cost of $175 per test per basic model for large
manufacturers (derived from the test procedure estimate of a maximum of
4 hours per test) (79 FR 500 (Jan. 3, 2014)) and a cost of $2,000 per
test per basic model for small manufacturers (77 FR 28674 (May 15,
2012)). See Table IV.13 and Table IV.14 below for a summary of testing
and certification cost calculations and overall product conversion
costs. Conversion costs are discussed in detail in section V.B.2.a of
today's document and in chapter 12 of the final rule TSD.
Table IV.13--Testing and Certification Costs
------------------------------------------------------------------------
Value
------------------------------------------------------------------------
General assumptions:
[a] Number of FER tests required per Basic Model....... 2
[b] Total Industry Number of Basic Models \1\.......... 2,254
[c] Number of Basic Models for Large Manufacturers..... 1,943
[d] Number of Basic Models for Small Manufacturers..... 311
Large manufacturer assumptions:
[e] Labor rate ($/hr) \2\.............................. 43.73
[f] Time required per test (hours) \3\................. 4
Small manufacturer assumptions:
[g] Cost per FER test (outsource) ($) \4\ =............ $2,000
[h] FER costs per model for Large Manufacturer ($) = $350
[a]*[e]*[f]...........................................
[i] FER costs per model for Small Manufacturer ($) = $4,000
[a]*[g]...............................................
Total Industry FER costs ($ millions) = [h]*[c] + $1.9
[i]*[d]...............................................
Total Industry FER costs rescaled to account for EF/MB $2.2
and MH-EF/MB product classes ($ millions) \5\.........
------------------------------------------------------------------------
\1\ AHRI Directory: Residential Furnaces.
\2\ Bureau of Labor Statistics, 2012 mean hourly wage for all engineers.
\3\ 2012-05-15 Test Procedures for Residential Furnace Fans; Notice of
proposed rulemaking, section IV, part B.
\4\ 2012-05-15 Test Procedures for Residential Furnace Fans; Notice of
proposed rulemaking, section IV, part B.
\5\ The AHRI residential furnaces database does not contain electric
furnaces/modular blowers. In order to account for CC&E costs relates
to these products (standard and MH), DOE rescaled the $1.9 value by
12%, which is the estimated proportion of shipments for these two
categories combined. $2.2 is the value used in the GRIM.
Table IV.14--Product Conversion Costs
----------------------------------------------------------------------------------------------------------------
Baseline TSL 1 TSL 2 TSL 3 TSL 4 TSL 5 TSL 6
----------------------------------------------------------------------------------------------------------------
Total Number of Basic Models 2,254 .......... .......... .......... .......... .......... ..........
\1\........................
Average Testing and 853 8,449 10,577 11,356 11,434 12,157 13,182
Certification Costs + R&D
Costs per Basic Model ($)..
Total Industry PCCs ($ 2.2 18.8 23.6 25.3 25.5 27.1 29.4
millions)..................
----------------------------------------------------------------------------------------------------------------
\1\ AHRI Directory: Residential Furnaces.
b. Cumulative Regulatory Burden
Interested parties expressed concern over the cumulative regulatory
burden that would result from a residential furnace fan energy
conservation standard. AHRI, Morrison, and Lennox commented that DOE
did not account for the cumulative impacts of additional DOE
regulations, including energy conservation standards or potential
standards for commercial and industrial fans and blowers, commercial
package air conditioners and heat pumps, and commercial warm air
furnaces. The three stakeholders also asserted that DOE did not address
testing burdens associated with the recently finalized test procedures
for two-stage and modulating condensing furnaces and boilers, and
potential updates to test procedures for residential furnaces and
boilers. (AHRI, No. 98 at p. 8-9; Morrison, No. 108 at p. 6; Lennox,
No. 100 at p. 8) Rheem argued that DOE failed to address cumulative
burdens relating to regulations for water heaters, boilers, pool
heaters, and commercial refrigeration equipment. (Rheem, No. 83 at p.
14)
DOE notes that the energy conservation standard rulemakings for
commercial and industrial fans and blowers, commercial package air
conditioners and heat pumps, commercial warm air furnaces, water
heaters, residential boilers, commercial boilers, and pool heaters are
all regulation currently in progress. No standards have been proposed,
and no final regulations have been issued for these rulemakings. It is
DOE's policy not to include the impacts of regulatory proposals until
the analyses are complete and the standards are finalized. Until such
rulemaking is complete, it is unclear what, if any, requirements will
be adopted for the products in question. Consequently, it would be
speculative to try to include incomplete regulatory actions in an
assessment of cumulative regulatory burden. With regard to the test
procedure final rule for residential furnaces and boilers published on
July 10, 2013, the changes have a compliance date of January 6, 2014.
78 FR 41265. Because the regulation goes into effect before 2016, it is
outside of the 3-year window set for consideration in the cumulative
regulatory burden analysis. With regard to the commercial refrigeration
equipment (CRE) energy conservation standard rulemaking, at the time of
the residential furnace fan rulemaking NOPR publication, the final rule
for CRE standards had not yet been published. The final rule for CRE
standards was published on March 28, 2014 and is now included in the
final rule cumulative regulatory burden review in section V.B.2.e. 79
FR 17725.
Johnson Controls commented that DOE should consider the cumulative
impacts of State or local weatherization programs that may be
restrictive on HVAC equipment selections, as well as building code
standards at State, national, and international levels. In addition,
JCI believes DOE should include the impact of commercial product energy
efficiency standards,
[[Page 38175]]
alternate refrigeration requirements, and modifications to existing or
the generation of new building performance standards, such as ASHRAE
standards. (JCI, No. 95 at p. 7).
DOE considers cumulative regulatory burden pursuant to the
directions in the Process Rule (10 CFR part 430, subpart C, appendix
A). DOE notes that States and localities are generally preempted from
requiring HVAC standards beyond the Federal minimum through building
codes or other regulatory requirements. Once finalized, Federal
commercial energy efficiency standards, alternative refrigeration
requirements, and ASHRAE 90.1 standards that go into effect within 3
years of the effective date of today's standard are considered in the
cumulative regulatory burden analysis.
AHRI and Morrison commented that DOE failed to provide quantitative
estimates of the incremental burden imposed by the additional DOE
standards impacting furnace fan manufacturers. As a result, both
parties do not feel that such impacts were adequately reflected in the
GRIM. (AHRI, No. 98 at p. 9, and Morrison, No. 108 at p. 7).
In the final rule cumulative regulatory burden section, DOE has
provided an explicit review of the conversion costs associated with DOE
energy conservation standards that impact the manufacturers covered
under the residential furnace fan rulemaking. For more information,
please see section V.B.2.e of this document.
c. Scope of MIA Coverage
AHRI and Rheem commented that impacts on motor manufacturers should
be included in the manufacturing impact analysis. (AHRI, No. 43 at p.
151, and Rheem, No. 83 at p. 6)
DOE's manufacturer impact analysis focuses on the manufacturers
that have the direct burden of complying with the energy conservation
standard. In this rulemaking, the manufacturer of the residential
furnace has the burden of certifying and labeling the furnace fan
performance. Motors manufacturers are a component supplier but do not
have a direct compliance burden associated with this rule.
d. Markups Analysis
AHRI provided comments relating to both markup scenarios used in
the GRIM. With regards to the preservation of gross margin percentage
markup scenario, AHRI commented that it is unreasonable for DOE to
assume that, as manufacturer production costs increase in response to
an energy conservation standard, manufacturers would be able to
maintain the same gross margin percentage markup as the base case.
(AHRI, No. 98 at p. 10) AHRI continued by commenting that the
preservation of operating profit scenario is also inaccurate since it
implies that manufacturer markups are set so that operating profit one
year after the compliance date of the new energy conservation standards
is the same as in the base case. AHRI believes that the one year time
period is an extremely optimistic assumption and that a five-year time
period would be a more realistic average for the industry. (AHRI, No.
98 at p. 10)
DOE intends for the preservation of gross margin percentage and
preservation of per-unit operating profit markup scenarios to represent
the upper and lower bounds for the performance of the industry as a
result of new standards. The preservation of gross margin percentage
scenario assumes that manufacturers are able to pass on all increases
in MPC that result from standards to their first customers.
Additionally, the scenario assumes manufacturers are able to maintain
the existing markup on the incremental manufacturer production costs
that result from the standard, thereby allowing manufacturers to
recover portions of their conversion cost investments. The preservation
of per-unit operating profit scenario assumes that manufacturers are
not able to generate greater operating profit per unit sold in the
standards case. Additionally, the scenario assumes that manufacturers
are not able to recover any of their conversion cost investments. By
applying these two scenarios, DOE models examine the range of potential
industry impacts that reflect manufacturers' varying ability to pass
costs on to customers and recover conversion costs. The scenario
described by AHRI appears to relate to manufacturers' ability to
recover conversion costs, which is likely not possible by one year
following the standard year. However, the preservation of operating
profit per-unit markup scenario assumes only that manufacturers will
maintain the same annual operating profit as in the base case in the
year after the standards go into effect. DOE believes that
manufacturers' annual operating profit will be relatively constant in
the years following the standard, and, accordingly, the choice between
a one-year and five-year time horizon for this scenario is arbitrary.
e. Employment Impacts
AHRI and EEI commented that it is unrealistic to assume there would
be no reductions in domestic production employment at TSLs 1 through 5.
This is because labor costs will increase with higher design options,
and, subsequently, manufacturers will try to compensate by reducing
labor. (AHRI, No. 98 at p. 10 and EEI, No. 43 at p. 349) Additionally,
AHRI commented that subsection 12.7.1 in the NOPR TSD accounts for
line-supervisors as production workers who contribute towards the
manufacture of furnace fans, but should also account for engineers and
managers in supervisory roles who may not be involved in the day-to-day
assembly line operations. (AHRI, No. 98 at p. 11)
At the NOPR stage, DOE's employment analysis only provided an upper
bound to employment changes. These upper bound impacts were directly
correlated to changes in shipments and changes in per-unit labor
inputs. For the final rule, DOE uses the same employment model to
determine the upper bound of employment impacts. At the lower bound,
DOE models the scenario in which all production moves to lower
production cost countries. In reference to AHRI's second comment, DOE
does account for non-production workers in the GRIM and presents these
results along with revised estimates of domestic production employment
in chapter 12 of the final rule TSD.
f. Consumer Utility
Morrison commented in support of DOE's previously-stated concern
relating to the use of multiple rating systems on a given product.
Morrison emphasized that this would indeed lead to consumer confusion.
(Morrison, No. 108 at p. 2)
DOE understands manufacturer concern relating to multiple ratings.
However, DOE is required by legislation to set a separate standard and
an associated metric for the covered product, furnace fans.
g. Small Businesses
In reference to the Regulatory Flexibility Analysis contained in
the NOPR, Mortex expressed concern that DOE significantly
underestimated capital and product conversion costs. According to
Mortex, even at the underestimated level, the calculated impact to
small businesses (conversion costs of 5.1 percent of annual revenues)
would be highly detrimental. (Mortex, No. 104 at pp. 2-3)
DOE has revised its analysis of conversion costs for the final
rule. The increase in conversion costs is reflected in the Final
Regulatory Flexibility Analysis (FRFA), in section VI.B of this notice.
To help portray the magnitude of
[[Page 38176]]
the conversion costs relative to the size of the average small
business, the conversion costs (which are invested over a five-year
period) are compared to the financial metric of a single year's
operation.
K. Emissions Analysis
In the emissions analysis, DOE estimated the reduction in power
sector emissions of carbon dioxide (CO2), nitrogen oxides
(NOX), sulfur dioxide (SO2), and mercury (Hg)
from potential energy conservation standards for the considered
products (here, furnace fans). In addition to estimating impacts of
standards on power sector emissions, DOE estimated emissions impacts in
production activities (extracting, processing, and transporting fuels)
that provide the energy inputs to power plants. These are referred to
as ``upstream'' emissions. Together, these emissions account for the
full-fuel-cycle (FFC). In accordance with DOE's FFC Statement of Policy
(76 FR 51281 (August 18, 2011) as amended at 77 FR 49701 (August 17,
2012)), this FFC analysis also includes impacts on emissions of methane
(CH4) and nitrous oxide (N2O), both of which are
recognized as greenhouse gases.
DOE primarily conducted the emissions analysis using emissions
factors for CO2 and most of the other gases derived from
data in AEO 2013, supplemented by data from other sources. DOE
developed separate emissions factors for power sector emissions and
upstream emissions. The method that DOE used to derive emissions
factors is described in chapter 13 of the final rule TSD.
For CH4 and N2O, DOE calculated emissions
reduction in tons and also in terms of units of carbon dioxide
equivalent (CO2eq). Gases are converted to CO2eq
by multiplying each ton of the greenhouse gas by the gas's global
warming potential (GWP) over a 100-year time horizon. Based on the
Fourth Assessment Report of the Intergovernmental Panel on Climate
Change,\49\ DOE used GWP values of 25 for CH4 and 298 for
N2O.
---------------------------------------------------------------------------
\49\ Forster, P., V. Ramaswamy, P. Artaxo, T. Berntsen, R.
Betts, D.W. Fahey, J. Haywood, J. Lean, D.C. Lowe, G. Myhre, J.
Nganga, R. Prinn, G. Raga, M. Schulz and R. Van Dorland, 2007:
Changes in Atmospheric Constituents and in Radiative Forcing. In
Climate Change 2007: The Physical Science Basis. Contribution of
Working Group I to the Fourth Assessment Report of the
Intergovernmental Panel on Climate Change. S. Solomon, D. Qin, M.
Manning, Z. Chen, M. Marquis, K.B. Averyt, M. Tignor and H.L.
Miller, Editors (2007) Cambridge University Press, Cambridge, United
Kingdom and New York, NY, USA. p. 212.
---------------------------------------------------------------------------
EIA prepares the Annual Energy Outlook using the National Energy
Modeling System (NEMS). Each annual version of NEMS incorporates the
projected impacts of existing air quality regulations on emissions. AEO
2013 generally represents current legislation and environmental
regulations, including recent government actions, for which
implementing regulations were available as of December 31, 2012.
SO2 emissions from affected electric generating units
(EGUs) are subject to nationwide and regional emissions cap-and-trade
programs. Title IV of the Clean Air Act sets an annual emissions cap on
SO2 for affected EGUs in the 48 contiguous States (42 U.S.C.
7651 et seq.) and the District of Columbia (DC). SO2
emissions from 28 eastern States and DC were also limited under the
Clean Air Interstate Rule (CAIR; 70 FR 25162 (May 12, 2005)), which
created an allowance-based trading program. CAIR was remanded to the
U.S. Environmental Protection Agency (EPA) by the U.S. Court of Appeals
for the District of Columbia, but it remained in effect.\50\ See North
Carolina v. EPA, 550 F.3d 1176 (D.C. Cir. 2008); North Carolina v. EPA,
531 F.3d 896 (D.C. Cir. 2008). In 2011, EPA issued a replacement for
CAIR, the Cross-State Air Pollution Rule (CSAPR). 76 FR 48208 (August
8, 2011). On August 21, 2012, the DC Circuit issued a decision to
vacate CSAPR.\51\ The court ordered EPA to continue administering CAIR.
The AEO 2013 emissions factors used for today's final rule assume that
CAIR remains a binding regulation through 2040.
---------------------------------------------------------------------------
\50\ See North Carolina v. EPA, 550 F.3d 1176 (D.C. Cir. 2008);
North Carolina v. EPA, 531 F.3d 896 (D.C. Cir. 2008).
\51\ See EME Homer City Generation, LP v. EPA, 696 F.3d 7, 38
(D.C. Cir. 2012), cert. granted, 81 U.S.L.W. 3567, 81 U.S.L.W. 3696,
81 U.S.L.W. 3702 (U.S. June 24, 2013) (No. 12-1182).
---------------------------------------------------------------------------
The attainment of emissions caps is typically flexible among EGUs
and is enforced through the use of tradable emissions allowances. Under
existing EPA regulations, any excess SO2 emissions
allowances resulting from the lower electricity demand caused by the
adoption of a new or amended efficiency standard could be used to allow
offsetting increases in SO2 emissions by any regulated EGU.
In past rulemakings, DOE recognized that there was uncertainty about
the effects of efficiency standards on SO2 emissions covered
by the existing cap-and-trade system, but it concluded that negligible
reductions in power sector SO2 emissions would occur as a
result of standards.
Beginning in 2015, however, SO2 emissions will fall as a
result of the Mercury and Air Toxics Standards (MATS) for power plants.
77 FR 9304 (Feb. 16, 2012). In the final MATS rule, EPA established a
standard for hydrogen chloride as a surrogate for acid gas hazardous
air pollutants (HAP), and also established a standard for
SO2 (a non-HAP acid gas) as an alternative equivalent
surrogate standard for acid gas HAP. The same controls are used to
reduce HAP and non-HAP acid gas; thus, SO2 emissions will be
reduced as a result of the control technologies installed on coal-fired
power plants to comply with the MATS requirements for acid gas. AEO2013
assumes that, in order to continue operating, coal plants must have
either flue gas desulfurization or dry sorbent injection systems
installed by 2015. Both technologies, which are used to reduce acid gas
emissions, also reduce SO2 emissions. Under the MATS, NEMS
shows a reduction in SO2 emissions when electricity demand
decreases (e.g., as a result of energy efficiency standards). Emissions
will be far below the cap that would be established by CAIR, so it is
unlikely that excess SO2 emissions allowances resulting from
the lower electricity demand would be needed or used to allow
offsetting increases in SO2 emissions by any regulated EGU.
Therefore, DOE believes that energy efficiency standards will reduce
SO2 emissions in 2015 and beyond.
CAIR established a cap on NOX emissions in 28 eastern
States and the District of Columbia. Energy conservation standards are
expected to have little effect on NOX emissions in those
States covered by CAIR because excess NOX emissions
allowances resulting from the lower electricity demand could be used to
allow offsetting increases in NOX emissions. However,
standards would be expected to reduce NOX emissions in the
States not affected by the caps, so DOE estimated NOX
emissions reductions from the standards considered in today's final
rule for these States.
The MATS limit mercury emissions from power plants, but they do not
include emissions caps, and, as such, DOE's energy conservation
standards would likely reduce Hg emissions. DOE estimated mercury
emissions reduction using emissions factors based on AEO 2013, which
incorporates the MATS.
JCI and EEI stated that DOE did not consider the impact of the EPA
rulemakings on new and existing power plants, which likely will
materially affect the projections of CO2 emissions
reductions on which the DOE's SCC benefit calculations are based. (JCI,
No. 95 at p. 10-11; EEI, No. 87 at p. 9) Consistent with past practice,
DOE has
[[Page 38177]]
concluded that it would not be appropriate for its analysis to assume
implementation of regulations that are not in effect at this time. The
shape of any final EPA regulations is uncertain, as is the outcome of
potential legal challenges to those regulations.
EEI stated that, to be consistent with other rulemakings, DOE
should use modeling that calculates no emissions reductions as a result
of efficiency standards where such emissions are capped by State,
regional, or Federal regulations. In particular, DOE should eliminate
any estimated CO2 reductions in California and in the
Northeastern/Mid-Atlantic states that participate in the Regional
Greenhouse Gas Initiative (RGGI). (EEI, No. 87 at p. 10) Morrison
stated that different agencies simultaneously addressing similar
sources of CO2 emissions should not double-count emissions
reductions. (Morrison, No. 108 at p. 10)
As stated above, DOE based its emissions analysis on AEO 2013,
which represents current legislation and environmental regulations,
including recent government actions, for which implementing regulations
were available as of December 31, 2012. AEO 2013 accounts for the
implementation of regional and State air emissions regulations,
including those cited by EEI.\52\ Its analysis also considers the
impact of caps set by Federal regulations, as discussed above.
Consequently, the emissions reductions estimated to result from today's
standards are over and above any reductions attributable to other
State, regional, or Federal regulations.
---------------------------------------------------------------------------
\52\ See Assumptions to AEO 2013 (Available at: https://www.eia.gov/forecasts/aeo/assumptions/).
---------------------------------------------------------------------------
EEI stated that DOE's analysis significantly overestimates the
future emissions from power plants, as coal-fired power plants are
being retired and large amounts of wind and solar capacity are being
added. It stated that due to these factors, along with EPA regulations,
there will be a significant reduction in the baseline emissions from
power plants and a reduced emissions impact from any efficiency
standard. (EEI, No. 87 at p. 9)
DOE bases its emissions analysis on the latest projections from the
AEO, which consider retirement of coal-fired power plants, addition of
wind and solar capacity, and current EPA regulations. Decline in
baseline emissions from power plants does not mean that there would be
reduced impact from any efficiency standard, however. The impact of
standards on electricity demand takes place at the margin, and DOE's
analysis endeavors to reflect this marginal impact.
EEI stated that it is not clear how or why the power plant
emissions factors would increase for any regulated emission
(SO2, NOX, Hg, and CO2) after 2025 or
2030, based on current trends and Federal and State regulations. (EEI,
No. 87 at p. 10) DOE agrees that average power plant emissions factors
for the Nation as a whole would likely not increase after 2025 or 2030.
DOE's analysis uses marginal emissions factors, however, which depend
on changes to the mix of generation capacity by fuel type induced by a
marginal reduction in electricity demand for a particular end use
(e.g., residential heating). The behavior of marginal emissions factors
can be significantly different from the behavior of average emissions
factors. Marginal emissions factors are very sensitive to shifts in the
capacity mix relative to the AEO reference case, whereas average
emissions factors are not affected by these small shifts.
L. Monetizing Carbon Dioxide and Other Emissions Impacts
As part of the development of the standards in this final rule, DOE
considered the estimated monetary benefits from the reduced emissions
of CO2 and NOX that are expected to result from
each of the TSLs considered. In order to make this calculation
analogous to the calculation of the NPV of consumer benefit, DOE
considered the reduced emissions expected to result over the lifetime
of equipment shipped in the forecast period for each TSL. This section
summarizes the basis for the monetary values used for each of these
emissions and presents the values considered in this final rule.
For today's final rule, DOE is relying on a set of values for the
SCC that was developed by a Federal interagency process. The basis for
these values is summarized below, and a more detailed description of
the methodologies used is provided as an appendix to chapter 14 of the
final rule TSD.
1. Social Cost of Carbon
The SCC is an estimate of the monetized damages associated with an
incremental increase in carbon emissions in a given year. It is
intended to include (but is not limited to) changes in net agricultural
productivity, human health, property damages from increased flood risk,
and the value of ecosystem services. Estimates of the SCC are provided
in dollars per metric ton of carbon dioxide. A domestic SCC value is
meant to reflect the value of damages in the United States resulting
from a unit change in carbon dioxide emissions, while a global SCC
value is meant to reflect the value of damages worldwide.
Under section 1(b) of Executive Order 12866, agencies must, to the
extent permitted by law, ``assess both the costs and the benefits of
the intended regulation and, recognizing that some costs and benefits
are difficult to quantify, propose or adopt a regulation only upon a
reasoned determination that the benefits of the intended regulation
justify its costs.'' The purpose of the SCC estimates presented here is
to allow agencies to incorporate the monetized social benefits of
reducing CO2 emissions into cost-benefit analyses of
regulatory actions. The estimates are presented with an acknowledgement
of the many uncertainties involved and with a clear understanding that
they should be updated over time to reflect increasing knowledge of the
science and economics of climate impacts.
As part of the interagency process that developed these SCC
estimates, technical experts from numerous agencies met on a regular
basis to consider public comments, explore the technical literature in
relevant fields, and discuss key model inputs and assumptions. The main
objective of this process was to develop a range of SCC values using a
defensible set of input assumptions grounded in the existing scientific
and economic literatures. In this way, key uncertainties and model
differences transparently and consistently inform the range of SCC
estimates used in the rulemaking process.
Monetizing Carbon Dioxide Emissions
When attempting to assess the incremental economic impacts of
carbon dioxide emissions, the analyst faces a number of challenges. A
report from the National Research Council \53\ points out that any
assessment will suffer from uncertainty, speculation, and lack of
information about: (1) Future emissions of GHGs; (2) the effects of
past and future emissions on the climate system; (3) the impact of
changes in climate on the physical and biological environment; and (4)
the translation of these environmental impacts into economic damages.
As a result, any effort to quantify and monetize the harms associated
with climate change will raise questions of science, economics, and
ethics and should be viewed as provisional.
---------------------------------------------------------------------------
\53\ National Research Council. Hidden Costs of Energy: Unpriced
Consequences of Energy Production and Use (2009) National Academies
Press: Washington, DC.
---------------------------------------------------------------------------
[[Page 38178]]
Despite the limits of both quantification and monetization, SCC
estimates can be useful in estimating the social benefits of reducing
CO2 emissions. The agency can estimate the benefits from
reduced (or costs from increased) emissions in any future year by
multiplying the change in emissions in that year by the SCC values
appropriate for that year. The net present value of the benefits can
then be calculated by multiplying each of these future benefits by an
appropriate discount factor and summing across all affected years.
It is important to emphasize that the interagency process is
committed to updating these estimates as the science and economic
understanding of climate change and its impacts on society improves
over time. In the meantime, the interagency group will continue to
explore the issues raised by this analysis and consider public comments
as part of the ongoing interagency process.
Development of Social Cost of Carbon Values
In 2009, an interagency process was initiated to offer a
preliminary assessment of how best to quantify the benefits from
reducing carbon dioxide emissions. To ensure consistency in how
benefits are evaluated across Federal agencies, the Administration
sought to develop a transparent and defensible method, specifically
designed for the rulemaking process, to quantify avoided climate change
damages from reduced CO2 emissions. The interagency group
did not undertake any original analysis. Instead, it combined SCC
estimates from the existing literature to use as interim values until a
more comprehensive analysis could be conducted. The outcome of the
preliminary assessment by the interagency group was a set of five
interim values: Global SCC estimates for 2007 (in 2006$) of $55, $33,
$19, $10, and $5 per metric ton of CO2. These interim values
represented the first sustained interagency effort within the U.S.
government to develop an SCC for use in regulatory analysis. The
results of this preliminary effort were presented in several proposed
and final rules.
Current Approach and Key Assumptions
After the release of the interim values, the interagency group
reconvened on a regular basis to generate improved SCC estimates.
Specially, the group considered public comments and further explored
the technical literature in relevant fields. The interagency group
relied on three integrated assessment models commonly used to estimate
the SCC: the FUND, DICE, and PAGE models. These models are frequently
cited in the peer-reviewed literature and were used in the last
assessment of the Intergovernmental Panel on Climate Change (IPCC).
Each model was given equal weight in the SCC values that were
developed.
Each model takes a slightly different approach to model how changes
in emissions result in changes in economic damages. A key objective of
the interagency process was to enable a consistent exploration of the
three models, while respecting the different approaches to quantifying
damages taken by the key modelers in the field. An extensive review of
the literature was conducted to select three sets of input parameters
for these models: climate sensitivity, socio-economic and emissions
trajectories, and discount rates. A probability distribution for
climate sensitivity was specified as an input into all three models. In
addition, the interagency group used a range of scenarios for the
socio-economic parameters and a range of values for the discount rate.
All other model features were left unchanged, relying on the model
developers' best estimates and judgments.
The interagency group selected four sets of SCC values for use in
regulatory analyses. Three sets of values are based on the average SCC
from the three IAMs, at discount rates of 2.5, 3, and 5 percent. The
fourth set, which represents the 95th percentile SCC estimate across
all three models at a 3-percent discount rate, was included to
represent higher-than-expected impacts from temperature change further
out in the tails of the SCC distribution. The values grow in real terms
over time. Additionally, the interagency group determined that a range
of values from 7 percent to 23 percent should be used to adjust the
global SCC to calculate domestic effects,\54\ although preference is
given to consideration of the global benefits of reducing
CO2 emissions. Table IV.15 presents the values in the 2010
interagency group report,\55\ which is reproduced in appendix 14A of
the DOE final rule TSD.
---------------------------------------------------------------------------
\54\ It is recognized that this calculation for domestic values
is approximate, provisional, and highly speculative. There is no a
priori reason why domestic benefits should be a constant fraction of
net global damages over time.
\55\ Social Cost of Carbon for Regulatory Impact Analysis Under
Executive Order 12866. Interagency Working Group on Social Cost of
Carbon, United States Government (February 2010) (Available at:
www.whitehouse.gov/sites/default/files/omb/inforeg/for-agencies/Social-Cost-of-Carbon-for-RIA.pdf).
Table IV.15--Annual SCC Values From 2010 Interagency Report, 2010-2050
[2007$ per metric ton CO2]
----------------------------------------------------------------------------------------------------------------
Discount rate
---------------------------------------------------------------------------
Year 5% 3% 2.5% 3%
---------------------------------------------------------------------------
Average Average Average 95th percentile
----------------------------------------------------------------------------------------------------------------
2010................................ 4.7 21.4 35.1 64.9
2015................................ 5.7 23.8 38.4 72.8
2020................................ 6.8 26.3 41.7 80.7
2025................................ 8.2 29.6 45.9 90.4
2030................................ 9.7 32.8 50.0 100.0
2035................................ 11.2 36.0 54.2 109.7
2040................................ 12.7 39.2 58.4 119.3
2045................................ 14.2 42.1 61.7 127.8
2050................................ 15.7 44.9 65.0 136.2
----------------------------------------------------------------------------------------------------------------
[[Page 38179]]
The SCC values used for today's notice were generated using the
most recent versions of the three integrated assessment models that
have been published in the peer-reviewed literature.\56\
---------------------------------------------------------------------------
\56\ Technical Update of the Social Cost of Carbon for
Regulatory Impact Analysis Under Executive Order 12866, Interagency
Working Group on Social Cost of Carbon, United States Government
(May 2013; revised November 2013) (Available at: https://www.whitehouse.gov/sites/default/files/omb/assets/inforeg/technical-update-social-cost-of-carbon-for-regulator-impact-analysis.pdf).
---------------------------------------------------------------------------
Table IV.16 shows the updated sets of SCC estimates in 5-year
increments from 2010 to 2050. The full set of annual SCC estimates
between 2010 and 2050 is reported in appendix 14B of the DOE final rule
TSD. The central value that emerges is the average SCC across models at
the 3-percent discount rate. However, for purposes of capturing the
uncertainties involved in regulatory impact analysis, the interagency
group emphasizes the importance of including all four sets of SCC
values.
Table IV.16--Annual SCC Values From 2013 Interagency Report, 2010-2050
[2007$ per metric ton CO2]
----------------------------------------------------------------------------------------------------------------
Discount rate
---------------------------------------------------------------------------
Year 5% 3% 2.5% 3%
---------------------------------------------------------------------------
Average Average Average 95th percentile
----------------------------------------------------------------------------------------------------------------
2010................................ 11 32 51 89
2015................................ 11 37 57 109
2020................................ 12 43 64 128
2025................................ 14 47 69 143
2030................................ 16 52 75 159
2035................................ 19 56 80 175
2040................................ 21 61 86 191
2045................................ 24 66 92 206
2050................................ 26 71 97 220
----------------------------------------------------------------------------------------------------------------
It is important to recognize that a number of key uncertainties
remain, and that current SCC estimates should be treated as provisional
and revisable because they will evolve with improved scientific and
economic understanding. The interagency group also recognizes that the
existing models are imperfect and incomplete. The 2009 National
Research Council report mentioned above points out that there is
tension between the goal of producing quantified estimates of the
economic damages from an incremental ton of carbon and the limits of
existing efforts to model these effects. There are a number of
analytical challenges that are being addressed by the research
community, including research programs housed in many of the Federal
agencies participating in the interagency process to estimate the SCC.
The interagency group intends to periodically review and reconsider
those estimates to reflect increasing knowledge of the science and
economics of climate impacts, as well as improvements in modeling.
In summary, in considering the potential global benefits resulting
from reduced CO2 emissions, DOE used the values from the
2013 interagency report adjusted to 2013$ using the GDP price deflator.
For each of the four sets of SCC values, the values for emissions in
2015 were $12.0, $40.5, $62.4, and $119 per metric ton avoided (values
expressed in 2013$). DOE derived values after 2050 using the relevant
growth rates for the 2040-2050 period in the interagency update.
DOE multiplied the CO2 emissions reduction estimated for
each year by the SCC value for that year in each of the four cases. To
calculate a present value of the stream of monetary values, DOE
discounted the values in each of the four cases using the specific
discount rate that had been used to obtain the SCC values in each case.
In responding to the NOPR, many commenters questioned the
scientific and economic basis of the SCC values.
A number of stakeholders stated that DOE should not use SCC values
to establish monetary figures for emissions reductions until the SCC
undergoes a more rigorous notice, review, and comment process.
(Morrison, No. 108 at p. 9; JCI, No. 95 at p. 10; AHRI, No. 98 at pp.
12-13; The Associations, No. 99 at p. 2; NAM, No. 84 at p. 1-2; Cato
Institute, No. 81 at p. 2) Ingersoll Rand agrees with AHRI's comments.
(Ingersoll Rand, No. 107 at p. 11) Rheem stated that the Federal
Interagency Working Group has failed to disclose and quantify key
uncertainties to inform decision makers and the public about the
effects and uncertainties of alternative regulatory actions, as
required by OMB. (Rheem, No. 83 at p. 9) NAM stated that the SCC
estimates were developed without sufficient transparency, inadequate
supporting information related to assumptions and other data, and a
failure to peer-review critical model inputs. (NAM, No. 84 at pp. 1-2)
Morrison stated that the SCC estimates are the product of an opaque
process and that any pretensions to their supposed accuracy are
unsupportable. (Morrison, No. 108 at p. 9) JCI stated that the SCC has
not been adequately noticed and reviewed before being used in this NOPR
or any other rulemaking. JCI added that it is aware that the SCC
process is undergoing a current review and comment process, which has
the potential for significant changes in how those SCC calculations are
used in any rulemakings. (JCI, No. 95 at p. 10) Rheem stated that even
if the SCC estimate development process were transparent, rigorous, and
peer-reviewed, the modeling conducted in this effort does not offer a
reasonably acceptable range of accuracy for use in policymaking.
(Rheem, No. 83 at p. 9)
In conducting the interagency process that developed the SCC
values, technical experts from numerous agencies met on a regular basis
to consider public comments, explore the technical literature in
relevant fields, and discuss key model inputs and assumptions. Key
uncertainties and model differences transparently and consistently
inform the range of SCC estimates. These uncertainties and model
differences are discussed in the interagency working group's reports,
which are reproduced in appendix 14A and 14B of the final rule TSD, as
are the major assumptions. The 2010 SCC
[[Page 38180]]
values have been used in a number of Federal rulemakings in which the
public had opportunity to comment. In November 2013, the OMB announced
a new opportunity for public comment on the TSD underlying the revised
SCC estimates. See 78 FR 70586 (Nov. 26, 2013). OMB is currently
reviewing comments and considering whether further revisions to the
2013 SCC estimates are warranted. DOE stands ready to work with OMB and
the other members of the interagency working group on further review
and revision of the SCC estimates as appropriate.
NAM stated that in using the SCC estimates, DOE fails to adhere to
its own guidelines for ensuring and maximizing the quality,
objectivity, utility, and integrity of information disseminated by the
DOE. (NAM, No. 84 at pp. 1-2) DOE has sought to ensure that the data
and research used to support its policy decisions--including the SCC
values--are of high scientific and technical quality and objectivity,
as called for by the Secretarial Policy Statement on Scientific
Integrity.\57\ See section VI.J for DOE's evaluation of today's final
rule and supporting analyses under the DOE and OMB information quality
guidelines.
---------------------------------------------------------------------------
\57\ See https://www.directives.doe.gov/directives-documents/0411.2-APolicy.
---------------------------------------------------------------------------
Rheem stated that the modeling systems used for the SCC estimates
and the subsequent analyses were not subject to peer review as
appropriate. (Rheem, No. 83 at p. 9) The Cato Institute stated that the
determination of the SCC is discordant with the best scientific
literature on the equilibrium climate sensitivity and the fertilization
effect of carbon dioxide--two critically important parameters for
establishing the net externality of carbon dioxide emissions. (Cato
Institute, No. 81 at p. 2)
The three integrated assessment models used to estimate the SCC are
frequently cited in the peer-reviewed literature and were used in the
last assessment of the IPCC. In addition, new versions of the models
that were used in 2013 to estimate revised SCC values were published in
the peer-reviewed literature (see appendix 14B of the final rule TSD).
The revised estimates that were issued in November 2013 are based on
the best available scientific information on the impacts of climate
change. The issue of equilibrium climate sensitivity is addressed in
section 14A.4 of appendix 14A in the final rule TSD. The EPA, in
collaboration with other Federal agencies, continues to investigate
potential improvements to the way in which economic damages associated
with changes in CO2 emissions are quantified.
Morrison stated that the CO2 emissions reductions
benefits are overestimated, because the SCC values do not account for
any prior changes that impact the baseline emissions trends in previous
years. According to the commenter, DOE fails to take into consideration
EPA regulations of greenhouse gas emissions from power plants, which
would affect the SCC values. (Morrison, No. 108 at p. 10)
The SCC values are based on projections of global GHG emissions
over many decades. Such projections are influenced by many factors,
particularly economic growth rates and prices of different energy
sources. In the context of these projections, the proposed EPA
regulations of greenhouse gas emissions from new power plants are a
minor factor. In any case, it would not be appropriate for DOE to
account for regulations that are not currently in effect, because
whether such regulations will be adopted and their final form are
matters of speculation at this time.
Miller stated that the Department appears to violate the directive
in OMB Circular A-4, which states: ``The analysis should focus on
benefits and costs that accrue to citizens and residents of the United
States. Where the agency chooses to evaluate a regulation that is
likely to have effects beyond the borders of the United States, these
effects should be reported separately.'' Miller stated that instead of
focusing on domestic benefits and separately reporting any
international effects, the Department focused on much-larger global
benefits in the text of the proposed rule and separately reported the
(much smaller) domestic effects in a chapter of the TSD. (Miller, No.
79 at pp. 6-7) Similarly, Rheem stated that by presenting only global
SCC estimates and downplaying domestic SCC estimates in 2013, the IWG
has severely limited the utility of the SCC for use in benefit-cost
analysis and policymaking. (Rheem, No. 83 at p. 9) Mercatus stated that
OMB guidelines specifically require that benefit-cost analysis of
Federal regulations be reported for domestic estimates, with global
estimates being optional. Mercatus argued that by using the global
estimate at a three-percent discount rate, DOE inflated the benefits of
reducing carbon emissions by almost double compared to using a domestic
SCC at five percent. (Mercatus, No. 82 at pp. 7-8) EEI stated that the
use of global SCC values, which are estimates that are based on many
global assumptions and are subject to a great deal of uncertainty, may
be important in assessing the overall costs and benefits of particular
regulations, but using these values in the context of setting energy
conservation standards is problematic, as the geographic and temporal
scales of the LCC and SCC values are very different. (EEI, No. 87 at p.
10-11)
Although the relevant analyses address both domestic and global
impacts, the interagency group has determined that it is appropriate to
focus on a global measure of SCC because of the distinctive nature of
the climate change problem, which is highly unusual in at least two
respects. First, it involves a global externality: Emissions of most
greenhouse gases contribute to damages around the world when they are
emitted in the United States. Second, climate change presents a problem
that the United States alone cannot solve. The issue of global versus
domestic measures of the SCC is further discussed in appendix 14A of
the final rule TSD.
NAM stated that under DOE's analysis, the cost-benefit results and
the proposed rule are legally sufficient without the inclusion of the
SCC estimate. (NAM, No. 84 at p. 3) In contrast, JCI stated that the
monetary value of the CO2 emissions reduction plays a
significant role in DOE's justification to set the TSL 4 levels as the
national standards. (JCI, No. 95 at p. 10)
DOE disagrees with NAM's assessment, which suggests that
consideration of the SCC in the context of this rulemaking is somehow
unnecessary or unimportant. When selecting a proposed standard level or
adopting a final standard level, DOE considers and carefully weighs all
relevant factors. Thus, the monetary value of the CO2
emissions reduction did play a role in DOE's decision to propose TSL 4
(and to adopt TSL 4 in today's notice), as appropriate. DOE has
determined that today's standards are expected to achieve the maximum
improvement in energy efficiency that is technologically feasible and
economically justified, with or without consideration of the economic
benefits associated with reduced CO2 emissions.
Morrison stated that DOE does not conduct the cost-benefit analysis
for NPV and SCC values over the same time frame and within the same
scope, an important principle of cost-benefit analysis. (Morrison, No.
108 at p. 9)
For the analysis of national impacts of standards, DOE considers
the lifetime impacts of equipment shipped in a 30-year period. With
respect to energy and energy cost savings, impacts continue past 30
years until all of the equipment
[[Page 38181]]
shipped in the 30-year period is retired. With respect to the valuation
of CO2 emissions reductions, the SCC estimates developed by
the interagency working group are meant to represent the full
discounted value (using an appropriate range of discount rates) of
emissions reductions occurring in a given year. DOE is thus comparing
the costs of achieving the emissions reductions in each year of the
analysis, with the carbon reduction value of the emissions reductions
in those same years. Neither the costs nor the benefits of emissions
reductions outside the analytic time frame are included in the
analysis.
M. Utility Impact Analysis
The utility impact analysis estimates several effects on the power
generation industry that would result from the adoption of new or
amended energy conservation standards. In the utility impact analysis,
DOE analyzes the changes in electric installed capacity and generation
that result for each trial standard level. The utility impact analysis
uses a variant of NEMS, which is a public domain, multi-sectored,
partial equilibrium model of the U.S. energy sector. DOE uses a variant
of this model, referred to as NEMS-BT,\58\ to account for selected
utility impacts of new or amended energy conservation standards. DOE's
analysis consists of a comparison between model results for the most
recent AEO Reference Case and for cases in which energy use is
decremented to reflect the impact of potential standards. The energy
savings inputs associated with each TSL come from the NIA. Chapter 15
of the final rule TSD describes the utility impact analysis in further
detail.
---------------------------------------------------------------------------
\58\ DOE/EIA approves use of the name NEMS to describe only an
official version of the model without any modification to code or
data. Because this analysis entails some minor code modifications
and the model is run under various policy scenarios that are
variations on DOE/EIA assumptions, DOE refers to it by the name
``NEMS-BT'' (``BT'' is DOE's Building Technologies Program, under
whose aegis this work has been performed).
---------------------------------------------------------------------------
EEI stated that it is not possible under most operational scenarios
to increase electric capacity and decrease the amount of electric
generation, as is indicated by DOE's analysis. (EEI, No. 87 at p. 8) In
response, it would appear that the commenter has misinterpreted Table
15.3.1 in the NOPR TSD. The figure shows the capacity reduction as a
positive value; it is not an increase as it might appear at first
glance.
EEI stated that it is ironic that DOE is showing that an estimated
reduction of renewable power plants provides an economic benefit to the
United States. (EEI, No. 87 at p. 9) DOE reports the projected changes
in the installed capacity of different types of power plants resulting
from potential standards. Since the change in demand occurs at the
margin, it is not surprising that plant types with relatively high
first cost (such as solar and wind power) would be affected by
standards. When assessing the energy savings associated with energy
conservation standards, DOE does not claim that any particular changes
in installed capacity of different types of power plants provide an
economic benefit to the Nation relative to other types of power plant
facilities.
EEI stated that the analysis appears to ignore the impacts of
renewable portfolio standards in 29 States and the District of Columbia
(as well as the renewable power goals in 8 other States). (EEI, No. 87
at p. 9) DOE disagrees with EEI's assertion regarding DOE's
consideration of renewable portfolio standards. In the utility impact
analysis, DOE used the projections of electricity generation by plant
type in AEO 2013. These projections account for the estimated impacts
of all renewable portfolio standards that were in place at the end of
2012.
Several stakeholders stated that DOE did not adequately consider
power quality issues, specifically that DOE did not account for the
effect of such a large number of non-linear power supplies (constant-
torque BPM motors and multi-staging controls) without power factor
correction on the grid. Several of them stated that the non-linear
loads produced by constant-torque and constant-airflow BPM motors tend
to cause harmonic distortions in both voltage and current, and could
potentially cause voltage control problems within a power grid system.
(JCI, No. 95 at p. 9; Morrison, No. 108 at p. 7; AHRI, No. 98 at p. 11)
JCI stated that the Electric Power Research Institute suggests that
while harmonic emissions from a single system may not have a major
impact on the grid, the cumulative impact of millions of furnaces could
be significant on the grid systems within the U.S. (JCI, No. 95 at p.
9) Southern Company stated that the BPM motors considered in this
rulemaking typically have poor power factors and emit strong 3rd and
5th order harmonics, which is likely to cause problems with utility
systems at a future date when most of the older equipment has been
retired and replaced by BPM motors. (Southern Company, No. 85 at p. 4)
JCI, Morrison, and AHRI stated that the mitigation costs associated
with harmonic distortions would have a significant impact on consumers,
especially related to failure rates, maintenance and repair costs, and
the overall economic analysis for life-cycle costs. (JCI, No. 95 at p.
9; Morrison, No. 108 at p. 7; AHRI, No. 98 at p. 11) Southern Company
stated that, for furnace fans with BPM motors, DOE could assume a
percentage of households would require wiring upgrades and some
additional costs to either the utility or the homeowner for filtering
of harmonics or power factor correction. (Southern Company, No. 85 at
p. 4) APGA stated that DOE should include the cost of installation of
harmonic filters in the LCC analysis and recalculate the economic
justification of design options incorporating ECM motors. (APGA, No.
110 at p. 3)
Regarding these comments, DOE notes that a number of studies assume
that output from BPM motors is constant at full load at time of use,
similar to operation of PSC motors. However, BPM motors are
specifically designed to accommodate reduced-load operation, and,
therefore, most of the time, they will operate at part load (i.e., at
lower speeds and higher efficiency). The current of a BPM motor at
lower-speed operation is significantly lower than a PSC motor at normal
operation; therefore, total current contribution will not exceed the
existing system grid capacity. In addition, the harmonic contribution
is a small part of total circuit loading, at the lower current levels.
For example, motor performance data from GE \59\ shows an increase in
power of 133 volt-amperes (VA) from a \1/3\ HP PSC to BPM at full
output. On average, 5 to 20 residential customers are served per
distribution transformer, which are normally rated between 15 and 50
kVA.60 61 An increase of this current would result in an
increase in loading less than 3 percent at the extreme case. (The
extreme case is all HVAC at full load concurrently, served by the same
distribution transformer.) The transformers are normally rated
approximately 30 percent to 50 percent above predicted peak load.\62\
In this case, the increased current draw (VA) would have negligible
impact. Measured
[[Page 38182]]
performance data \63\ show a decrease in current drawn for cooling
functionality (152 VA) and an increase for heating functionality (32
VA) from PSC to equivalent BPM, confirming the small BPM loading
impact. In addition, an evaluation of increased penetration of BPM
motors in commercial buildings was presented at the ASHRAE 6 ECM Motor
Workshop at the CEC, which reviewed California Utility Codes with
regards to the BPM-specific issue.\64\ It was stated in this study that
while the power factor could be reduced to 50 percent, a BPM motor will
have a lower current draw than a PSC motor at 100 percent power factor
due to efficiency gains.
---------------------------------------------------------------------------
\59\ GE Industrial Systems, GE ECM 2.3 Series motors datasheet
(Available at: https://www.columbiaheating.com/page_images/file/GET-8068.pdf).
\60\ Farmer, C., Hines, P., Dowds, J., Blumsack, S., Modeling
the Impact of Increasing PHEV Loads on the Distribution
Infrastructure, Proceedings of the 43rd International Conference on
System Sciences (2010).
\61\ NEMA. NEMA TP 1-2002: Guide for Determining Energy
Efficiency for Distribution Transformers.
\62\ NEMA Standards Publication TP 1-2002: Guide for Determining
Energy Efficiency for Distribution Transformers (Available at:
https://www.nema.org/Standards/Pages/Guide-for-Determining-Energy-Efficiency-for-Distribution-Transformers.aspx?#download).
\63\ Gusdorf, J., M. Swinton, C. Simpson, E. Enchev, S. Hayden,
D. Furdas, and B. Castellan, Saving Electricity and Reducing GHG
Emissions with ECM Furnace Motors: Results from the CCHT and
Projections to Various Houses and Locations (2004) ACEEE Proceedings
(Available at: https://aceee.org/files/proceedings/2004/data/papers/SS04_Panel1_Paper12.pdf).
\64\ Taylor Engineering LLC, ASHRAE 6 ECM Motors, August 17th
CEC Workshop (2011) California Statewide Utility Code and Standard
Program (Available at: https://www.energy.ca.gov/title24/2013standards/prerulemaking/documents/2011-08-17_workshop/presentations/08%20EC%20Motors.pdf).
---------------------------------------------------------------------------
Regarding the EPRI study \65\ referenced in the JCI comment, DOE
noticed that the power factor impacts are associated with several types
of loads becoming common in the modern household: Low power factor
lighting, modern entertainment systems, and electric vehicle chargers,
as well as HVAC with BPM motors. This reference indicates that the
power quality issues caused by the BPM motors are a small contributor
to the total harmonic distortion experienced at the utility level
compared to all contributing loads. The study indicated that for
devices with an existing 3rd harmonic resonance, the contribution of
all new devices would require filtering; however, this correction is
not attributed to the high penetration of EC motors alone. The BPM's
third harmonic distortion contributed a 1.5-percent current increase to
the circuit. The study showed the overall impact on the 3rd, 5th, 7th
order and included in total harmonic distortion (THD) was within 0.1
percent of the original harmonic profile applied to the studied feeder.
In summary, the impact of introducing BPM motors for HVAC under a high
penetration scenario on a residential line was negligible.
---------------------------------------------------------------------------
\65\ Sharma, H. M. Rylander, and D. Dorr, Grid Impacts due to
Increased Penetration of Newer Harmonic Sources, Proceedings of IEEE
Rural Electric Power Conference (April 2013) pp. B5-1--B5-5
(Available at: https://ieeexplore.ieee.org/stamp/stamp.jsp?tp=&arnumber=6681854).
---------------------------------------------------------------------------
With regards to household power quality, furnaces have a minimum
basic electrical requirement for THD of 5 percent, and individual
harmonic distortion of 3 percent.66 67 Furnaces supplied
with voltages with harmonic distortion greater than 8 percent THD may
not be operated.\68\ The EPRI study, which simulates a harmonic
spectrum of a large number of BPM-based HVAC, shows that the BPM-
related harmonic distortions are within the 5 percent THD limit, and
within the 3 percent individual harmonic limit. Therefore, DOE
concludes the BPM-related harmonic distortions would not cause the
problems cited by the commenters.
---------------------------------------------------------------------------
\66\ IEEE Standard 519-1992--IEEE Recommended Practices and
Requirements for Harmonic Control in Electric Power Systems (April 9
1993) pp. 1-112 (Available at: https://ieeexplore.ieee.org/stamp/stamp.jsp?tp=&arnumber=210894).
\67\ Fluke Corporation, Generator power quality and furnaces:
The effects of harmonic distortion (2009) (Available at: https://support.fluke.com/find-sales/Download/Asset/3497420_6112_ENG_A_W.PDF).
\68\ Id.
---------------------------------------------------------------------------
In addition to the analysis described above, DOE used NEMS-BT,
along with EIA data on the capital cost of various power plant types,
to estimate the reduction in national expenditures for electricity
generating capacity due to potential residential furnace fan standards.
The method used and the results are described in chapter 15 of the
final rule TSD.
N. Employment Impact Analysis
Employment impacts from new or amended energy conservation
standards include direct and indirect impacts. Direct employment
impacts are any changes in the number of employees of manufacturers of
the products subject to standards; the MIA addresses those impacts.
Indirect employment impacts are changes in national employment that
occur due to the shift in expenditures and capital investment caused by
the purchase and operation of more-efficient appliances. Indirect
employment impacts from standards consist of the jobs created or
eliminated in the national economy due to: (1) Reduced spending by end
users on energy; (2) reduced spending on new energy supply by the
utility industry; (3) increased consumer spending on the purchase of
new products; and (4) the effects of those three factors throughout the
economy.
One method for assessing the possible effects on the demand for
labor of such shifts in economic activity is to compare sector
employment statistics developed by the Labor Department's Bureau of
Labor Statistics (BLS). BLS regularly publishes its estimates of the
number of jobs per million dollars of economic activity in different
sectors of the economy, as well as the jobs created elsewhere in the
economy by this same economic activity. Data from BLS indicate that
expenditures in the utility sector generally create fewer jobs (both
directly and indirectly) than expenditures in other sectors of the
economy.\69\ There are many reasons for these differences, including
wage differences and the fact that the utility sector is more capital-
intensive and less labor-intensive than other sectors. Energy
conservation standards have the effect of reducing consumer utility
bills. Because reduced consumer expenditures for energy likely lead to
increased expenditures in other sectors of the economy, the general
effect of efficiency standards is to shift economic activity from a
less labor-intensive sector (i.e., the utility sector) to more labor-
intensive sectors (e.g., the retail and service sectors). Thus, based
on the BLS data alone, DOE believes net national employment may
increase because of shifts in economic activity resulting from energy
conservation standards for residential furnace fans.
---------------------------------------------------------------------------
\69\ See Bureau of Economic Analysis, ``Regional Multipliers: A
User Handbook for the Regional Input-Output Modeling System (RIMS
II),'' U.S. Department of Commerce (1992).
---------------------------------------------------------------------------
For the standard levels considered in today's document, DOE
estimated indirect national employment impacts using an input/output
model of the U.S. economy called Impact of Sector Energy Technologies
version 3.1.1 (ImSET).\70\ ImSET is a special-purpose version of the
``U.S. Benchmark National Input-Output'' (I-O) model, which was
designed to estimate the national employment and income effects of
energy-saving technologies. The ImSET software includes a computer-
based I-O model having structural coefficients that characterize
economic flows among the 187 sectors. ImSET's national economic I-O
structure is based on a 2002 U.S. benchmark table, specially aggregated
to the 187 sectors most relevant to industrial, commercial, and
residential building energy use. DOE notes that ImSET is not a general
equilibrium forecasting model, and understands the uncertainties
involved in projecting employment impacts, especially changes in the
later years of the analysis. Because ImSET does not incorporate price
changes, the employment effects predicted by ImSET
[[Page 38183]]
may over-estimate actual job impacts over the long run. For the final
rule, DOE used ImSET only to estimate short-term (2019 and 2024)
employment impacts.
---------------------------------------------------------------------------
\70\ J. M. Roop, M. J. Scott, and R. W. Schultz, ImSET 3.1:
Impact of Sector Energy Technologies, PNNL-18412, Pacific Northwest
National Laboratory (2009) (Available at: www.pnl.gov/main/publications/external/technical_reports/PNNL-18412.pdf).
---------------------------------------------------------------------------
For more details on the employment impact analysis, see chapter 16
of the final rule TSD.
O. Comments on Proposed Standards
NEEP, CA IOUs, and the Joint Advocates support the selection of
DOE's proposed trial standard level, given the limited impact on
furnace fan manufacturers, positive benefits to consumers, and
substantial energy savings. (NEEP, No. 109 at p. 2; CA IOUs, No. 106 at
p. 2; Joint Advocates, No. 105 at p. 1)
A number of stakeholders disagreed with the proposed selection of
TSL 4. Rheem argued that TSL 4 is not economically justified. (Rheem,
No. 83 at p. 7) Lennox stated that because TSL 4 likely has costs that
are understated, and overly optimistic efficiency projections, DOE
should not pursue TSL 4, and instead adopt standards based on a less-
stringent, less-costly technology. (Lennox, No. 100 at p. 2) EEI
suggested the adoption of TSL 1 or TSL 2 to conserve energy, minimize
economic harm to consumers, and minimize the possible negative impacts
on the electric grid from the motors that would be able to meet the
proposed standard. (EEI, No. 87 at p. 2)
DOE has addressed specific issues regarding costs, efficiency
projections, and possible negative impacts on the electric grid in
previous parts of section IV of this document. DOE addresses the
economic justification for today's standards in section V.C of this
document.
Southern Company believes that under TSL 4, too large a proportion
of consumers have net costs. Southern Company would prefer that a
substantial majority of consumers derive benefits from a proposed rule.
(Southern Company, No. 85 at p. 3) EEI also stated that a much higher
percentages of consumers will experience a net cost than is the case
with many other DOE energy conservation standards. (EEI, No. 87 at p.
2) The Mercatus Center stated that the proposed rule will confer net
benefits on a majority of the consumers for only one product class
(i.e., non-weatherized, non-condensing gas furnace fans). It added that
the aggregate financial benefits to consumers are not spread uniformly
over the population, but instead are mostly concentrated in a minority
of households. (Mercatus Center, No. 82 at p. 7)
As shown in Table V.31 of today's final rule, more consumers would
have a net benefit from standards at TSL 4 than would have a net cost
for all of the considered product classes. For the two largest product
classes (non-weatherized non-condensing gas furnace fans and non-
weatherized condensing gas furnace fans), nearly twice as many
consumers would have a net benefit from standards at TSL 4 as would
have a net cost.
The Mercatus Center stated that seven out of eight proposed
standards at TSL 4 fail the rebuttable payback period benchmark,
thereby making it difficult for DOE to demonstrate economic
justification for the proposed rule. (Mercatus Center, No. 82 at p. 6)
In response, the commenter has misinterpreted the role of the
rebuttable payback period presumption. As discussed in section III.E.2,
EPCA provides that a rebuttable presumption is established that an
energy conservation standard is economically justified if the
additional cost to the consumer of a product that meets the standard is
less than three times the value of the first year's energy savings
resulting from the standard, as calculated under the applicable DOE
test procedure. (42 U.S.C. 6295(o)(2)(B)(iii)) To determine economic
justification, DOE routinely conducts an analysis that considers the
full range of impacts, including those to consumers, manufacturers, the
Nation, and the environment, as required under 42 U.S.C.
6295(o)(2)(B)(i). The results of this analysis serve as the basis for
DOE to definitively evaluate the economic justification for a potential
standard level, thereby supporting or rebutting the results of any
preliminary determination of economic justification.
Rheem and Miller stated that the proposed standard may act as a
transfer payment from lower-income households, who are more likely to
bear net costs as a result of this rule, to higher-income households;
and that higher-priced furnace fans resulting from this rule will be
out of reach for some consumers. They stated that these distributive
impacts necessitate close scrutiny from the Department in order to
determine whether the proposed standards will actually improve social
welfare. (Rheem, No. 83 at p. 14; Miller, No. 79 at p. 14)
DOE's consumer subgroup analysis indicates that, for non-
weatherized gas furnace fans, lower-income households would have
positive average LCC savings and median PBPs less than five years (see
section V.B.1). Furthermore, many lower-income households rent rather
than own their dwelling, and are responsible for utility bills but not
for purchase of a furnace. To the extent that there is delay in the
landlords' passing of extra costs into the rent, consumers that rent
will benefit more those who own, all else being equal.
Ingersoll Rand stated that promulgating a rule at TSL4 would force
the future generation of furnaces sold in the U.S. to be less reliable
than many of those on the market today as a result of eliminating PSC
motors from the market. (Ingersoll Rand, No. 107 at p. 7) DOE notes
that furnace fans meeting today's standards are already widely
available as a substitute for units with baseline motors. DOE evaluated
issues related to reliability, as discussed in section IV.F.2, and
concluded that the benefits to consumers outweigh any costs related to
reliability that may be associated with products meeting the standards.
V. Analytical Results and Conclusions
This section addresses the results from DOE's analyses with respect
to potential energy conservation standards for residential furnace
fans. It addresses the TSLs examined by DOE, the projected impacts of
each of these levels if adopted as energy conservation standards for
furnace fans, and the standard levels ultimately adopted by DOE in
today's final rule. Additional details regarding DOE's analyses are
contained in the TSD supporting this document.
A. Trial Standard Levels
DOE developed trial standard levels (TSLs) that combine efficiency
levels for each product class of residential furnace fans. Table V.1
presents the efficiency levels for each product class in each TSL. TSL
6 consists of the max-tech efficiency levels. TSL 5 consists of those
efficiency levels that provide the maximum NPV using a 7-percent
discount rate (see section V.B.3 for NPV results). TSL 4 consists of
those efficiency levels that provide the highest NPV using a 7-percent
discount rate, and that also result in a higher percentage of consumers
that receive an LCC benefit than experience an LCC loss (see section
V.B.1 for LCC results). TSL 3 uses efficiency level 3 for all product
classes. TSL 2 consists of efficiency levels that are the same as TSL 3
for non-weatherized gas furnace fans, weatherized gas furnace fans, and
electric furnace fans, but are at efficiency level 1 for oil-fired
furnace fans and mobile home furnace fans. TSL 1 consists of the most
common efficiency levels in the current market. In summary, Table V.1
presents the six TSLs which DOE has identified for residential furnace
fans, including the efficiency level associated with each
[[Page 38184]]
TSL, the technology options anticipated to achieve those levels, and
the expected resulting percentage reduction in FER from the baseline
corresponding to each efficiency level.
Table V.1--Trial Standard Levels for Residential Furnace Fans
----------------------------------------------------------------------------------------------------------------
Trial standard levels (Efficiency level) *
Product class -----------------------------------------------------------------
1 2 3 4 5 6
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace 1 3 3 4 4 6
Fan..........................................
Non-Weatherized, Condensing Gas Furnace Fan... 1 3 3 4 4 6
Weatherized Non-Condensing Gas Furnace Fan.... 1 3 3 4 4 6
Non-Weatherized, Non-Condensing Oil Furnace 1 1 3 1 3 6
Fan..........................................
Non-Weatherized Electric Furnace/Modular 1 3 3 4 4 6
Blower Fan...................................
Mobile Home Non-Weatherized, Non-Condensing 1 1 3 1 3 6
Gas Furnace Fan..............................
Mobile Home Non-Weatherized, Condensing Gas 1 1 3 1 3 6
Furnace Fan..................................
Mobile Home Electric Furnace/Modular Blower 1 1 3 4 4 6
Fan..........................................
----------------------------------------------------------------------------------------------------------------
* Efficiency level (EL) 1 = Improved PSC (12 percent). (For each EL, the percentages given refer to percent
reduction in FER from the baseline level.) EL 2 = Inverter-driven PSC (25 percent). EL 3 = Constant-torque BPM
motor (38 percent). EL 4 = Constant-torque BPM motor + Multi-Staging (51 percent). EL 5 = Constant-airflow BPM
motor (57 percent). EL 6 = Constant-airflow BPM motor + Multi-Staging (61 percent).
B. Economic Justification and Energy Savings
1. Economic Impacts on Consumers
Life-Cycle Cost and Payback Period
To evaluate the economic impact of the considered efficiency levels
on consumers, DOE conducted an LCC analysis for each efficiency level.
More-efficient residential furnace fans would affect these consumers in
two ways: (1) Annual operating expense would decrease; and (2) purchase
price would increase. Inputs used for calculating the LCC include total
installed costs (i.e., equipment price plus installation costs),
operating expenses (i.e., energy costs, repair costs, and maintenance
costs), product lifetime, and discount rates.
The output of the LCC model is a mean LCC savings (or cost) for
each product class, relative to the base-case efficiency distribution
for residential furnace fans. The LCC analysis also provides
information on the percentage of consumers for whom an increase in the
minimum efficiency standard would have a positive impact (net benefit),
a negative impact (net cost), or no impact.
DOE also performed a PBP analysis as part of the LCC analysis. The
PBP is the number of years it would take for the consumer to recover
the increased costs of higher-efficiency products as a result of energy
savings based on the operating cost savings. The PBP is an economic
benefit-cost measure that uses benefits and costs without discounting.
Chapter 8 of the final rule TSD provides detailed information on the
LCC and PBP analyses.
DOE's LCC and PBP analyses provide five key outputs for each
efficiency level above the baseline, as reported in Table V.2 through
Table V.9 for the considered TSLs. (Results for all efficiency levels
are reported in chapter 8 of the final rule TSD.) These outputs include
the proportion of residential furnace fan purchases in which the
purchase of a furnace fan compliant with the new energy conservation
standard creates a net LCC increase, no impact, or a net LCC savings
for the consumer. Another output is the average LCC savings from
standards-compliant products, as well as the median PBP for the
consumer investment in standards-compliant products. Savings are
measured relative to the base-case efficiency distribution (see section
IV.F.4), not the baseline efficiency level.
Table V.2--LCC and PBP Results for Non-Weatherized, Non-Condensing Gas Furnace Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Life-cycle cost 2013$ Life-cycle cost savings
----------------------------------------------------------------------------------
Percent of consumers that Median
Efficiency level TSL Discounted Average experience payback
Installed operating LCC savings --------------------------------- period
cost cost 2013$ Net years
Net cost No impact benefit
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baseline.............................. ................... $347 $2,194 $2,541 $0 0 100 0 .........
1..................................... 1.................. 359 1,933 2,292 85 1 68 30 1.1
2..................................... ................... 408 1,655 2,063 263 25 25 50 3.8
3..................................... 2, 3............... 423 1,367 1,791 471 17 25 58 2.6
4..................................... 4, 5............... 501 1,249 1,750 506 30 14 56 5.4
5..................................... ................... 658 1,244 1,902 373 47 12 41 10.6
6..................................... 6.................. 694 1,150 1,844 431 50 0 50 10.2
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 38185]]
Table V.3--LCC and PBP Results for Non-Weatherized, Condensing Gas Furnace Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Life-cycle cost 2013$ Life-cycle cost savings
----------------------------------------------------------------------------------
Percent of consumers that Median
Efficiency level TSL Discounted Average experience payback
Installed operating LCC savings --------------------------------- period
cost cost 2013$ Net years
Net cost No impact benefit
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baseline.............................. ................... $343 $2,134 $2,478 $0 0 100 0 .........
1..................................... 1.................. 355 1,909 2,264 58 1 75 24 1.2
2..................................... ................... 403 1,666 2,070 182 21 41 38 4.2
3..................................... 2, 3............... 416 1,402 1,818 335 11 41 48 2.9
4..................................... 4, 5............... 493 1,319 1,812 341 23 34 43 5.8
5..................................... ................... 652 1,334 1,987 219 42 29 30 12.0
6..................................... 6.................. 687 1,250 1,937 268 51 0 49 11.0
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table V.4--LCC and PBP Results for Weatherized, Non-Condensing Gas Furnace Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Life-cycle cost 2013$ Life-cycle cost savings
----------------------------------------------------------------------------------
Percent of consumers that Median
Efficiency level TSL Discounted Average experience payback
Installed operating LCC savings --------------------------------- period
cost cost 2013$ Net years
Net cost No Impact benefit
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baseline.............................. ................... $333 $2,667 $3,000 $0 0 100 0 .........
1..................................... 1.................. 345 2,329 2,674 67 0 81 19 0.7
2..................................... ................... 393 2,025 2,418 189 8 56 36 3.2
3..................................... 2, 3............... 406 1,609 2,015 378 3 56 41 1.8
4..................................... 4, 5............... 481 1,434 1,914 447 16 33 51 4.4
5..................................... ................... 633 1,476 2,109 304 38 27 35 10.3
6..................................... 6.................. 668 1,354 2,022 391 41 0 59 8.2
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table V.5--LCC and PBP Results for Non-Weatherized, Non-Condensing Oil Furnace Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Life-cycle cost 2013$ Life-cycle cost savings
----------------------------------------------------------------------------------
Percent of consumers that Median
Efficiency level TSL Discounted Average experience payback
Installed operating LCC savings --------------------------------- period
cost cost 2013$ Net years
Net cost No impact benefit
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baseline.............................. ................... $417 $2,510 $2,927 $0 0 100 0 .........
1..................................... 1, 2, 4............ 427 2,356 2,783 46 13 71 17 1.7
2..................................... ................... 501 2,090 2,592 181 46 28 26 10.3
3..................................... 3, 5............... 507 1,979 2,486 259 44 28 28 4.6
4..................................... ................... 589 1,920 2,509 244 48 28 24 8.1
5..................................... ................... 813 1,922 2,736 80 56 28 16 18.3
6..................................... 6.................. 863 1,873 2,736 80 78 0 22 18.6
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table V.6--LCC and PBP Results for Non-Weatherized Electric Furnace/Modular Blower Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Life-cycle cost 2013$ Life-cycle cost savings
----------------------------------------------------------------------------------
Percent of consumers that Median
Efficiency level TSL Discounted Average experience payback
Installed operating LCC savings --------------------------------- period
cost cost 2013$ Net years
Net cost No impact benefit
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baseline.............................. ................... $244 $1,211 $1,455 $0 0 100 0 .........
1..................................... 1.................. 255 1,079 1,335 29 4 73 22 1.9
2..................................... ................... 299 941 1,241 88 27 37 36 6.2
3..................................... 2, 3............... 292 797 1,089 181 17 37 45 2.6
4..................................... 4, 5............... 309 747 1,055 204 23 25 51 3.2
5..................................... ................... 444 796 1,240 66 48 25 27 12.0
6..................................... 6.................. 477 748 1,225 81 60 0 39 11.5
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 38186]]
Table V.7--LCC and PBP Results for Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Life-cycle cost 2013$ Life-cycle cost savings
----------------------------------------------------------------------------------
Percent of consumers that Median
Efficiency level TSL Discounted Average experience payback
Installed operating LCC savings --------------------------------- period
cost cost 2013$ Net years
Net cost No impact benefit
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baseline.............................. ................... $256 $1,118 $1,374 $0 0 100 0 .........
1..................................... 1, 2, 4............ 268 1,026 1,293 36 10 56 34 2.7
2..................................... ................... 313 930 1,243 87 62 0 38 10.2
3..................................... 3, 5............... 318 867 1,185 144 55 0 45 6.8
4..................................... ................... 390 831 1,222 108 67 0 33 12.7
5..................................... ................... 530 853 1,383 (54) 81 0 19 24.3
6..................................... 6.................. 563 824 1,388 (58) 80 0 20 24.4
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Parentheses indicate negative values.
Table V.8--LCC and PBP Results for Mobile Home Non-Weatherized, Condensing Gas Furnace Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Life-cycle cost 2013$ Life-cycle cost savings
----------------------------------------------------------------------------------
Percent of consumers that Median
Efficiency level TSL Discounted Average experience payback
Installed operating LCC savings --------------------------------- period
cost cost 2013$ Net years
Net cost No impact benefit
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baseline.............................. ................... $274 $1,283 $1,556 $0 0 100 0 .........
1..................................... 1, 2, 4............ 285 1,170 1,454 35 5 68 27 2.3
2..................................... ................... 330 1,061 1,391 79 43 29 28 9.7
3..................................... 3, 5............... 339 977 1,316 133 37 29 33 6.6
4..................................... ................... 411 936 1,347 103 66 4 29 15.8
5..................................... ................... 558 953 1,510 (53) 80 4 16 33.3
6..................................... 6.................. 591 917 1,508 (51) 82 0 18 31.3
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Parentheses indicate negative values.
Table V.9--LCC and PBP Results for Mobile Home Electric Furnace/Modular Blower Fan
--------------------------------------------------------------------------------------------------------------------------------------------------------
Life-cycle cost 2013$ Life-cycle cost savings
----------------------------------------------------------------------------------
Percent of consumers that Median
Efficiency level TSL Discounted Average experience payback
Installed operating LCC savings --------------------------------- period
cost cost 2013$ Net years
Net cost No impact benefit
--------------------------------------------------------------------------------------------------------------------------------------------------------
Baseline.............................. ................... $194 $643 $837 $0 0 100 0 .........
1..................................... 1, 2............... 204 575 778 19 7 71 22 2.1
2..................................... ................... 245 531 777 20 36 38 26 8.9
3..................................... 3.................. 237 466 702 70 26 38 37 3.6
4..................................... 4, 5............... 251 433 685 85 32 26 43 4.1
5..................................... ................... 375 487 862 (48) 57 26 18 15.0
6..................................... 6.................. 406 462 868 (54) 75 0 25 14.9
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Parentheses indicate negative values.
Consumer Subgroup Analysis
DOE estimated the impacts of the considered efficiency levels
(TSLs) on the following consumer subgroups: (1) Senior-only households;
and (2) low-income households. The results of the consumer subgroup
analysis indicate that for residential furnace fans, senior-only
households and low-income households experience lower average LCC
savings and longer payback periods than consumers overall, with the
difference being larger for low-income households. The difference
between the two subgroups and all consumers is larger for non-
weatherized, non-condensing gas furnace fans (see Table V.10) than for
non-weatherized, condensing gas furnace fans (see Table V.11). Chapter
11 of the final rule TSD provides more detailed discussion on the
consumer subgroup analysis and results for the other product classes.
[[Page 38187]]
Table V.10--Comparison of Impacts for Consumer Subgroups With All Consumers, Non-Weatherized, Non-Condensing Gas Furnace Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Average life-cycle cost savings (2013$) Median payback period (years)
-----------------------------------------------------------------------------------------------------------
Efficiency level All All
TSL Senior-only Low-income consumers Senior-only Low-income consumers
--------------------------------------------------------------------------------------------------------------------------------------------------------
1........................................... 1........................... $65 $48 $85 1.6 1.7 1.1
2........................................... ............................ 209 133 263 5.2 6.3 3.8
3........................................... 2, 3........................ 366 251 471 3.7 3.6 2.6
4........................................... 4, 5........................ 373 234 506 7.6 7.8 5.4
5........................................... ............................ 226 77 373 14.5 15.9 10.6
6........................................... 6........................... 264 96 431 13.7 15.3 10.2
--------------------------------------------------------------------------------------------------------------------------------------------------------
Table V.11--Comparison of Impacts for Consumer Subgroups With All Consumers, Non-Weatherized, Condensing Gas Furnace Fans
--------------------------------------------------------------------------------------------------------------------------------------------------------
Average life-cycle cost savings (2013$) Median payback period (years)
-----------------------------------------------------------------------------------------------------------
Efficiency level All All
TSL Senior-only Low-income consumers Senior-only Low-income consumers
--------------------------------------------------------------------------------------------------------------------------------------------------------
1........................................... 1........................... $49 $38 $58 1.5 2.0 1.2
2........................................... ............................ 155 121 182 5.5 7.1 4.2
3........................................... 2, 3........................ 288 230 335 3.7 4.4 2.9
4........................................... 4, 5........................ 275 202 341 7.5 9.7 5.8
5........................................... ............................ 141 66 219 15.4 19.5 12.0
6........................................... 6........................... 178 90 268 12.2 17.0 11.0
--------------------------------------------------------------------------------------------------------------------------------------------------------
Rebuttable Presumption Payback
As discussed in section III.E.2, EPCA provides a rebuttable
presumption that, in essence, an energy conservation standard is
economically justified if the increased purchase cost for a product
that meets the standard is less than three times the value of the
first-year energy savings resulting from the standard. However, DOE
routinely conducts a full economic analysis that considers the full
range of impacts, including those to the consumer, manufacturer,
Nation, and environment, as required under 42 U.S.C. 6295(o)(2)(B)(i).
The results of this analysis serve as the basis for DOE to definitively
evaluate the economic justification for a potential standard level,
thereby supporting or rebutting the results of any preliminary
determination of economic justification. For comparison with the more
detailed analytical results, DOE calculated a rebuttable presumption
payback period for each TSL. Table V.12 shows the rebuttable
presumption payback results to determine whether any of them meet the
rebuttable presumption conditions for the residential furnace fans
product classes.
Table V.12--Rebuttable Presumption Payback Periods for Residential Furnace Fan Product Classes
----------------------------------------------------------------------------------------------------------------
Rebuttable presumption payback (years)
Product class -----------------------------------------------------------------
TSL 1 TSL 2 TSL 3 TSL 4 TSL 5 TSL 6
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace 3.3 5.3 5.3 10.3 10.3 19.4
Fan..........................................
Non-Weatherized, Condensing Gas Furnace Fan... 3.1 4.9 4.9 9.6 9.6 18.2
Weatherized Non-Condensing Gas Furnace Fan.... 3.0 4.8 4.8 9.4 9.4 17.6
Non-Weatherized, Non-Condensing Oil Furnace 2.3 2.3 5.9 2.3 5.9 19.8
Fan..........................................
Non-Weatherized Electric Furnace/Modular 3.2 5.1 5.1 5.8 5.8 15.4
Blower Fan...................................
Mobile Home Non-Weatherized, Non-Condensing 3.8 3.8 6.1 3.8 6.1 22.1
Gas Furnace Fan..............................
Mobile Home Non-Weatherized, Condensing Gas 3.5 3.5 5.7 3.5 5.7 20.9
Furnace Fan..................................
Mobile Home Electric Furnace/Modular Blower 4.3 4.3 6.8 7.7 7.7 20.2
Fan..........................................
----------------------------------------------------------------------------------------------------------------
2. Economic Impact on Manufacturers
As noted above, DOE performed an MIA to estimate the impact of new
energy conservation standards on manufacturers of residential furnace
fans. The following section describes the expected impacts on
manufacturers at each considered TSL. Chapter 12 of the final rule TSD
explains the analysis in further detail.
Industry Cash-Flow Analysis Results
Table V.13 and Table V.14 depict the financial impacts (represented
by changes in INPV) of new energy standards on manufacturers of
residential furnace fans, as well as the conversion costs that DOE
expects manufacturers would incur for all product classes at each TSL.
To evaluate the range of cash flow impacts on the residential furnace
fans industry, DOE modeled two different mark-up scenarios using
different assumptions that correspond to the range of anticipated
market responses to potential new energy conservation standards: (1)
The preservation of gross
[[Page 38188]]
margin percentage; and (2) the preservation of per-unit operating
profit. Each of these scenarios is discussed immediately below.
To assess the lower (less severe) end of the range of potential
impacts, DOE modeled a preservation of gross margin percentage markup
scenario, in which a uniform ``gross margin percentage'' markup is
applied across all potential efficiency levels. In this scenario, DOE
assumed that a manufacturer's absolute dollar markup would increase as
production costs increase in the standards case.
To assess the higher (more severe) end of the range of potential
impacts, DOE modeled the preservation of per-unit operating profit
markup scenario, which assumes that manufacturers would be able to earn
the same operating margin in absolute dollars per-unit in the standards
case as in the base case. In this scenario, while manufacturers make
the necessary investments required to convert their facilities to
produce new standards-compliant products, operating profit does not
change in absolute dollars per unit and decreases as a percentage of
revenue.
The set of results below shows potential INPV impacts for
residential furnace fan manufacturers; Table V.13 reflects the lower
bound of impacts, and Table V.14 represents the upper bound.
Each of the modeled scenarios results in a unique set of cash flows
and corresponding industry values at each TSL. In the following
discussion, the INPV results refer to the difference in industry value
between the base case and each standards case that results from the sum
of discounted cash flows from the base year 2014 through 2048, the end
of the analysis period. To provide perspective on the short-run cash
flow impact, DOE includes in the discussion of the results below a
comparison of free cash flow between the base case and the standards
case at each TSL in the year before new standards would take effect.
This figure provides an understanding of the magnitude of the required
conversion costs relative to the cash flow generated by the industry in
the base case.
Table V.13--Manufacturer Impact Analysis for Residential Furnace Fans--Preservation of Gross Margin Percentage Markup Scenario *
--------------------------------------------------------------------------------------------------------------------------------------------------------
Trial standard level
Units Base case -----------------------------------------------------------------
1 2 3 4 5 6
--------------------------------------------------------------------------------------------------------------------------------------------------------
INPV.......................................... $M......................... 349.6 336.6 360.0 359.1 397.8 397.6 422.4
Change in INPV................................ $M......................... ......... (13.0) 10.4 9.4 48.2 48.0 72.8
(%)........................ ......... (3.7) 3.0 2.7 13.8 13.7 20.8
Product Conversion Costs...................... $M......................... 2.2 18.8 23.6 25.3 25.5 27.1 29.4
Capital Conversion Costs...................... $M......................... ......... 8.8 11.1 11.8 15.1 15.7 134.7
Total Conversion Costs........................ $M......................... 2.2 27.7 34.7 37.1 40.6 42.8 164.2
Free Cash Flow (2018)......................... $M......................... 20.3 11.3 8.8 8.0 6.4 5.6 (48.6)
Free Cash Flow (change from Base Case) (2018). %.......................... 0.0 (44.5) (56.7) (60.8) (68.3) (72.2) (339.8)
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Values in parentheses are negative values. All values have been rounded to the nearest tenth.
M = millions.
Table V.14--Manufacturer Impact Analysis for Residential Furnace Fans--Preservation of Operating Profit Markup Scenario *
--------------------------------------------------------------------------------------------------------------------------------------------------------
Trial standard level
Units Base case -----------------------------------------------------------------
1 2 3 4 5 6
--------------------------------------------------------------------------------------------------------------------------------------------------------
INPV.......................................... $M......................... 349.6 332.3 313.2 311.0 290.6 288.8 147.2
Change in INPV................................ $M......................... ......... (17.3) (36.4) (38.6) (59.0) (60.8) (202.5)
(%)........................ ......... (5.0) (10.4) (11.0) (16.9) (17.4) (57.9)
Product Conversion Costs...................... $M......................... 2.2 18.8 23.6 25.3 25.5 27.1 29.4
Capital Conversion Costs...................... $M......................... ......... 8.8 11.1 11.8 15.1 15.7 134.7
Total Conversion Costs........................ $M......................... 2.2 27.7 34.7 37.1 40.6 42.8 164.2
Free Cash Flow................................ $M......................... 20.3 11.3 8.8 8.0 6.4 5.6 (48.6)
Free Cash Flow (change from Base Case)........ %.......................... 0.0 (44.5) (56.7) (60.8) (68.3) (72.2) (339.8)
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Values in parentheses are negative values. All values have been rounded to the nearest tenth.
M = millions.
TSL 1 represents the most common efficiency levels in the current
market for all product classes. At TSL 1, DOE estimates impacts on INPV
for residential furnace fan manufacturers to range from -$17.3 million
to -$13.0 million, or a change in INPV of -5.0 percent to -3.7 percent.
At this potential standard level, industry free cash flow is estimated
to decrease by as much as 44.5 percent to $11.3 million, compared to
the base-case value of $20.3 million in the year before the compliance
date (2018). DOE anticipates industry conversion costs totaling $27.7
million at TSL 1.
TSL 2 represents EL 1 for the oil and mobile home product classes,
and EL 3 for all other product classes. At TSL 2, DOE estimates impacts
on INPV for residential furnace fan manufacturers to range from -$36.4
million to $10.4 million, or a change in INPV of -10.4 percent to 3.0
percent. At this potential standard level, industry free cash flow is
estimated to decrease by as much as 56.7 percent to $8.8 million,
compared to the base-case value of $20.3 million in the year before the
compliance date (2018). DOE anticipates industry conversion costs of
$34.7 million at TSL 2.
TSL 3 represents EL 3 for all product classes. At TSL 3, DOE
estimates impacts on INPV for residential furnace fan manufacturers to
range from -$38.6 million to $9.4 million, or a change in INPV of -11.0
percent to 2.7 percent. At this potential standard level,
[[Page 38189]]
industry free cash flow is estimated to decrease by as much as 60.8
percent to $8.0 million, compared to the base-case value of $20.3
million in the year before the compliance date (2018). DOE anticipates
industry conversion costs of $37.1 million at TSL 3.
TSL 4 represents the efficiency levels that provide the highest NPV
using a 7-percent discount rate, and that also result in a higher
percentage of consumers receiving an LCC benefit rather than an LCC
loss. At TSL 4, DOE estimates impacts on INPV for residential furnace
fan manufacturers to range from -$59.0 million to $48.2 million, or a
change in INPV of -16.9 percent to 13.8 percent. At this potential
standard level, industry free cash flow is estimated to decrease by as
much as 68.3 percent to $6.4 million, compared to the base-case value
of $20.3 million in the year before the compliance date (2018). DOE
anticipates industry conversion costs totaling $40.6 million at TSL 4.
TSL 5 represents the efficiency levels that provide the maximum NPV
using a 7-percent discount rate. At TSL 5, DOE estimates impacts on
INPV for residential furnace fan manufacturers to range from -$60.8
million to $48.0 million, or a change in INPV of -17.4 percent to 13.7
percent. At this potential standard level, industry free cash flow is
estimated to decrease by as much as 72.2 percent to $5.6 million,
compared to the base-case value of $20.3 million in the year before the
compliance date (2018). DOE anticipates industry conversion costs of
$42.8 million at TSL 5.
TSL 6 represents the max-tech efficiency level for all product
classes. At TSL 6, DOE estimates impacts on INPV for residential
furnace fan manufacturers to range from -$202.5 million to $72.8
million, or a change in INPV of -57.9 percent to 20.8 percent. At this
potential standard level, industry free cash flow is estimated to
decrease by as much as 339.8 percent to -$48.6 million, compared to the
base-case value of $20.3 million in the year before the compliance date
(2018). DOE anticipates industry conversion costs totaling $164.2
million at TSL 6.
DOE anticipates very high capital conversion costs at TSL 6 because
manufacturers would need to make significant changes to their
manufacturing equipment and production processes in order to
accommodate the use of backward-inclined impellers. This design option
would require modifying, or potentially eliminating, current fan
housings. DOE also anticipates high product conversion costs to develop
new designs with backward-inclined impellers for all their products.
Some manufacturers may also have stranded assets from specialized
machines for building fan housing that can no longer be used.
Impacts on Employment
To quantitatively assess the impacts of energy conservation
standards on direct employment in the residential furnace fan industry,
DOE used the GRIM to estimate the domestic labor expenditures and
number of employees in the base case and at each TSL from 2014 through
2048. DOE used statistical data from the U.S. Census Bureau's 2011
Annual Survey of Manufacturers (ASM),\71\ the results of the
engineering analysis, and interviews with manufacturers to determine
the inputs necessary to calculate industry-wide labor expenditures and
domestic employment levels. Labor expenditures related to manufacturing
of the product are a function of the labor intensity of the product,
the sales volume, and an assumption that wages remain fixed in real
terms over time. The total labor expenditures in each year are
calculated by multiplying the MPCs by the labor percentage of MPCs.
---------------------------------------------------------------------------
\71\ ``Annual Survey of Manufactures (ASM),'' U.S. Census Bureau
(2011) (Available at: https://www.census.gov/manufacturing/asm/).
---------------------------------------------------------------------------
The total labor expenditures in the GRIM were then converted to
domestic production employment levels by dividing production labor
expenditures by the annual payment per production worker (production
worker hours times the labor rate found in the U.S. Census Bureau's
2011 ASM). The estimates of production workers in this section cover
workers, including line-supervisors who are directly involved in
fabricating and assembling a product within the manufacturing facility.
Workers performing services that are closely associated with production
operations, such as materials handling tasks using forklifts, are also
included as production labor. DOE's estimates only account for
production workers who manufacture the specific products covered by
this rulemaking.
The total direct employment impacts calculated in the GRIM are the
sum of the changes in the number of production workers resulting from
the new energy conservation standards for residential furnace fans, as
compared to the base case.
Table V.15--Potential Changes in the Number of Furnace Fan Industry Employment in 2019
--------------------------------------------------------------------------------------------------------------------------------------------------------
Trial standard level *
------------------------------------------------------------------------------------------------------------------------
Base case 1 2 3 4 5 6
--------------------------------------------------------------------------------------------------------------------------------------------------------
Total Number of Domestic 303 303............ 303........... 303........... 301............... 301............... 349.
Production Workers in 2019
(assuming no changes in
production locations).
Total Number of Domestic Non- 107 107............ 107........... 107........... 106............... 106............... 123.
Production Workers in 2019.
Range of Potential Changes in .......... (410) to 0..... (410) to 0.... (410) to 0.... (410) to (3)...... (410) to (3)...... (410) to 62.
Domestic Workers in 2019 **.
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Numbers in parentheses represent negative values.
** DOE presents a range of potential employment impacts, where the lower range represents the scenario in which all domestic manufacturers move
production to other countries.
The employment impacts shown in Table V.15 represent the potential
production and non-production employment changes that could result
following the compliance date of a new energy conservation standard for
residential furnace fans. The upper end of the results in the table
estimates the maximum increase in the number of production and non-
production workers after the implementation of new energy conservation
standards, and it assumes
[[Page 38190]]
that manufacturers would continue to produce the same scope of covered
products within the United States. The lower end of the range indicates
the total number of U.S. production and non-production workers in the
industry who could lose their jobs if all existing production were
moved outside of the United States or if companies exited the market.
This scenario is highly conservative. Even if all production was
relocated overseas, manufacturers would likely maintain large portions
of domestic non-production staff (e.g., sales, marketing, technical,
and management employees). The industry did not provide sufficient
information for DOE fully quantify the percentage of the non-production
workers that would leave the country or be eliminated at each evaluated
standard level.
For residential furnace fans, DOE does not expect significant
changes in domestic employment levels from baseline to TSL 5. Based on
the engineering analysis, DOE has concluded that most product lines
could be converted to meet the standard with changes in motor
technology and the application of multi-staging designs. While such
designs require more controls and have more complex assembly, DOE does
not believe the per-unit labor requirements for the furnace fan
assembly would change significantly.
The only standard level at which significant changes in employment
would be expected is at TSL 6, the max-tech level. At TSL 6, DOE
estimates increases in labor costs because backwards-inclined impeller
assemblies are heavier and require more robust mounting approaches than
are currently used for forward-curved impeller assemblies. Backward-
inclined impeller assemblies could require manufacturers to adjust
their assembly processes, with the potential for increases in per-unit
labor requirements. However, DOE received limited feedback from
manufacturers regarding the labor required to produce furnace fans with
backward-curved impellers, because they generally do not have any
experience in working with this design option.
DOE notes that the employment impacts discussed here are
independent of the indirect employment impacts to the broader U.S.
economy, which are documented in chapter 15 of the final rule TSD.
Impacts on Manufacturing Capacity
According to the residential furnace fan manufacturers interviewed,
the new energy conservation standards being adopted in today's final
rule would not significantly affect manufacturers' production capacity,
or throughput levels. Some manufacturers noted in interviews that
testing resources could potentially be a bottleneck to the conversion
process and cited the potential need for adding in-house testing
capacity. However, in written comments, stakeholders generally agreed
that a five-year lead time between the publication date and compliance
date is appropriate for this rulemaking.
Impacts on Subgroups of Manufacturers
Small manufacturers, niche equipment manufacturers, and
manufacturers exhibiting a cost structure substantially different from
the industry average could be affected disproportionately. As discussed
in section IV.J, using average cost assumptions developed for an
industry cash-flow estimate is inadequate to assess differential
impacts among manufacturer subgroups.
For the residential furnace fans industry, DOE identified and
evaluated the impact of new energy conservation standards on one
subgroup, specifically small manufacturers. The SBA defines a ``small
business'' as having 750 employees or less for NAICS 333415, ``Air-
Conditioning and Warm Air Heating Equipment and Commercial and
Industrial Refrigeration Equipment Manufacturing.'' Based on this
definition, DOE identified 15 manufacturers in the residential furnace
fans industry that qualify as small businesses. For a discussion of the
impacts on the small manufacturer subgroup, see the regulatory
flexibility analysis in section VI.B of this notice and chapter 12 of
the final rule TSD.
Cumulative Regulatory Burden
While any one regulation may not impose a significant burden on
manufacturers, the combined effects of recent or impending regulations
may have serious consequences for some manufacturers, groups of
manufacturers, or an entire industry. Assessing the impact of a single
regulation may overlook this cumulative regulatory burden. In addition
to energy conservation standards, other regulations can significantly
affect manufacturers' financial operations. Multiple regulations
affecting the same manufacturer can strain profits and lead companies
to abandon product lines or markets with lower expected future returns
than competing products. For these reasons, DOE conducts an analysis of
cumulative regulatory burden as part of its rulemakings pertaining to
appliance efficiency.
During previous stages of this rulemaking, DOE identified a number
of requirements in addition to new energy conservation standards for
residential furnace fans. The following section briefly summarizes
those identified regulatory requirements and addresses comments DOE
received with respect to cumulative regulatory burden, as well as other
key related concerns that manufacturers raised during interviews.
While the cumulative regulatory burden analysis contained in the
NOPR reflects manufacturers' concerns regarding CC&E costs, DOE has
decided to exclude CC&E costs from the cumulative burden analysis for
the final rule. The furnace fan test procedure changed from the NOPR to
the final rule. Much of the concern relating to CC&E costs expressed by
stakeholders, and summarized in the NOPR, had to do with the old test
procedure. The new test procedure reduces burden substantially. Also,
for the final rule, CC&E costs have been explicitly incorporated into
product conversion costs inputted into the GRIM, so they are no longer
considered separately in the cumulative regulatory burdens section.
DOE Energy Conservation Standards
Companies that produce a wide range of regulated products and
equipment may face more capital and product development expenditures
than competitors with a narrower scope of products and equipment. Many
furnace fan manufacturers also produce other residential and commercial
equipment. In addition to the amended energy conservation standards for
furnace fans, these manufacturers contend with several other Federal
regulations and pending regulations that apply to other products and
equipment. DOE recognizes that each regulation can significantly affect
a manufacturer's financial operations. Multiple regulations affecting
the same manufacturer can quickly strain manufacturers' profits and
possibly cause an exit from the market. Table V.16 lists the other DOE
energy conservation standards that could also affect manufacturers of
furnace fans in the 3 years leading up to and after the compliance date
of the new energy conservation standards for this equipment.
Additionally, at the request of stakeholders, DOE has listed several
DOE rulemakings in the table below that are currently in process but
that have not been finalized.
[[Page 38191]]
Table V.16--Other DOE Regulations Impacting Furnace Fan Manufacturers
----------------------------------------------------------------------------------------------------------------
Number of
Regulation Compliance impacted Estimated total industry conversion costs
year companies
----------------------------------------------------------------------------------------------------------------
Commercial Refrigeration Equipment... 2017 4 $184.0 million (2012$).
Commercial Packaged Air-Conditioning * 2018 24 N/A.**
and Heating Equipment.
Commercial/Industrial Fans and * 2019 29 N/A.**
Blowers.
Residential Boilers.................. * 2019 9 N/A.**
Residential Non-Weatherized Gas n/a 38 N/A.**
Furnaces.
----------------------------------------------------------------------------------------------------------------
* The dates listed are an approximation. The exact dates are pending final DOE action.
** For energy conservation standards that have not been issued, DOE does not have finalized industry conversion
cost data available.
EPA ENERGY STAR
During interviews, some manufacturers stated that ENERGY STAR
specifications for residential furnaces, central air conditioners, and
heat pumps would be a source of cumulative regulatory burden. ENERGY
STAR specifications are as follows:
Table V.17--ENERGY STAR Specifications for HVAC Products That Use
Furnace Fans
------------------------------------------------------------------------
------------------------------------------------------------------------
Gas Furnaces...................... Rating of 90% AFUE or greater for
U.S. South gas furnaces.
Rating of 95% AFUE or greater for
U.S. North gas furnaces.
Less than or equal to 2.0% furnace
fan efficiency.*
Oil Furnaces...................... Rating of 85% AFUE or greater.
Less than or equal to 2.0% furnace
fan efficiency.*
Air-Source Heat Pumps............. >= 8.2 HSPF/>= 14.5 SEER/>= 12 EER
for split systems.
>= 8.0 HSPF/>= 14 SEER/>=11 EER for
single-package equipment.
Central Air Conditioners.......... >= 14.5 SEER/>= 12 EER for split
systems.
>= 14 SEER/>=11 EER for single-
package equipment.
------------------------------------------------------------------------
* Furnace fan efficiency in this context is furnace fan electrical
consumption as a percentage of total furnace energy consumption in
heating mode.
DOE realizes that the cumulative effect of several regulations on
an industry may significantly increase the burden faced by
manufacturers that need to comply with multiple regulations and
certification programs from different organizations and levels of
government. However, DOE notes that certain standards, such as ENERGY
STAR, are optional for manufacturers. As they are voluntary standards,
they are not considered by DOE to be part of manufacturers' cumulative
regulatory burden.
DOE discusses these and other requirements (e.g., Canadian Energy
Efficiency Regulations, California Title 24, Low NOX
requirements), and includes the full details of the cumulative
regulatory burden analysis, in chapter 12 of the final rule TSD. DOE
also discusses the impacts on the small manufacturer subgroup in the
regulatory flexibility analysis in section VI.B of this final rule.
3. National Impact Analysis
Significance of Energy Savings
For each TSL, DOE projected energy savings for residential furnace
fans purchased in the 30-year period that begins in the first full year
of compliance with amended standards (2019-2048). The savings are
measured over the entire lifetime of products purchased in the 30-year
period. DOE quantified the energy savings attributable to each TSL as
the difference in energy consumption between each standards case and
the base case. Table V.18 presents the estimated primary energy savings
for each considered TSL, and Table V.19 presents the estimated FFC
energy savings for each considered TSL. The energy savings in the
tables below are net savings that reflect the subtraction of the
additional gas or oil used by the furnace associated with higher-
efficiency furnace fans. The approach for estimating national energy
savings is further described in section IV.H.1.
The difference between primary energy savings and FFC energy
savings for all TSLs is small (less than 1 percent), because the
upstream energy savings associated with the electricity savings are
partially or fully offset by the upstream energy use from the
additional gas or oil used by the furnace due to higher-efficiency
furnace fans.
Table V.18--Cumulative National Primary Energy Savings for Trial Standard Levels for Residential Furnace Fans
Sold in 2019-2048
----------------------------------------------------------------------------------------------------------------
Trial standard level
Product class -----------------------------------------------------------------------------
1 2 3 4 5 6
----------------------------------------------------------------------------------------------------------------
quads
-----------------------------------------------------------------------------
Non-Weatherized, Non-Condensing 0.296 1.341 1.341 1.796 1.796 2.426
Gas Furnace Fan..................
Non-Weatherized, Condensing Gas 0.278 1.188 1.188 1.614 1.614 2.324
Furnace Fan......................
Weatherized Non-Condensing Gas 0.048 0.224 0.224 0.330 0.330 0.462
Furnace Fan......................
Non-Weatherized, Non-Condensing 0.006 0.006 0.022 0.006 0.022 0.046
Oil Furnace Fan..................
Non-Weatherized Electric Furnace/ 0.032 0.143 0.143 0.193 0.193 0.264
Modular Blower Fan...............
Mobile Home Non-Weatherized, Non- 0.009 0.009 0.023 0.009 0.023 0.053
Condensing Gas Furnace Fan.......
[[Page 38192]]
Mobile Home Non-Weatherized, 0.001 0.001 0.003 0.001 0.003 0.008
Condensing Gas Furnace Fan.......
Mobile Home Electric Furnace/ 0.009 0.009 0.030 0.044 0.044 0.055
Modular Blower Fan...............
-----------------------------------------------------------------------------
Total--All Classes............ 0.679 2.922 2.974 3.994 4.024 5.639
----------------------------------------------------------------------------------------------------------------
Note: Components may not sum to total due to rounding.
Table V.19--Cumulative National Full-Fuel-Cycle Energy Savings for Trial Standard Levels for Residential Furnace
Fans Sold in 2019-2048
----------------------------------------------------------------------------------------------------------------
Trial standard level
Product class -----------------------------------------------------------------------------
1 2 3 4 5 6
----------------------------------------------------------------------------------------------------------------
quads
-----------------------------------------------------------------------------
Non-Weatherized, Non-Condensing 0.297 1.338 1.338 1.793 1.793 2.428
Gas Furnace Fan..................
Non-Weatherized, Condensing Gas 0.278 1.176 1.176 1.604 1.604 2.314
Furnace Fan......................
Weatherized Non-Condensing Gas 0.048 0.225 0.225 0.331 0.331 0.463
Furnace Fan......................
Non-Weatherized, Non-Condensing 0.006 0.006 0.020 0.006 0.020 0.044
Oil Furnace Fan..................
Non-Weatherized Electric Furnace/ 0.032 0.145 0.145 0.196 0.196 0.268
Modular Blower Fan...............
Mobile Home Non-Weatherized, Non- 0.009 0.009 0.022 0.009 0.022 0.052
Condensing Gas Furnace Fan.......
Mobile Home Non-Weatherized, 0.001 0.001 0.003 0.001 0.003 0.008
Condensing Gas Furnace Fan.......
Mobile Home Electric Furnace/ 0.010 0.010 0.030 0.045 0.045 0.056
Modular Blower Fan...............
Total--All Classes............ 0.680 2.909 2.958 3.986 4.014 5.635
----------------------------------------------------------------------------------------------------------------
Note: Components may not sum to total due to rounding.
OMB Circular A-4 \72\ requires agencies to present analytical
results, including separate schedules of the monetized benefits and
costs that show the type and timing of benefits and costs. Circular A-4
also directs agencies to consider the variability of key elements
underlying the estimates of benefits and costs. For this rulemaking,
DOE undertook a sensitivity analysis using nine, rather than 30, years
of product shipments. The choice of a nin-year period is a proxy for
the timeline in EPCA for the review of certain energy conservation
standards and potential revision of and compliance with such revised
standards.\73\ The review timeframe established in EPCA is generally
not synchronized with the product lifetime, product manufacturing
cycles, or other factors specific to residential furnace fans. Thus,
such results are presented for informational purposes only and are not
indicative of any change in DOE's analytical methodology. The NES
results based on a 9-year analytical period are presented in Table
V.20. The impacts are counted over the lifetime of products purchased
in 2019-2027.
---------------------------------------------------------------------------
\72\ U.S. Office of Management and Budget, ``Circular A-4:
Regulatory Analysis'' (Sept. 17, 2003) (Last accessed September 17,
2013 from https://www.whitehouse.gov/omb/circulars_a004_a-4/.)
\73\ Section 325(m) of EPCA requires DOE to review its standards
at least once every 6 years, and requires, for certain products, a
3-year period after any new standard is promulgated before
compliance is required, except that in no case may any new standards
be required within 6 years of the compliance date of the previous
standards. While adding a 6-year review to the 3-year compliance
period adds up to 9 years, DOE notes that it may undertake reviews
at any time within the 6-year period and that the 3-year compliance
date may yield to the 6-year backstop. A 9-year analysis period may
not be appropriate given the variability that occurs in the timing
of standards reviews and the fact that for some consumer products,
the compliance period is 5 years rather than 3 years.
Table V.20--Cumulative National Primary Energy Savings for Trial Standard Levels for Residential Furnace Fans
Sold in 2019-2027
----------------------------------------------------------------------------------------------------------------
Trial standard level
Product class -----------------------------------------------------------------------------
1 2 3 4 5 6
----------------------------------------------------------------------------------------------------------------
quads
-----------------------------------------------------------------------------
Non-Weatherized, Non-Condensing 0.099 0.454 0.454 0.611 0.611 0.838
Gas Furnace Fan..................
Non-Weatherized, Condensing Gas 0.075 0.316 0.316 0.429 0.429 0.612
Furnace Fan......................
Weatherized Non-Condensing Gas 0.016 0.075 0.075 0.108 0.108 0.150
Furnace Fan......................
Non-Weatherized, Non-Condensing 0.002 0.002 0.009 0.002 0.009 0.020
Oil Furnace Fan..................
Non-Weatherized Electric Furnace/ 0.009 0.043 0.043 0.058 0.058 0.080
Modular Blower Fan...............
[[Page 38193]]
Mobile Home Non-Weatherized, Non- 0.003 0.003 0.007 0.003 0.007 0.018
Condensing Gas Furnace Fan.......
Mobile Home Non-Weatherized, 0.000 0.000 0.001 0.000 0.001 0.002
Condensing Gas Furnace Fan.......
Mobile Home Electric Furnace/ 0.003 0.003 0.009 0.013 0.013 0.017
Modular Blower Fan...............
-----------------------------------------------------------------------------
Total--All Classes............ 0.207 0.897 0.914 1.225 1.236 1.737
----------------------------------------------------------------------------------------------------------------
Note: Components may not sum to total due to rounding.
Net Present Value of Consumer Costs and Benefits
DOE estimated the cumulative NPV of the total costs and savings for
consumers that would result from the TSLs considered for residential
furnace fans. In accordance with OMB's guidelines on regulatory
analysis,\74\ DOE calculated NPV using both a 7-percent and a 3-percent
real discount rate. Table V.21 shows the consumer NPV results for each
TSL considered for residential furnace fans. In each case, the impacts
cover the lifetime of products purchased in 2019-2048.
---------------------------------------------------------------------------
\74\ OMB Circular A-4, section E (Sept. 17, 2003) (Available at:
https://www.whitehouse.gov/omb/circulars_a004_a-4).
Table V.21--Cumulative Net Present Value of Consumer Benefit for Trial Standard Levels for Residential Furnace Fans Sold in 2019-2048
--------------------------------------------------------------------------------------------------------------------------------------------------------
Trial standard level
Product class Discount ------------------------------------------------------------------------------
rate % 1 2 3 4 5 6
--------------------------------------------------------------------------------------------------------------------------------------------------------
billion 2013$ *
------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan............. 3 2.150 12.031 12.031 13.309 13.309 11.943
Non-Weatherized, Condensing Gas Furnace Fan................. 1.842 10.769 10.769 11.444 11.444 10.156
Weatherized Non-Condensing Gas Furnace Fan.................. 0.335 1.849 1.849 2.288 2.288 2.082
Non-Weatherized, Non-Condensing Oil Furnace Fan............. 0.028 0.028 0.154 0.028 0.154 0.078
Non-Weatherized Electric Furnace/Modular Blower Fan......... 0.215 1.237 1.237 1.480 1.480 0.615
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan. 0.045 0.045 0.171 0.045 0.171 (0.039)
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan..... 0.007 0.007 0.025 0.007 0.025 (0.005)
Mobile Home Electric Furnace/Modular Blower Fan............. 0.047 0.047 0.168 0.209 0.209 (0.099)
------------------------------------------------------------------------------
Total--All Classes...................................... 4.668 26.013 26.403 28.810 29.079 24.731
--------------------------------------------------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan............. 7 0.823 4.502 4.502 4.713 4.713 3.381
Non-Weatherized, Condensing Gas Furnace Fan................. 0.677 3.856 3.856 3.876 3.876 2.686
Weatherized Non-Condensing Gas Furnace Fan.................. 0.129 0.702 0.702 0.825 0.825 0.604
Non-Weatherized, Non-Condensing Oil Furnace Fan............. 0.012 0.012 0.061 0.012 0.061 0.006
Non-Weatherized Electric Furnace/Modular Blower Fan......... 0.078 0.438 0.438 0.515 0.515 0.014
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan. 0.017 0.017 0.058 0.017 0.058 (0.071)
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan..... 0.003 0.003 0.008 0.003 0.008 (0.010)
Mobile Home Electric Furnace/Modular Blower Fan............. 0.017 0.017 0.054 0.065 0.065 (0.102)
------------------------------------------------------------------------------
[[Page 38194]]
Total--All Classes...................................... 1.754 9.545 9.679 10.024 10.120 6.509
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Numbers in parentheses indicate negative NPV.
The NPV results based on the aforementioned 9-year analytical
period are presented in Table V.22. The impacts are counted over the
lifetime of products purchased in 2019-2027. As mentioned previously,
this information is presented for informational purposes only and is
not indicative of any change in DOE's analytical methodology or
decision criteria.
Table V.22--Cumulative Net Present Value of Consumer Benefit for Trial Standard Levels for Residential Furnace Fans Sold in 2019-2027
--------------------------------------------------------------------------------------------------------------------------------------------------------
Trial standard level
Product class Discount ------------------------------------------------------------------------------
rate % 1 2 3 4 5 6
--------------------------------------------------------------------------------------------------------------------------------------------------------
billion 2013$ *
------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan............. 3 0.893 5.028 5.028 5.527 5.527 4.908
Non-Weatherized, Condensing Gas Furnace Fan................. 0.652 3.784 3.784 4.005 4.005 3.550
Weatherized Non-Condensing Gas Furnace Fan.................. 0.139 0.777 0.777 0.945 0.945 0.864
Non-Weatherized, Non-Condensing Oil Furnace Fan............. 0.015 0.015 0.082 0.015 0.082 0.064
Non-Weatherized Electric Furnace/Modular Blower Fan......... 0.080 0.463 0.463 0.549 0.549 0.217
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan. 0.019 0.019 0.073 0.019 0.073 (0.012)
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan..... 0.003 0.003 0.010 0.003 0.010 (0.001)
Mobile Home Electric Furnace/Modular Blower Fan............. 0.017 0.017 0.061 0.074 0.074 (0.052)
------------------------------------------------------------------------------
Total--All Classes...................................... 1.819 10.106 10.278 11.137 11.266 9.537
--------------------------------------------------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace Fan............. 7 0.444 2.433 2.433 2.531 2.531 1.799
Non-Weatherized, Condensing Gas Furnace Fan................. 0.325 1.840 1.840 1.845 1.845 1.290
Weatherized Non-Condensing Gas Furnace Fan.................. 0.070 0.384 0.384 0.446 0.446 0.333
Non-Weatherized, Non-Condensing Oil Furnace Fan............. 0.008 0.008 0.040 0.008 0.040 0.015
Non-Weatherized Electric Furnace/Modular Blower Fan......... 0.039 0.220 0.220 0.257 0.257 0.001
Mobile Home Non-Weatherized, Non-Condensing Gas Furnace Fan. 0.009 0.009 0.033 0.009 0.033 (0.037)
Mobile Home Non-Weatherized, Condensing Gas Furnace Fan..... 0.001 0.001 0.004 0.001 0.004 (0.005)
Mobile Home Electric Furnace/Modular Blower Fan............. 0.008 0.008 0.026 0.031 0.031 (0.059)
------------------------------------------------------------------------------
Total--All Classes...................................... 0.905 4.904 4.980 5.128 5.186 3.338
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Numbers in parentheses indicate negative NPV.
As noted in section IV.H.2, DOE assumed no change in residential
furnace fan prices over the 2019-2048 period. In addition, DOE
conducted a sensitivity analysis using alternative price trends: One in
which prices decline over time, and one in which prices increase over
time. These price trends, and the NPV results from the associated
sensitivity cases, are described in appendix 10-C of the final rule
TSD.
Indirect Impacts on Employment
DOE expects energy conservation standards for residential furnace
fans to reduce energy costs for consumers, with the resulting net
savings being redirected to other forms of economic
[[Page 38195]]
activity. Those shifts in spending and economic activity could affect
the demand for labor. As described in section IV.N, DOE used an input/
output model of the U.S. economy to estimate indirect employment
impacts of the TSLs that DOE considered in this rulemaking. DOE
understands that there are uncertainties involved in projecting
employment impacts, especially changes in the later years of the
analysis. Therefore, DOE generated results for near-term time frames
(2019 and 2024), where these uncertainties are reduced.
The results suggest that today's standards would be likely to have
negligible impact on the net demand for labor in the economy. The net
change in jobs is so small that it would be imperceptible in national
labor statistics and might be offset by other, unanticipated effects on
employment. Chapter 16 of the final rule TSD presents more detailed
results about anticipated indirect employment impacts.
4. Impact on Product Utility or Performance
DOE has concluded that the standards it is adopting in this final
rule would not lessen the utility or performance of residential furnace
fans.
5. Impact of Any Lessening of Competition
EPCA directs DOE to consider any lessening of competition that is
likely to result from standards. It also directs the Attorney General
of the United States (Attorney General) to determine the impact, if
any, of any lessening of competition likely to result from a proposed
standard and to transmit such determination in writing to the Secretary
within 60 days of the publication of a proposed rule, together with an
analysis of the nature and extent of the impact. (42 U.S.C.
6295(o)(2)(B)(i)(V) and (ii))
To assist the Attorney General in making such a determination for
today's standards, DOE provided the Department of Justice (DOJ) with
copies of the NOPR and the TSD for review. In its assessment letter
responding to DOE, DOJ concluded that the proposed energy conservation
standards for residential furnace fans are unlikely to have a
significant adverse impact on competition. DOE is publishing the
Attorney General's assessment at the end of this final rule.
6. Need of the Nation To Conserve Energy
An improvement in the energy efficiency of the products subject to
this rule is likely to improve the security of the nation's energy
system by reducing overall demand for energy. Reduction in the growth
of electricity demand resulting from energy conservation standards may
also improve the reliability of the electricity system. Reductions in
national electric generating capacity estimated for each considered TSL
are reported in chapter 15 of the final rule TSD.
Energy savings from standards for the residential furnace fan
products covered in today's final rule could also produce environmental
benefits in the form of reduced emissions of air pollutants and
greenhouse gases associated with electricity production. Table V.23
provides DOE's estimate of cumulative emissions reductions projected to
result from the TSLs considered in this rulemaking. The table includes
both power sector emissions and upstream emissions. The emissions were
calculated using the multipliers discussed in section IV.K. DOE reports
annual emissions reductions for each TSL in chapter 13 of the final
rule TSD.
As discussed in section IV.K, DOE did not include NOX
emissions reduction from power plants in States subject to CAIR,
because an energy conservation standard would not affect the overall
level of NOX emissions in those States due to the emissions
caps mandated by CAIR. For SO2, under the MATS, projected
emissions will be far below the cap established by CAIR, so it is
unlikely that excess SO2 emissions allowances resulting from
lower electricity demand would be needed or used to permit offsetting
increases in SO2 emissions by any regulated EGU. Therefore,
DOE believes that efficiency standards will reduce SO2
emissions.
Table V.23--Cumulative Emissions Reduction for Potential Standards for Residential Furnace Fans
----------------------------------------------------------------------------------------------------------------
TSL
-----------------------------------------------------------------------------------
1 2 3 4 5 6
----------------------------------------------------------------------------------------------------------------
Primary Energy Emissions *
----------------------------------------------------------------------------------------------------------------
CO2 (million metric tons)... 29.3 124.5 126.3 171.1 172.0 241.5
SO2 (thousand tons)......... 38.1 174.3 178.0 232.5 235.2 323.5
NOX (thousand tons)......... (5.2) (32.4) (33.8) (38.7) (40.2) (51.1)
Hg (tons)................... 0.1 0.3 0.3 0.4 0.4 0.5
N2O (thousand tons)......... 1.0 4.5 4.6 6.0 6.1 8.4
CH4 (thousand tons)......... 5.2 23.4 23.9 31.3 31.6 43.7
----------------------------------------------------------------------------------------------------------------
Upstream Emissions
----------------------------------------------------------------------------------------------------------------
CO2 (million metric tons)... 1.7 6.7 6.7 9.6 9.5 13.7
SO2 (thousand tons)......... 0.5 2.4 2.4 3.2 3.2 4.4
NOX (thousand tons)......... 22.5 84.9 85.0 122.8 122.0 177.5
Hg (tons)................... 0.0 0.0 0.0 0.0 0.0 0.0
N2O (thousand tons)......... 0.0 0.1 0.1 0.1 0.1 0.2
CH4 (thousand tons)......... 127.0 447.7 455.4 663.7 666.1 984.3
----------------------------------------------------------------------------------------------------------------
Total FFC Emissions
----------------------------------------------------------------------------------------------------------------
CO2 (million metric tons)... 31.0 131.2 133.1 180.6 181.5 255.2
SO2 (thousand tons)......... 38.6 176.7 180.4 235.7 238.4 327.9
NOX (thousand tons)......... 17.2 52.6 51.2 84.0 81.8 126.4
Hg (tons)................... 0.1 0.3 0.3 0.4 0.4 0.5
N2O (thousand tons)......... 1.0 4.6 4.7 6.2 6.2 8.6
N2O thousand tons CO2eq **.. 302.2 1378.9 1402.4 1843.7 1859.3 2569.2
CH4 (thousand tons)......... 132.1 471.1 479.3 695.0 697.7 1028.0
[[Page 38196]]
CH4 million tons CO2eq **... 3303.3 11778 11982 17375 17442 25700
----------------------------------------------------------------------------------------------------------------
* Includes emissions from additional gas use associated with more-efficient furnace fans.
** CO2eq is the quantity of CO2 that would have the same global warming potential (GWP).
Note: Parentheses indicate negative values.
As part of the analysis for this final rule, DOE estimated monetary
benefits likely to result from the reduced emissions of CO2
and NOX estimated for each of the TSLs considered for
residential furnace fans. As discussed in section IV.L, for
CO2, DOE used four sets of values for the SCC developed by
an interagency process. Three sets of values are based on the average
SCC from three integrated assessment models, at discount rates of 2.5
percent, 3 percent, and 5 percent. The fourth set represents the 95th-
percentile SCC estimate across all three models at a 3-percent discount
rate. The SCC values for CO2 emissions reductions in 2015,
expressed in 2013$, are $12.0/ton, $40.5/ton, $62.4/ton, and $119/ton.
The values for later years are higher due to increasing damages as the
magnitude of projected climate change increases. Table V.24 presents
the global value of CO2 emissions reductions at each TSL.
DOE calculated domestic values as a range from 7 percent to 23 percent
of the global values, and these results are presented in chapter 14 of
the final rule TSD.
Table V.24--Global Present Value of CO2 Emissions Reduction for Potential Standards for Residential Furnace Fans
----------------------------------------------------------------------------------------------------------------
SCC Case *
---------------------------------------------------------------
TSL 3% discount
5% discount 3% discount 2.5% discount rate, 95th
rate, average rate, average rate, average percentile
----------------------------------------------------------------------------------------------------------------
million 2013$
----------------------------------------------------------------------------------------------------------------
Primary Energy Emissions **
----------------------------------------------------------------------------------------------------------------
1............................................... 184 880 1,409 2,722
2............................................... 785 3,755 6,007 11,612
3............................................... 797 3,811 6,096 11,784
4............................................... 1,077 5,152 8,245 15,934
5............................................... 1,083 5,181 8,291 16,023
6............................................... 1,517 7,265 11,628 22,467
----------------------------------------------------------------------------------------------------------------
Upstream Emissions
----------------------------------------------------------------------------------------------------------------
1............................................... 10.2 50.1 81 155
2............................................... 40.0 196 315 607
3............................................... 40.0 196 316 608
4............................................... 57.0 279 449 866
5............................................... 56.6 278 447 861
6............................................... 81.7 401 644 1,241
----------------------------------------------------------------------------------------------------------------
Total FFC Emissions
----------------------------------------------------------------------------------------------------------------
1............................................... 194 930 1,489 2,878
2............................................... 825 3,951 6,323 12,219
3............................................... 837 4,007 6,412 12,392
4............................................... 1,134 5,432 8,694 16,799
5............................................... 1,140 5,459 8,737 16,884
6............................................... 1,599 7,666 12,272 23,709
----------------------------------------------------------------------------------------------------------------
* For each of the four cases, the corresponding SCC value for emissions in 2015 is $12.0, $40.5, $62.4, and $119
per metric ton (2013$). The values are for CO2 only (i.e., not CO2eq of other greenhouse gases).
** Includes site emissions from additional use of natural gas associated with more-efficient furnace fans.
DOE is well aware that scientific and economic knowledge about the
contribution of CO2 and other greenhouse gas (GHG) emissions
to changes in the future global climate and the potential resulting
damages to the world economy continues to evolve rapidly. Thus, any
value placed in this rulemaking on reducing CO2 emissions is
subject to change. DOE, together with other Federal agencies, will
continue to review various methodologies for estimating the monetary
value of reductions in CO2 and other GHG emissions. This
ongoing review will consider the comments on this subject that are part
of the public record for this and other rulemakings, as well as other
methodological assumptions and issues. However, consistent with DOE's
legal obligations, and taking into account the
[[Page 38197]]
uncertainty involved with this particular issue, DOE has included in
this final rule the most recent values and analyses resulting from the
interagency review process.
DOE also estimated a range for the cumulative monetary value of the
economic benefits associated with NOX emissions reductions
anticipated to result from standards for the residential furnace fan
products that are the subject of this final rule. The dollar-per-ton
values that DOE used are discussed in section IV.L. Table V.25 presents
the present value of cumulative NOX emissions reductions for
each TSL calculated using the average dollar-per-ton values and 7-
percent and 3-percent discount rates.
Table V.25--Present Value of NOX Emissions Reduction for Potential
Standards for Residential Furnace Fans
------------------------------------------------------------------------
TSL 3% Discount rate 7% Discount rate
------------------------------------------------------------------------
million 2013$
------------------------------------------------------------------------
Power Sector and Site Emissions *
------------------------------------------------------------------------
1............................... (3.8) 0.0
2............................... (27.1) (3.7)
3............................... (28.6) (4.1)
4............................... (31.0) (2.8)
5............................... (32.5) (3.3)
6............................... (39.4) (2.1)
------------------------------------------------------------------------
Upstream Emissions
------------------------------------------------------------------------
1............................... 25.9 10.2
2............................... 98.1 38.7
3............................... 98.3 38.8
4............................... 141.8 55.9
5............................... 140.9 55.6
6............................... 205.5 81.4
------------------------------------------------------------------------
Total FFC Emissions **
------------------------------------------------------------------------
1............................... 22.1 10.2
2............................... 71.0 35.1
3............................... 69.7 34.7
4............................... 110.8 53.1
5............................... 108.4 52.3
6............................... 166.1 79.3
------------------------------------------------------------------------
* Includes site emissions from additional use of natural gas associated
with more-efficient furnace fans.
** Components may not sum to total due to rounding.
Note: Parentheses indicate negative values.
The NPV of the monetized benefits associated with emissions
reductions can be viewed as a complement to the NPV of the consumer
savings calculated for each TSL considered in this rulemaking. Table
V.26 presents the NPV values that result from adding the estimates of
the potential economic benefits resulting from reduced full-fuel-cycle
CO2 and NOX emissions in each of four valuation
scenarios to the NPV of consumer savings calculated for each TSL
considered in this rulemaking, at both a 7-percent and a 3-percent
discount rate. The CO2 values used in the columns of each
table correspond to the four scenarios for the valuation of
CO2 emission reductions discussed above.
Table V.26--Potential Standards for Residential Furnace Fans: Net Present Value of Consumer Savings Combined
With Present Value of Monetized Benefits From CO2 and NOX Emissions Reductions
----------------------------------------------------------------------------------------------------------------
Consumer NPV at 3% Discount Rate added with:
---------------------------------------------------------------------------
SCC Case $12.0/ SCC Case $40.5/ SCC Case $62.4/ SCC Case $119/
TSL metric ton CO2* metric ton CO2* metric ton CO2* metric ton CO2*
and low value for and medium value and medium value and high value
NOX** for NOX** for NOX** for NOX**
----------------------------------------------------------------------------------------------------------------
billion 2013$
----------------------------------------------------------------------------------------------------------------
1................................... 4.9 5.6 6.2 7.6
2................................... 26.9 30.0 32.4 38.3
3................................... 27.3 30.5 32.9 38.9
4................................... 30.1 34.4 37.6 45.7
5................................... 30.3 34.6 37.9 46.1
6................................... 26.5 32.6 37.2 48.6
----------------------------------------------------------------------------------------------------------------
[[Page 38198]]
Consumer NPV at 7% Discount Rate added with:
---------------------------------------------------------------------------
SCC Case $12.0/ SCC Case $40.5/ SCC Case $62.4/ SCC Case $119/
TSL metric ton CO2* metric ton CO2* metric ton CO2* metric ton CO2*
and low value for and medium value and medium value and high value
NOX** for NOX** for NOX** for NOX**
----------------------------------------------------------------------------------------------------------------
billion 2013$
----------------------------------------------------------------------------------------------------------------
1................................... 2.0 2.7 3.3 4.6
2................................... 10.4 13.5 15.9 21.8
3................................... 10.6 13.7 16.1 22.1
4................................... 11.2 15.5 18.8 26.9
5................................... 11.3 15.6 18.9 27.1
6................................... 8.2 14.3 18.9 30.3
----------------------------------------------------------------------------------------------------------------
* These label values represent the global SCC in 2015, in 2013$.
** Low Value corresponds to $476 per ton of NOX emissions. Medium Value corresponds to $2,684 per ton, and High
Value corresponds to $4,893 per ton.
Although adding the value of consumer savings to the values of
emission reductions provides a valuable perspective, two issues should
be considered. First, the national operating cost savings are domestic
U.S. consumer monetary savings that occur as a result of market
transactions, while the value of CO2 reductions is based on
a global value. Second, the assessments of operating cost savings and
the SCC are performed with different methods that use quite different
time frames for analysis. The national operating cost savings is
measured for the lifetime of products shipped in 2019-2048. The SCC
values, on the other hand, reflect the present value of future climate-
related impacts resulting from the emission of one metric ton of
CO2 in each year. Because of the long residence time of
CO2 in the atmosphere, these impacts continue well beyond
2100.
7. Other Factors
The Secretary of Energy, in determining whether a standard is
economically justified, may consider any other factors that the
Secretary deems to be relevant. (42 U.S.C. 6295(o)(2)(B)(i)(VI)) No
other factors were considered in this analysis.
C. Conclusions
When considering proposed standards, the new or amended energy
conservation standard that DOE adopts for any type (or class) of
covered product shall be designed to achieve the maximum improvement in
energy efficiency that the Secretary determines is technologically
feasible and economically justified. (42 U.S.C. 6295(o)(2)(A)) In
determining whether a standard is economically justified, the Secretary
must determine whether the benefits of the standard exceed its burdens
by, to the greatest extent practicable, considering the seven statutory
factors discussed previously. (42 U.S.C. 6295(o)(2)(B)(i)) The new or
amended standard must also result in significant conservation of
energy. (42 U.S.C. 6295(o)(3)(B))
For today's final rule, DOE considered the impacts of standards at
each TSL, beginning with the maximum technologically feasible level, to
determine whether that level was economically justified. Where the max-
tech level was not justified, DOE then considered the next most
efficient level and undertook the same evaluation until it reached the
highest efficiency level that is both technologically feasible and
economically justified and saves a significant amount of energy.
To aid the reader in understanding the benefits and/or burdens of
each TSL, tables in this section summarize the quantitative analytical
results for each TSL, based on the assumptions and methodology
discussed herein. The efficiency levels contained in each TSL are
described in section V.A. In addition to the quantitative results
presented in the tables, DOE also considers other burdens and benefits
that affect economic justification. These include the impacts on
identifiable subgroups of consumers who may be disproportionately
affected by a national standard, and impacts on employment. Section
V.B.1.b presents the estimated impacts of each TSL for these subgroups.
DOE discusses the impacts on direct employment in residential furnace
fan manufacturing in section V.B.2.b, and discusses the indirect
employment impacts in section V.B.3.c.
DOE also notes that the economics literature provides a wide-
ranging discussion of how consumers trade off upfront costs and energy
savings in the absence of government intervention. Much of this
literature attempts to explain why consumers appear to undervalue
energy efficiency improvements. There is evidence that consumers
undervalue future energy savings as a result of: (1) A lack of
information; (2) a lack of sufficient salience of the long-term or
aggregate benefits; (3) a lack of sufficient savings to warrant
delaying or altering purchases; (4) excessive focus on the short term,
in the form of inconsistent weighting of future energy cost savings
relative to available returns on other investments; (5) computational
or other difficulties associated with the evaluation of relevant
tradeoffs; and (6) a divergence in incentives (for example, renter
versus owner or builder versus purchaser). Other literature indicates
that with less than perfect foresight and a high degree of uncertainty
about the future, consumers may trade off at a higher than expected
rate between current consumption and uncertain future energy cost
savings. This undervaluation suggests that regulation that promotes
energy efficiency can produce significant net private gains (as well as
producing social gains by, for example, reducing pollution).
In DOE's current regulatory analysis, potential changes in the
benefits and costs of a regulation due to changes in consumer purchase
decisions are included in two ways. First, if consumers forego a
purchase of a product in the standards case, this decreases sales for
product manufacturers and the cost to manufacturers is included in the
MIA. Second, DOE accounts for energy savings attributable only to
products actually used by consumers in the standards case; if a
standard decreases the number of products purchased by consumers, this
decreases the potential energy savings from an energy conservation
standard. DOE provides estimates of changes in the volume of product
purchases in chapter 9 of the final rule TSD. DOE's current analysis
does not explicitly control for heterogeneity in consumer preferences,
preferences across subcategories of products or specific features, or
[[Page 38199]]
consumer price sensitivity variation according to household income.\75\
---------------------------------------------------------------------------
\75\ P.C. Reiss and M.W. White, Household Electricity Demand,
Revisited, Review of Economic Studies (2005) 72, 853-883.
---------------------------------------------------------------------------
While DOE is not prepared at present to provide a fuller
quantifiable framework for estimating the benefits and costs of changes
in consumer purchase decisions due to an energy conservation standard,
DOE is committed to developing a framework that can support empirical
quantitative tools for improved assessment of the consumer welfare
impacts of appliance standards. DOE has posted a paper that discusses
the issue of consumer welfare impacts of appliance standards, and
potential enhancements to the methodology by which these impacts are
defined and estimated in the regulatory process.\76\ DOE welcomes
comments on how to more fully assess the potential impact of energy
conservation standards on consumer choice and how to quantify this
impact in its regulatory analysis.
---------------------------------------------------------------------------
\76\ Alan Sanstad, Notes on the Economics of Household Energy
Consumption and Technology Choice. Lawrence Berkeley National
Laboratory (2010) (Available at: https://www1.eere.energy.gov/buildings/appliance_standards/pdfs/consumer_ee_theory.pdf (Last
accessed May 3, 2013).
---------------------------------------------------------------------------
1. Benefits and Burdens of Trial Standard Levels Considered for
Residential Furnace Fans
Table V.27 through Table V.29 summarize the quantitative impacts
estimated for each TSL for residential furnace fans. The national
impacts are measured over the lifetime of furnace fans purchased in the
30-year period that begins in the first full year of compliance with
amended standards (2019-2048). The energy savings, emissions
reductions, and value of emissions reductions refer to full-fuel-cycle
results. Results that refer to primary energy savings are presented in
chapter 10 of the final rule TSD.
Table V.27--Summary of Analytical Results for Residential Furnace Fan Standards: National Impacts
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
Category TSL 1 TSL 2 TSL 3 TSL 4 TSL 5 TSL 6
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
National Full-Fuel-Cycle Energy Savings quads
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
0.680 2.909 2.958 3.986 4.014 5.635
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
NPV of Consumer Benefits 2013$ billion
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
3% discount rate................. 4.668 26.013 26.403 28.810 29.079 24.731
7% discount rate................. 1.754 9.545 9.679 10.024 10.120 6.509
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
Cumulative Emissions Reduction (FFC Emissions)
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
CO2 million metric tons.......... 31.0 131.2 133.1 180.6 181.5 255.2
SO2 thousand tons................ 38.6 176.7 180.4 235.7 238.4 327.9
NOX thousand tons................ 17.2 52.6 51.2 84.0 81.8 126.4
Hg tons.......................... 0.1 0.3 0.3 0.4 0.4 0.5
N2O thousand tons................ 1.0 4.6 4.7 6.2 6.2 8.6
N2O thousand tons CO2eq *........ 302.2 1378.9 1402.4 1843.7 1859.3 2569.2
CH4 thousand tons................ 132.1 471.1 479.3 695.0 697.7 1028.0
CH4 million tons CO2eq *......... 3303 11778 11982 17375 17442 25700
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
Value of Emissions Reduction (FFC Emissions) 2013$ billion
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
CO2 **........................... 0.194 to 2.878 0.825 to 12.219 0.837 to 12.392 1.134 to 16.799 1.140 to 16.884 1.599 to 23.709
NOX--3% discount rate............ 0.0221 0.0710 0.0697 0.1108 0.1084 0.1661
NOX--7% discount rate............ 0.0102 0.0351 0.0347 0.0531 0.0523 0.0793
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
* CO2eq is the quantity of CO2 that would have the same global warming potential (GWP).
** Range of the economic value of CO2 reductions is based on interagency estimates of the global benefit of reduced CO2 emissions.
Table V.28--Summary of Analytical Results for Residential Furnace Fan Standards: Manufacturer and Average or
Median Consumer Impacts
----------------------------------------------------------------------------------------------------------------
Category TSL 1 TSL 2 TSL 3 TSL 4 TSL 5 TSL 6
----------------------------------------------------------------------------------------------------------------
Manufacturer Impacts
----------------------------------------------------------------------------------------------------------------
Industry NPV (baseline value is 349.6) 332.3 to 313.2 to 311.0 to 290.6 to 288.8 to 147.2 to
(2013$ in millions).................... 336.6 360.0 359.1 397.8 397.6 422.4
Change in Industry NPV (% change)....... (5.0) to (10.4) to (11.0) to (16.9) to (17.4) to (57.9) to
(3.7) 3.0 2.7 13.8 13.7 20.8
----------------------------------------------------------------------------------------------------------------
Consumer Average LCC Savings (2013$)
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-condensing Gas $85 $471 $471 $506 $506 $431
Furnace Fan............................
Non-Weatherized, Condensing Gas Furnace $58 $335 $335 $341 $341 $268
Fan....................................
Weatherized Non-Condensing Gas Furnace $67 $378 $378 $447 $447 $391
Fan....................................
Non-Weatherized, Non-Condensing Oil $46 $46 $259 $46 $259 $80
Furnace Fan............................
Non-Weatherized Electric Furnace/Modular $29 $181 $181 $204 $204 $81
Blower Fan.............................
Mobile Home Non-Weatherized, Non- $36 $36 $144 $36 $144 ($58)
condensing Gas Furnace Fan.............
Mobile Home Non-Weatherized, Condensing $35 $35 $133 $35 $133 ($51)
Gas Furnace Fan........................
[[Page 38200]]
Mobile Home Electric Furnace/Modular $19 $19 $70 $85 $85 ($54)
Blower Fan.............................
----------------------------------------------------------------------------------------------------------------
Consumer Median PBP (years)
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-condensing Gas 1.12 2.60 2.60 5.41 5.41 10.16
Furnace Fan............................
Non-Weatherized, Condensing Gas Furnace 1.18 2.87 2.87 5.78 5.78 11.01
Fan....................................
Weatherized Non-Condensing Gas Furnace 0.73 1.79 1.79 4.42 4.42 8.19
Fan....................................
Non-Weatherized, Non-Condensing Oil 1.70 1.70 4.65 1.70 4.65 18.56
Furnace Fan............................
Non-Weatherized Electric Furnace/Modular 1.94 2.64 2.64 3.21 3.21 11.45
Blower Fan.............................
Mobile Home Non-Weatherized, Non- 2.72 2.72 6.84 2.72 6.84 24.38
condensing Gas Furnace Fan.............
Mobile Home Non-Weatherized, Condensing 2.31 2.31 6.65 2.31 6.65 31.27
Gas Furnace Fan........................
Mobile Home Electric Furnace/Modular 2.07 2.07 3.58 4.09 4.09 14.90
Blower Fan.............................
----------------------------------------------------------------------------------------------------------------
Note: Parentheses indicate negative values.
Table V.29--Summary of Analytical Results for Residential Furnace Fan Standards: Distribution of Consumer LCC
Impacts
----------------------------------------------------------------------------------------------------------------
Product Class TSL 1 TSL 2 TSL 3 TSL 4 TSL 5 TSL 6
----------------------------------------------------------------------------------------------------------------
Non-Weatherized, Non-Condensing Gas Furnace
Fan:
Net Cost.................................. 1% 17% 17% 30% 30% 50%
No Impact................................. 68% 25% 25% 14% 14% 0%
Net Benefit............................... 30% 58% 58% 56% 56% 50%
Non-Weatherized, Condensing Gas Furnace Fan:
Net Cost.................................. 1% 11% 11% 23% 23% 51%
No Impact................................. 75% 41% 41% 34% 34% 0%
Net Benefit............................... 24% 48% 48% 43% 43% 49%
Weatherized Non-Condensing Gas Furnace Fan:
Net Cost.................................. 0% 3% 3% 16% 16% 41%
No Impact................................. 81% 56% 56% 33% 33% 0%
Net Benefit............................... 19% 41% 41% 51% 51% 59%
Non-Weatherized, Non-Condensing Oil Furnace
Fan:
Net Cost.................................. 13% 13% 44% 13% 44% 78%
No Impact................................. 71% 71% 28% 71% 28% 0%
Net Benefit............................... 17% 17% 28% 17% 28% 22%
Non-Weatherized Electric Furnace/Modular
Blower Fan:
Net Cost.................................. 4% 17% 17% 23% 23% 60%
No Impact................................. 73% 37% 37% 25% 25% 0%
Net Benefit............................... 22% 45% 45% 51% 51% 39%
Mobile Home Non-Weatherized, Non-Condensing
Gas Furnace Fan:
Net Cost.................................. 10% 10% 55% 10% 55% 80%
No Impact................................. 56% 56% 0% 56% 0% 0%
Net Benefit............................... 34% 34% 45% 34% 45% 20%
Mobile Home Non-Weatherized, Condensing Gas
Furnace Fan:
Net Cost.................................. 5% 5% 37% 5% 37% 82%
No Impact................................. 68% 68% 29% 68% 29% 0%
Net Benefit............................... 27% 27% 33% 27% 33% 18%
Mobile Home Electric Furnace/Modular Blower
Fan:
Net Cost.................................. 7% 7% 26% 32% 32% 75%
No Impact................................. 71% 71% 38% 26% 26% 0%
Net Benefit............................... 22% 22% 37% 43% 43% 25%
----------------------------------------------------------------------------------------------------------------
Note: Components may not sum to total due to rounding.
First, DOE considered TSL 6, which would save an estimated total of
5.63 quads of energy, an amount DOE considers significant. TSL 6 has an
estimated NPV of consumer benefit of $6.51 billion using a 7-percent
discount rate, and $24.7 billion using a 3-percent discount rate.
The cumulative CO2 emissions reduction at TSL 6 is 255.2
million metric tons. The estimated monetary value of the CO2
emissions reductions ranges from $1.60 billion to $23.71 billion. The
other emissions reductions are 327.9 thousand tons of SO2,
126.4 thousand tons of NOX, 0.5 tons of Hg, 8.6 thousand
tons of N2O, and 1,028.0 thousand tons of CH4.
At TSL 6, the average LCC savings are positive for: (1) Non-
weatherized, non-condensing gas furnace fans; (2) non-weatherized,
condensing gas furnace fans; (3) weatherized non-condensing gas furnace
fans; (4) non-weatherized, non-condensing oil furnace fans; and (5)
non-weatherized electric furnace/modular blower fans. The LCC savings
are negative for: (1) Mobile home non-weatherized, non-condensing gas
furnace fans; (2) mobile home non-weatherized, condensing gas furnace
fans; and (3) mobile home electric furnace/modular blower fans. The
median payback period is lower than the median product lifetime (which
is 21.2 years for gas and electric furnace
[[Page 38201]]
fans) for all of the product classes except for: (1) Mobile home non-
weatherized, non-condensing gas furnace fans, and (2) mobile home non-
weatherized, condensing. The share of consumers experiencing an LCC
cost (increase in LCC) is higher than the share experiencing an LCC
benefit (decrease in LCC) for all of the product classes except for
weatherized non-condensing gas furnace fans.
At TSL 6, manufacturers may expect diminished profitability due to
increases in product costs, stranded assets, capital investments in
equipment and tooling, decreases in unit shipments, and expenditures
related to engineering and testing. The projected change in INPV ranges
from a decrease of $202.5 million to an increase of $72.8 million based
on DOE's manufacturer markup scenarios. The upper bound of $72.8
million is considered an optimistic scenario for manufacturers because
it assumes manufacturers can fully pass on substantial increases in
product costs and maintain existing mark ups. DOE recognizes the risk
of large negative impacts on industry if manufacturers' expectations
concerning reduced profit margins are realized. TSL 6 could reduce INPV
in the residential furnace fan industry by up to 57.9 percent if
impacts reach the lower bound of the range.
Accordingly, the Secretary concludes that at TSL 6 for residential
furnace fans, the benefits of significant energy savings, positive NPV
of consumer benefit, emission reductions and the estimated monetary
value of the CO2 emissions reductions, as well as positive
average LCC savings for most product classes would be outweighed by the
high percentage of consumers that would experience an LCC cost in all
of the product classes, and the substantial reduction in INPV for
manufacturers. Consequently, DOE has concluded that TSL 6 is not
economically justified.
Next, DOE considered TSL 5, which would save an estimated total of
4.01 quads of energy, an amount DOE considers significant. TSL 5 has an
estimated NPV of consumer benefit of $10.1 billion using a 7-percent
discount rate, and $29.1 billion using a 3-percent discount rate.
The cumulative CO2 emissions reduction at TSL 5 is 181.5
million metric tons. The estimated monetary value of the CO2
emissions reductions ranges from $1.14 billion to $16.88 billion. The
other emissions reductions are 238.4 thousand tons of SO2,
81.8 thousand tons of NOX, 0.4 tons of Hg, 6.2 thousand tons
of N2O, and 697.7 thousand tons of CH4.
At TSL 5, the average LCC savings are positive for all of the
product classes. The median payback period is lower than the average
product lifetime for all of the product classes. The share of consumers
experiencing an LCC benefit (decrease in LCC) is higher than the share
experiencing an LCC cost (increase in LCC) for five of the product
classes (non-weatherized, non-condensing gas furnace fans; non-
weatherized, condensing gas furnace fans; weatherized non-condensing
gas furnace fans; non-weatherized electric furnace/modular blower fans;
and mobile home electric furnace/modular blower fans), but lower for
the other three product classes.
At TSL 5, the projected change in INPV ranges from a decrease of
$60.8 million to an increase of $48.0 million. At TSL 5, DOE recognizes
the risk of negative impacts if manufacturers' expectations concerning
reduced profit margins are realized. If the lower bound of the range of
impacts is reached, as DOE expects, TSL 5 could result in a net loss of
17.4 percent in INPV for residential furnace fan manufacturers.
Accordingly, the Secretary concludes that at TSL 5 for residential
furnace fans, the benefits of significant energy savings, positive NPV
of consumer benefit, positive average LCC savings for all of the
product classes, emission reductions and the estimated monetary value
of the CO2 emissions reductions, would be outweighed by the
high percentage of consumers that would be negatively impacted for some
of the product classes, and the substantial reduction in INPV for
manufacturers. Consequently, DOE has concluded that TSL 5 is not
economically justified.
Next, DOE considered TSL 4, which would save an estimated total of
3.99 quads of energy, an amount DOE considers significant. TSL 4 has an
estimated NPV of consumer benefit of $10.0 billion using a 7-percent
discount rate, and $28.8 billion using a 3-percent discount rate.
The cumulative CO2 emissions reduction at TSL 4 is 180.6
million metric tons. The estimated monetary value of the CO2
emissions reductions ranges from $1.13 billion to $16.8 billion. The
other emissions reductions are 235.7 thousand tons of SO2,
84.0 thousand tons of NOX, 0.4 tons of Hg, 6.2 thousand tons
of N2O, and 695.0 thousand tons of CH4.
At TSL 4, the average LCC savings are positive for all of the
product classes. The median payback period is lower than the average
product lifetime for all of the product classes. The share of consumers
experiencing an LCC benefit (decrease in LCC) is higher than the share
experiencing an LCC cost (increase in LCC) for all of the product
classes.
At TSL 4, the projected change in INPV ranges from a decrease of
$59.0 million to an increase of $48.2 million. At TSL 4, DOE recognizes
the risk of negative impacts if manufacturers' expectations concerning
reduced profit margins are realized. If the lower bound of the range of
impacts is reached, as DOE expects, TSL 4 could result in a net loss of
16.9 percent in INPV for residential furnace fan manufacturers.
After considering the analysis and weighing the benefits and the
burdens, the Secretary concludes that at TSL 4 for residential furnace
fans, the benefits of significant energy savings, positive NPV of
consumer benefit, positive average LCC savings for all of the product
classes, emission reductions and the estimated monetary value of the
CO2 emissions reductions would outweigh the reduction in
INPV for manufacturers. The Secretary has concluded that TSL 4 would
save a significant amount of energy and is technologically feasible and
economically justified. Therefore, DOE today is adopting the energy
conservation standards for residential furnace fans at TSL 4. Table
V.30 presents the energy conservation standards for residential furnace
fans.
Table V.30--Energy Conservation Standards for Residential Furnace Fans
------------------------------------------------------------------------
Product class Standard: FER * (W/1000 cfm)
------------------------------------------------------------------------
Non-Weatherized, Non-Condensing FER = 0.044 x QMax + 182
Gas Furnace Fan.
Non-Weatherized, Condensing Gas FER = 0.044 x QMax + 195
Furnace Fan.
Weatherized Non-Condensing Gas FER = 0.044 x QMax + 199
Furnace Fan.
Non-Weatherized, Non-Condensing FER = 0.071 x QMax + 382
Oil Furnace Fan.
Non-Weatherized Electric FER = 0.044 x QMax + 165
Furnace/Modular Blower Fan.
Mobile Home Non-Weatherized, FER = 0.071 x QMax + 222
Non-Condensing Gas Furnace Fan.
Mobile Home Non-Weatherized, FER = 0.071 x QMax + 240
Condensing Gas Furnace Fan.
[[Page 38202]]
Mobile Home Electric Furnace/ FER = 0.044 x QMax + 101
Modular Blower Fan.
Mobile Home Weatherized Non- Reserved
Condensing Gas Furnace Fan.
Mobile Home Non-Weatherized Non- Reserved
Condensing Oil Furnace Fan.
------------------------------------------------------------------------
* QMax is the airflow, in cfm, at the maximum airflow-control setting
measured using the final DOE test procedure. 79 FR 500, 524 (Jan. 3,
2014).
2. Summary of Benefits and Costs (Annualized) of Today's Standards
The benefits and costs of today's standards can also be expressed
in terms of annualized values. The annualized monetary values are the
sum of: (1) The annualized national economic value, expressed in 2013$,
of the benefits from operating products that meet the standards
(consisting primarily of operating cost savings from using less energy,
minus increases in equipment purchase costs, which is another way of
representing consumer NPV), and (2) the monetary value of the benefits
of emission reductions, including CO2 emission
reductions.\77\ The value of the CO2 reductions, otherwise
known as the Social Cost of Carbon (SCC), is calculated using a range
of values per metric ton of CO2 developed by a recent
interagency process.
---------------------------------------------------------------------------
\77\ DOE used a two-step calculation process to convert the
time-series of costs and benefits into annualized values. First, DOE
calculated a present value in 2013, the year used for discounting
the NPV of total consumer costs and savings, for the time-series of
costs and benefits using discount rates of 3 and 7 percent for all
costs and benefits except for the value of CO2
reductions. For the latter, DOE used a range of discount rates. From
the present value, DOE then calculated the fixed annual payment over
a 30-year period, starting in 2013, that yields the same present
value. The fixed annual payment is the annualized value. Although
DOE calculated annualized values, this does not imply that the time-
series of cost and benefits from which the annualized values were
determined would be a steady stream of payments.
---------------------------------------------------------------------------
Although combining the values of operating savings and
CO2 reductions provides a useful perspective, two issues
should be considered. First, the national operating savings are
domestic U.S. consumer monetary savings that occur as a result of
market transactions while the value of CO2 reductions is
based on a global value. Second, the assessments of operating cost
savings and SCC are performed with different methods that use different
time frames for analysis. The national operating cost savings is
measured for the lifetime of products shipped in 2019-2048. The SCC
values, on the other hand, reflect the present value of future climate-
related impacts resulting from the emission of one metric ton of
CO2 in each year over a very long period.
Table V.31 shows the annualized values for today's standards for
residential furnace fans. The results under the primary estimate are as
follows. (All monetary values below are expressed in 2013$.) Using a 7-
percent discount rate for benefits and costs other than CO2
reduction (for which DOE used a 3-percent discount rate along with the
SCC series corresponding to a value of $40.5/ton in 2015), the cost of
the residential furnace fan standards in today's rule is $358 million
per year in increased equipment costs, while the benefits are $1,416
million per year in reduced equipment operating costs, $312 million in
CO2 reductions, and $5.61 million in reduced NOX
emissions. In this case, the net benefit amounts to $1,376 million per
year.
Using a 3-percent discount rate for all benefits and costs and the
SCC series corresponding to a value of $40.5/ton in 2015, Table V.31
shows the cost of the residential furnace fans standards in today's
rule is $355 million per year in increased equipment costs, while the
benefits are $2010 million per year in reduced operating costs, $312
million in CO2 reductions, and $6.36 million in reduced
NOX emissions. In this case, the net benefit amounts to
$1,973 million per year.
Table V.31--Annualized Benefits and Costs of Standards (TSL 4) for Residential Furnace Fans
----------------------------------------------------------------------------------------------------------------
Low net High net
Discount rate Primary benefits benefits
estimate * estimate estimate
----------------------------------------------------------------------------------------------------------------
million 2013$/year
----------------------------------------------------------------------------------------------------------------
Benefits:
Consumer Operating Cost Savings........... 7% 1416 1167 1718
3% 2010 1626 2467
CO[ihel2] Reduction Monetized Value ($12.0/ 5% 90 77 108
t case) **...............................
CO[ihel2] Reduction Monetized Value ($40.5/ 3% 312 268 377
t case) **...............................
CO2 Reduction Monetized Value ($62.4/t 2.5% 459 393 555
case) **.................................
CO2 Reduction Monetized Value ($119/t 3% 965 828 1166
case) **.................................
NOX Reduction Monetized Value (at $2,684/ 7% 5.61 4.80 6.82
ton) **.................................. 3% 6.36 5.35 7.86
-------------------------------------------------------------------
Total Benefits [dagger]................. 7% plus CO2 range 1,512 to 2,387 1,249 to 2,000 1,833 to 2,891
7% 1,734 1,439 2,102
3% plus CO2 range 2,106 to 2,981 1,708 to 2,459 2,583 to 3,641
3% 2,328 1,899 2,852
Costs:
Consumer Incremental Product Costs........ 7% 358 314 410
3% 355 304 419
Net Benefits:
-------------------------------------------------------------------
Total [dagger].......................... 7% plus CO2 range 1,154 to 2,029 935 to 1,685 1,423 to 2,481
7% 1,376 1,125 1,692
[[Page 38203]]
3% plus CO2 range 1,750 to 2,625 1,404 to 2,155 2,164 to 3,222
3% 1,973 1,595 2,433
----------------------------------------------------------------------------------------------------------------
* This table presents the annualized costs and benefits associated with residential furnace fans shipped in 2019-
2048. These results include benefits to consumers which accrue after 2048 from the products purchased in 2019-
2048. Costs incurred by manufacturers, some of which may be incurred in preparation for the rule, are not
directly included, but are indirectly included as part of incremental equipment costs. The Primary, Low
Benefits, and High Benefits Estimates utilize projections of energy prices and housing starts from the AEO
2013 Reference case, Low Estimate, and High Estimate, respectively. Incremental product costs reflect a
constant product price trend in the Primary Estimate, an increasing price trend in the Low Benefits Estimate,
and a decreasing price trend in the High Benefits Estimate.
** The CO2 values represent global values of the SCC, in 2013$, in 2015 under several scenarios. The first three
cases use the averages of SCC distributions calculated using 5%, 3%, and 2.5% discount rates, respectively.
The fourth case represents the 95th percentile of the SCC distribution calculated using a 3% discount rate.
The SCC values increase over time. The value for NOX (in 2013$) is the average of the low and high values used
in DOE's analysis.
[dagger] Total Benefits for both the 3% and 7% cases are derived using the series corresponding to the SCC value
of $40.5/t in 2015. In the rows labeled ``7% plus CO2 range'' and ``3% plus CO2 range,'' the operating cost
and NOX benefits are calculated using the labeled discount rate, and those values are added to the full range
of CO2 values.
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Orders 12866 and 13563
Section 1(b)(1) of Executive Order 12866, ``Regulatory Planning and
Review,'' 58 FR 51735 (Oct. 4, 1993), requires each agency to identify
the problem that it intends to address, including, where applicable,
the failures of private markets or public institutions that warrant new
agency action, as well as to assess the significance of that problem.
The problems that today's standards address, are as follows:
(1) There is a lack of consumer information and/or information
processing capability about energy efficiency opportunities in the
home appliance market.
(2) There is asymmetric information (one party to a transaction
has more and better information than the other) and/or high
transactions costs (costs of gathering information and effecting
exchanges of goods and services).
(3) There are external benefits resulting from improved energy
efficiency of residential furnace fans that are not captured by the
users of such equipment. These benefits include externalities
related to environmental protection and energy security that are not
reflected in energy prices, such as reduced emissions of greenhouse
gases.
In addition, DOE has determined that today's regulatory action is
an ``economically significant regulatory action'' under section 3(f) of
Executive Order 12866. Accordingly, section 6(a)(3) of the Executive
Order requires that DOE prepare a regulatory impact analysis (RIA) for
this rule and that the Office of Information and Regulatory Affairs
(OIRA) in the OMB review this rule. DOE presented to OIRA for review
the draft rule and other documents prepared for this rulemaking,
including the RIA, and has included these documents in the rulemaking
record. The assessments prepared pursuant to Executive Order 12866 can
be found in the technical support document for this rulemaking.
DOE has also reviewed this regulation pursuant to Executive Order
13563, issued on January 18, 2011. 76 FR 3281 (Jan. 21, 2011).
Executive Order 13563 is supplemental to and explicitly reaffirms the
principles, structures, and definitions governing regulatory review
established in Executive Order 12866. To the extent permitted by law,
agencies are required by Executive Order 13563 to: (1) Propose or adopt
a regulation only upon a reasoned determination that its benefits
justify its costs (recognizing that some benefits and costs are
difficult to quantify); (2) tailor regulations to impose the least
burden on society, consistent with obtaining regulatory objectives,
taking into account, among other things, and to the extent practicable,
the costs of cumulative regulations; (3) select, in choosing among
alternative regulatory approaches, those approaches that maximize net
benefits (including potential economic, environmental, public health
and safety, and other advantages; distributive impacts; and equity);
(4) to the extent feasible, specify performance objectives, rather than
specifying the behavior or manner of compliance that regulated entities
must adopt; and (5) identify and assess available alternatives to
direct regulation, including providing economic incentives to encourage
the desired behavior, such as user fees or marketable permits, or
providing information upon which choices can be made by the public.
DOE emphasizes as well that Executive Order 13563 requires agencies
to use the best available techniques to quantify anticipated present
and future benefits and costs as accurately as possible. In its
guidance, the Office of Information and Regulatory Affairs has
emphasized that such techniques may include identifying changing future
compliance costs that might result from technological innovation or
anticipated behavioral changes. For the reasons stated in the preamble,
DOE believes that today's final rule is consistent with these
principles, including the requirement that, to the extent permitted by
law, benefits justify costs and that net benefits are maximized.
B. Review Under the Regulatory Flexibility Act
The Regulatory Flexibility Act (5 U.S.C. 601 et seq.) requires
preparation of a final regulatory flexibility analysis (FRFA) for any
rule that by law must be proposed for public comment, unless the agency
certifies that the rule, if promulgated, will not have a significant
economic impact on a substantial number of small entities. As required
by Executive Order 13272, ``Proper Consideration of Small Entities in
Agency Rulemaking,'' 67 FR 53461 (August 16, 2002), DOE published
procedures and policies on February 19, 2003, to ensure that the
potential impacts of its rules on small entities are properly
considered during the rulemaking process. 68 FR 7990. DOE has made its
procedures and policies available on the Office of the General
Counsel's Web site (https://energy.gov/gc/office-general-counsel). DOE
has prepared the following FRFA for the products that are the subject
of this rulemaking.
[[Page 38204]]
1. Description and Estimated Number of Small Entities Regulated
Methodology for Estimating the Number of Small Entities
For the manufacturers of residential furnace fans, the Small
Business Administration (SBA) has set a size threshold, which defines
those entities classified as ``small businesses'' for the purposes of
the statute. DOE used the SBA's small business size standards to
determine whether any small entities would be subject to the
requirements of the rule. 65 FR 30836, 30848 (May 15, 2000), as amended
at 65 FR 53533, 53544 (Sept. 5, 2000) and codified at 13 CFR part 121.
The size standards are listed by NAICS code and industry description
and are available at: https://www.sba.gov/sites/default/files/files/Size_Standards_Table.pdf. Residential furnace fan manufacturing is
classified under NAICS 333415, ``Air-Conditioning and Warm Air Heating
Equipment and Commercial and Industrial Refrigeration Equipment
Manufacturing.'' The SBA sets a threshold of 750 employees or less for
an entity to be considered as a small business for this category.
To estimate the number of companies that could be small business
manufacturers of products covered by this rulemaking, DOE conducted a
market survey using available public information to identify potential
small manufacturers. DOE's research involved public databases (e.g.,
AHRI Directory,\78\ the SBA Database \79\), individual company Web
sites, and market research tools (e.g., Hoovers Web site \80\) to
create a list of companies that manufacture or sell products covered by
this rulemaking. DOE also asked stakeholders and industry
representatives if they were aware of any other small manufacturers
during manufacturer interviews and at DOE public meetings. DOE reviewed
publicly-available data and contacted select companies on its list, as
necessary, to determine whether they met the SBA's definition of a
small business manufacturer of covered residential furnace fans. DOE
screened out companies that do not offer products covered by this
rulemaking, do not meet the definition of a ``small business,'' or are
foreign owned and operated.
---------------------------------------------------------------------------
\78\ See https://www.ahridirectory.org/ahriDirectory/pages/home.aspx.
\79\ See https://dsbs.sba.gov/dsbs/search/dsp_dsbs.cfm.
\80\ See Hoovers: https://www.hoovers.com./.
---------------------------------------------------------------------------
DOE initially identified 38 manufacturers of residential furnace
fan products sold in the U.S. DOE then determined that 23 were large
manufacturers or manufacturers that are foreign owned and operated. DOE
was able to determine that 15 domestic manufacturers meet the SBA's
definition of a ``small business'' and manufacture products covered by
this rulemaking.
Manufacturer Participation
Before issuing this Notice, DOE attempted to contact all the small
business manufacturers of residential furnace fans it had identified.
One of the small businesses consented to being interviewed during the
MIA interviews. DOE also obtained information about small business
impacts while interviewing large manufacturers.
Industry Structure
The 15 identified domestic manufacturers of residential furnace
fans that qualify as small businesses under the SBA size standard
account for a small fraction of industry shipments. Generally,
manufacturers of furnaces are also manufacturers of furnace fan
products. The market for residential gas furnaces is almost completely
held by seven large manufacturers, and small manufacturers in total
account for only 1 percent of unit sales in the market. These seven
large manufacturers also control 97 percent of the market for central
air conditioners. The market for mobile home furnaces is primarily held
by one large manufacturer. In contrast, the market for domestic oil
furnaces is almost entirely comprised of small manufacturers.
Comparison Between Large and Small Entities
Today's standards for residential furnace fans could cause small
manufacturers to be at a disadvantage relative to large manufacturers.
One way in which small manufacturers could be at a disadvantage is that
they may be disproportionately affected by product conversion costs.
Product redesign, testing, and certification costs tend to be fixed per
basic model and do not scale with sales volume. For each model, small
businesses must make investments in research and development to
redesign their products, but because they have lower sales volumes,
they must spread these costs across fewer units. In addition, because
small manufacturers have fewer engineers than large manufacturers, they
would need to allocate a greater portion of their available resources
to meet a standard. Since engineers may need to spend more time
redesigning and testing existing models as a result of the new
standard, they may have less time to develop new products.
Furthermore, smaller manufacturers may lack the purchasing power of
larger manufacturers. For example, since motor suppliers give discounts
to manufacturers based on the number of motors they purchase, larger
manufacturers may have a pricing advantage because they have higher
volume purchases. This purchasing power differential between high-
volume and low-volume orders applies to other furnace fan components as
well, including the impeller fan blade, transformer, and capacitor.
2. Description and Estimate of Compliance Requirements
Since the standard in today's final rule for residential furnace
fans could cause small manufacturers to be at a disadvantage relative
to large manufacturers, DOE cannot certify that today's standards would
not have a significant impact on a significant number of small
businesses, and consequently, DOE has prepared this FRFA.
At TSL 4, the level adopted in today's document, DOE estimates
capital conversion costs of $0.14 million and product conversion costs
of $0.23 million over a five-year conversion period for a typical small
manufacturer. This is compared to capital conversion costs of $0.59 and
product conversion costs of $1.00 million over a five-year conversion
period for a typical large manufacturer. These costs and their impacts
are described in detail below.
To estimate how small manufacturers would be potentially impacted,
DOE used the market share of small manufacturers to estimate the annual
revenue, earnings before interest and tax (EBIT), and research and
development (R&D) expense for a typical small manufacturer. DOE then
compared these costs to the required product conversion costs at each
TSL for both an average small manufacturer and an average large
manufacturer. Table VI.1 and VI.2 show the capital and product
conversion costs for a typical small manufacturer versus those of a
typical large manufacturer. Tables VI.3 and VI.4 report the total
conversion costs as a percentage of annual R&D expense, annual revenue,
and EBIT for a typical small and large manufacturer, respectively. In
the following tables, TSL 4 represents the adopted standard.
[[Page 38205]]
Table VI.1--Comparison of Typical Small and Large Manufacturer's Capital
Conversion Costs
------------------------------------------------------------------------
Capital Capital
conversion conversion
costs for costs for
typical small typical large
manufacturer manufacturer
(in 2013$ (in 2013$
millions) millions)
------------------------------------------------------------------------
TSL 1................................... 0.08 0.35
TSL 2................................... 0.10 0.44
TSL 3................................... 0.11 0.46
TSL 4................................... 0.14 0.59
TSL 5................................... 0.14 0.62
TSL 6................................... 1.24 5.28
------------------------------------------------------------------------
Table VI.2:--Comparison of Typical Small and Large Manufacturer's
Product Conversion Costs
------------------------------------------------------------------------
Product Product
conversion conversion
costs for costs for
typical small typical large
manufacturer manufacturer
(in 2013$ (in 2013$
millions) millions)
------------------------------------------------------------------------
TSL 1................................... 0.17 0.74
TSL 2................................... 0.22 0.93
TSL 3................................... 0.23 0.99
TSL 4................................... 0.23 1.00
TSL 5................................... 0.25 1.06
TSL 6................................... 0.27 1.15
------------------------------------------------------------------------
Table VI.3--Impacts of Conversion Costs on a Small Manufacturer
----------------------------------------------------------------------------------------------------------------
Capital Product Total
conversion conversion conversion Total
cost as a cost as a cost as a conversion
percentage of percentage of percentage of cost as a
annual capital annual R&D annual percentage of
expenditures expense revenue annual EBIT
----------------------------------------------------------------------------------------------------------------
TSL 1........................................... 69% 185% 5% 72%
TSL 2........................................... 86% 232% 6% 90%
TSL 3........................................... 92% 249% 7% 96%
TSL 4........................................... 117% 250% 8% 105%
TSL 5........................................... 122% 266% 8% 111%
TSL 6........................................... 1048% 289% 31% 427%
----------------------------------------------------------------------------------------------------------------
Table VI.4--Impacts of Conversion Costs on a Large Manufacturer
----------------------------------------------------------------------------------------------------------------
Capital Product Total
conversion conversion conversion Total
cost as a cost as a cost as a conversion
percentage of percentage of percentage of cost as a
annual capital annual R&D annual percentage of
expenditures expense revenue annual EBIT
----------------------------------------------------------------------------------------------------------------
TSL 1........................................... 3% 8% 0% 3%
TSL 2........................................... 4% 10% 0% 4%
TSL 3........................................... 4% 11% 0% 4%
TSL 4........................................... 5% 11% 0% 5%
TSL 5........................................... 5% 11% 0% 5%
TSL 6........................................... 45% 12% 1% 18%
----------------------------------------------------------------------------------------------------------------
Based on the results in Table VI.1 and Table VI.2, DOE understands
that the potential conversions costs faced by small manufacturers may
be proportionally greater than those faced by larger manufacturers.
Small manufacturers have less engineering staff and lower R&D budgets.
They also have lower capital expenditures annually. As a result, the
conversion costs incurred by a small manufacturer would likely be a
larger percentage of its annual capital expenditures, R&D expenses,
revenue, and EBIT, than those for a large manufacturer.
[[Page 38206]]
3. Duplication, Overlap, and Conflict with Other Rules and Regulations
DOE is not aware of any rules or regulations that duplicate,
overlap, or conflict with the rule being adopted today.
4. Significant Alternatives to the Rule
The discussion above analyzes impacts on small businesses that
would result from the other TSLs DOE considered. Although TSLs lower
than the proposed TSLs would be expected to reduce the impacts on small
entities, DOE is required by EPCA to establish standards that achieve
the maximum improvement in energy efficiency that is technologically
feasible and economically justified, and result in a significant
conservation of energy. Thus, DOE rejected the lower TSLs.
In addition to the other TSLs being considered, the NOPR TSD
includes a regulatory impact analysis in chapter 17. For residential
furnace fans, this report discusses the following policy alternatives:
(1) No standard, (2) consumer rebates, (3) consumer tax credits, (4)
manufacturer tax credits, and (5) early replacement. DOE does not
intend to consider these alternatives further because they are either
not feasible to implement without authority and funding from Congress,
or are expected to result in energy savings that are much smaller
(ranging from less than 1 percent to less than 31 percent) than those
that would be achieved by the considered energy conservation standards.
C. Review Under the Paperwork Reduction Act
Manufacturers of furnace fans, or their third party
representatives, must certify to DOE that their products comply with
any applicable energy conservation standard. In certifying compliance,
manufacturers or their third-party representatives must test their
equipment according to the DOE test procedure for furnace fans,
including any amendments adopted for that test procedure. Manufacturers
or their third-party representatives must then submit certification
reports and compliance statements using DOE's electronic Web-based
tool, the Compliance and Certification Management System (CCMS),
regarding product characteristics and energy consumption information
regarding basic models of furnace fans distributed in commerce in the
U.S. CCMS uses product-specific templates that manufacturers are
required to use when submitting certification data to DOE. See https://www.regulations.doe.gov/ccms.
The collection-of-information requirement for furnace fan
certification is subject to review and approval by OMB under the
Paperwork Reduction Act (PRA). This requirement has been submitted to
OMB for approval. Public reporting burden for the certification is
estimated to average 30 hours per response, including the time for
reviewing instructions, searching existing data sources, gathering and
maintaining the data needed, and completing and reviewing the
collection of information. Note that the certification and
recordkeeping requirements for certain consumer products in 10 CFR part
430 have previously been approved by OMB and assigned OMB control
number 1910-1400; the certification requirement for furnace fans will
be included in this collection once approved by OMB. DOE will notify
the public of OMB approval through a Federal Register notice.
Public comment is sought regarding: whether this proposed
collection of information is necessary for the proper performance of
the functions of the agency, including whether the information shall
have practical utility; the accuracy of the burden estimate; ways to
enhance the quality, utility, and clarity of the information to be
collected; and ways to minimize the burden of the collection of
information, including through the use of automated collection
techniques or other forms of information technology. Send comments on
these or any other aspects of the collection of information to the DOE
program official listed in the ADDRESSES section above, and email to
Chad_S._Whiteman@omb.eop.gov.
Notwithstanding any other provision of the law, no person is
required to respond to, nor shall any person be subject to a penalty
for failure to comply with, a collection of information subject to the
requirements of the PRA, unless that collection of information displays
a currently valid OMB Control Number.
D. Review Under the National Environmental Policy Act of 1969
Pursuant to the National Environmental Policy Act (NEPA) of 1969,
DOE has determined that this rule fits within the category of actions
included in Categorical Exclusion (CX) B5.1 and otherwise meets the
requirements for application of a CX. See 10 CFR Part 1021, App. B,
B5.1(b); 1021.410(b) and Appendix B, B(1)-(5). The rule fits within the
category of actions because it is a rulemaking that establishes energy
conservation standards for consumer products or industrial equipment,
and for which none of the exceptions identified in CX B5.1(b) apply.
Therefore, DOE has made a CX determination for this rulemaking, and DOE
does not need to prepare an Environmental Assessment or Environmental
Impact Statement for this rule. DOE's CX determination for this rule is
available at https://cxnepa.energy.gov/.
E. Review Under Executive Order 13132
Executive Order 13132, ``Federalism.'' 64 FR 43255 (August 10,
1999) imposes certain requirements on Federal agencies formulating and
implementing policies or regulations that preempt State law or that
have Federalism implications. The Executive Order requires agencies to
examine the constitutional and statutory authority supporting any
action that would limit the policymaking discretion of the States and
to carefully assess the necessity for such actions. The Executive Order
also requires agencies to have an accountable process to ensure
meaningful and timely input by State and local officials in the
development of regulatory policies that have Federalism implications.
On March 14, 2000, DOE published a statement of policy describing the
intergovernmental consultation process it will follow in the
development of such regulations. 65 FR 13735. DOE has examined this
final rule and has determined that it would not have a substantial
direct effect on the States, on the relationship between the national
government and the States, or on the distribution of power and
responsibilities among the various levels of government. EPCA governs
and prescribes Federal preemption of State regulations as to energy
conservation for the products that are the subject of today's final
rule. States can petition DOE for exemption from such preemption to the
extent, and based on criteria, set forth in EPCA. (42 U.S.C. 6297) No
further action is required by Executive Order 13132.
F. Review Under Executive Order 12988
With respect to the review of existing regulations and the
promulgation of new regulations, section 3(a) of Executive Order 12988,
``Civil Justice Reform,'' imposes on Federal agencies the general duty
to adhere to the following requirements: (1) Eliminate drafting errors
and ambiguity; (2) write regulations to minimize litigation; (3)
provide a clear legal standard for affected conduct rather than a
general standard; and (4) promote simplification and burden reduction.
61 FR 4729 (Feb. 7, 1996). Regarding the review required by section
3(a), section 3(b) of Executive Order 12988 specifically requires that
[[Page 38207]]
Executive agencies make every reasonable effort to ensure that the
regulation: (1) Clearly specifies the preemptive effect, if any; (2)
clearly specifies any effect on existing Federal law or regulation; (3)
provides a clear legal standard for affected conduct while promoting
simplification and burden reduction; (4) specifies the retroactive
effect, if any; (5) adequately defines key terms; and (6) addresses
other important issues affecting clarity and general draftsmanship
under any guidelines issued by the Attorney General. Section 3(c) of
Executive Order 12988 requires Executive agencies to review regulations
in light of applicable standards in section 3(a) and section 3(b) to
determine whether they are met or it is unreasonable to meet one or
more of them. DOE has completed the required review and determined
that, to the extent permitted by law, this final rule meets the
relevant standards of Executive Order 12988.
G. Review Under the Unfunded Mandates Reform Act of 1995
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA)
requires each Federal agency to assess the effects of Federal
regulatory actions on State, local, and Tribal governments and the
private sector. Public Law 104-4, sec. 201 (codified at 2 U.S.C. 1531).
For a proposed regulatory action likely to result in a rule that may
cause the expenditure by State, local, and Tribal governments, in the
aggregate, or by the private sector of $100 million or more in any one
year (adjusted annually for inflation), section 202 of UMRA requires a
Federal agency to publish a written statement that estimates the
resulting costs, benefits, and other effects on the national economy.
(2 U.S.C. 1532(a), (b)) The UMRA also requires a Federal agency to
develop an effective process to permit timely input by elected officers
of State, local, and Tribal governments on a ``significant
intergovernmental mandate,'' and requires an agency plan for giving
notice and opportunity for timely input to potentially affected small
governments before establishing any requirements that might
significantly or uniquely affect them. On March 18, 1997, DOE published
a statement of policy on its process for intergovernmental consultation
under UMRA. 62 FR 12820. DOE's policy statement is also available at
https://energy.gov/sites/prod/files/gcprod/documents/umra_97.pdf.
Although today's final rule, which adopts new energy conservation
standards for residential furnace fans, does not contain a Federal
intergovernmental mandate, it may require annual expenditures of $100
million or more by the private sector. Specifically, the final rule
could require expenditures of $100 million or more, including: (1)
Investment in research and development and in capital expenditures by
residential furnace fans manufacturers in the years between the final
rule and the compliance date for the new standards, and (2) incremental
additional expenditures by consumers to purchase higher-efficiency
residential furnace fans, starting at the compliance date for the
applicable standard.
Section 202 of UMRA authorizes a Federal agency to respond to the
content requirements of UMRA in any other statement or analysis that
accompanies the final rule. 2 U.S.C. 1532(c). The content requirements
of section 202(b) of UMRA relevant to a private sector mandate
substantially overlap the economic analysis requirements that apply
under section 325(o) of EPCA and Executive Order 12866. The
SUPPLEMENTARY INFORMATION section of this final rule and the
``Regulatory Impact Analysis'' section of the TSD for this final rule
respond to those requirements.
Under section 205 of UMRA, the Department is obligated to identify
and consider a reasonable number of regulatory alternatives before
promulgating a rule for which a written statement under section 202 is
required. 2 U.S.C. 1535(a). DOE is required to select from those
alternatives the most cost-effective and least burdensome alternative
that achieves the objectives of the rule unless DOE publishes an
explanation for doing otherwise, or the selection of such an
alternative is inconsistent with law. As required by 42 U.S.C. 6295(f)
and (o), today's final rule establishes energy conservation standards
for residential furnace fans that are designed to achieve the maximum
improvement in energy efficiency that DOE has determined to be both
technologically feasible and economically justified. A full discussion
of the alternatives considered by DOE is presented in the ``Regulatory
Impact Analysis'' section of the TSD for this final rule.
H. Review Under the Treasury and General Government Appropriations Act,
1999
Section 654 of the Treasury and General Government Appropriations
Act, 1999 (Pub. L. 105-277) requires Federal agencies to issue a Family
Policymaking Assessment for any rule that may affect family well-being.
This rule would not have any impact on the autonomy or integrity of the
family as an institution. Accordingly, DOE has concluded that it is not
necessary to prepare a Family Policymaking Assessment.
I. Review Under Executive Order 12630
Pursuant to Executive Order 12630, ``Governmental Actions and
Interference with Constitutionally Protected Property Rights,'' 53 FR
8859 (March 18, 1988), DOE has determined that this regulation would
not result in any takings that might require compensation under the
Fifth Amendment to the U.S. Constitution.
J. Review Under the Treasury and General Government Appropriations Act,
2001
Section 515 of the Treasury and General Government Appropriations
Act, 2001 (44 U.S.C. 3516 note) provides for Federal agencies to review
most disseminations of information to the public under information
quality guidelines established by each agency pursuant to general
guidelines issued by OMB. OMB's guidelines were published at 67 FR 8452
(Feb. 22, 2002), and DOE's guidelines were published at 67 FR 62446
(Oct. 7, 2002). DOE has reviewed today's final rule under the OMB and
DOE guidelines and has concluded that it is consistent with applicable
policies in those guidelines.
K. Review Under Executive Order 13211
Executive Order 13211, ``Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use,'' 66 FR 28355
(May 22, 2001), requires Federal agencies to prepare and submit to OIRA
at OMB, a Statement of Energy Effects for any proposed significant
energy action. A ``significant energy action'' is defined as any action
by an agency that promulgates or is expected to lead to promulgation of
a final rule, and that: (1) Is a significant regulatory action under
Executive Order 12866, or any successor order; and (2) is likely to
have a significant adverse effect on the supply, distribution, or use
of energy, or (3) is designated by the Administrator of OIRA as a
significant energy action. For any proposed significant energy action,
the agency must give a detailed statement of any adverse effects on
energy supply, distribution, or use should the proposal be implemented,
and of reasonable alternatives to the action and their expected
benefits on energy supply, distribution, and use.
DOE has concluded that today's regulatory action, which sets forth
energy conservation standards for residential furnace fans, is not a
significant energy action because the
[[Page 38208]]
new standards are not likely to have a significant adverse effect on
the supply, distribution, or use of energy, nor has it been designated
as such by the Administrator at OIRA. Accordingly, DOE has not prepared
a Statement of Energy Effects on the final rule.
L. Review Under the Information Quality Bulletin for Peer Review
On December 16, 2004, OMB, in consultation with the Office of
Science and Technology Policy (OSTP), issued its Final Information
Quality Bulletin for Peer Review (the Bulletin). 70 FR 2664 (Jan. 14,
2005). The Bulletin establishes that certain scientific information
shall be peer reviewed by qualified specialists before it is
disseminated by the Federal Government, including influential
scientific information related to agency regulatory actions. The
purpose of the bulletin is to enhance the quality and credibility of
the Government's scientific information. Under the Bulletin, the energy
conservation standards rulemaking analyses are ``influential scientific
information,'' which the Bulletin defines as ``scientific information
the agency reasonably can determine will have or does have a clear and
substantial impact on important public policies or private sector
decisions.'' Id. at 2667.
In response to OMB's Bulletin, DOE conducted formal in-progress
peer reviews of the energy conservation standards development process
and analyses and has prepared a Peer Review Report pertaining to the
energy conservation standards rulemaking analyses. Generation of this
report involved a rigorous, formal, and documented evaluation using
objective criteria and qualified and independent reviewers to make a
judgment as to the technical/scientific/business merit, the actual or
anticipated results, and the productivity and management effectiveness
of programs and/or projects. The ``Energy Conservation Standards
Rulemaking Peer Review Report'' dated February 2007 has been
disseminated and is available at the following Web site:
www1.eere.energy.gov/buildings/appliance_standards/peer_review.html.
M. Congressional Notification
As required by 5 U.S.C. 801, DOE will report to Congress on the
promulgation of this rule prior to its effective date. The report will
state that it has been determined that the rule is a ``major rule'' as
defined by 5 U.S.C. 804(2).
VII. Approval of the Office of the Secretary
The Secretary of Energy has approved publication of this final
rule.
List of Subjects
10 CFR Part 429
Administrative practice and procedure, Commercial equipment,
Confidential business information, Energy conservation, Household
appliances, Imports, Reporting and recordkeeping requirements.
10 CFR Part 430
Administrative practice and procedure, Confidential business
information, Energy conservation, Household appliances, Imports,
Intergovernmental relations, Small businesses.
Issued in Washington, DC, on June 25, 2014.
David T. Danielson,
Assistant Secretary, Energy Efficiency and Renewable Energy.
For the reasons stated in the preamble, DOE amends parts 429 and
430 of chapter II, subchapter D, of title 10 of the Code of Federal
Regulations, as set forth below:
PART 429--CERTIFICATION, COMPLIANCE, AND ENFORCEMENT FOR CONSUMER
PRODUCTS AND COMMERCIAL AND INDUSTRIAL EQUIPMENT
0
1. The authority citation for part 429 continues to read as follows:
Authority: 42 U.S.C. 6291-6317.
Sec. 429.12 [Amended]
0
2. Section 429.12 is amended by:
0
a. Removing in paragraph (b)(13) ``429.54'' and adding in its place
``429.58'';
0
b. Removing in paragraph (d) table, first column, second row (i.e., for
products with a submission deadline of May 1st) the word ``and'' and
adding ``and Residential furnace fans'' at the end of the listed
products.
0
3. Section 429.58 is amended by:
0
a. Adding in paragraph (a)(2) introductory text ``within the scope of
appendix AA of subpart B of part 430'' after ``basic model of furnace
fan''; and
0
b. Adding paragraph (b).
The addition reads as follows:
Sec. 429.58 Furnace fans.
* * * * *
(b) Certification reports. (1) The requirements of Sec. 429.12 are
applicable to residential furnace fans; and
(2) Pursuant to Sec. 429.12(b)(13), a certification report shall
include the following public product-specific information: The fan
energy rating (FER) in watts per thousand cubic feet per minute (W/1000
cfm); the calculated maximum airflow at the reference system external
static pressure (ESP) in cubic feet per minute (cfm); the control
system configuration for achieving the heating and constant-circulation
airflow-control settings required for determining FER as specified in
the furnace fan test procedure (10 CFR part 430, subpart B, appendix
AA); the measured steady-state gas, oil, or electric heat input rate
(QIN) in the heating setting required for determining FER;
and for modular blowers, the manufacturer and model number of the
electric heat resistance kit with which it is equipped for
certification testing.
PART 430--ENERGY CONSERVATION PROGRAM FOR CONSUMER PRODUCTS
0
4. The authority citation for part 430 continues to read as follows:
Authority: 42 U.S.C. 6291-6309; 28 U.S.C. 2461 note.
0
5. Section 430.2 is amended by adding definitions for ``small-duct
high-velocity (SDHV) electric furnace'' and ``small-duct high-velocity
(SDHV) modular blower'' in alphabetical order to read as follows:
Sec. 430.2 Definitions.
* * * * *
Small-duct high-velocity (SDHV) electric furnace means an electric
furnace that:
(1) Is designed for, and produces, at least 1.2 inches of external
static pressure when operated at the certified air volume rate of 220-
350 CFM per rated ton of cooling in the highest default cooling
airflow-control setting; and
(2) When applied in the field, uses high velocity room outlets
generally greater than 1,000 fpm that have less than 6.0 square inches
of free area.
Small-duct high-velocity (SDHV) modular blower means a modular
blower that:
(1) Is designed for, and produces, at least 1.2 inches of external
static pressure when operated at the certified air volume rate of 220-
350 CFM per rated ton of cooling in the highest default cooling
airflow-controls setting; and
(2) When applied in the field, uses high velocity room outlets
generally greater than 1,000 fpm that have less than 6.0 square inches
of free area.
* * * * *
0
6. Section 430.32 is amended by adding paragraph (y) to read as
follows:
[[Page 38209]]
Sec. 430.32 Energy and water conservation standards and their
effective dates.
* * * * *
(y) Residential furnace fans. Residential furnace fans incorporated
in the products listed in Table 1 of this paragraph and manufactured on
and after July 3, 2019, shall have a fan energy rating (FER) value that
meets or is less than the following values:
Table 1--Energy Conservation Standards for Covered Residential Furnace
Fans*
------------------------------------------------------------------------
Product class FER ** (Watts/cfm)
------------------------------------------------------------------------
Non-Weatherized, Non- FER = 0.044 x QMax + 182
Condensing Gas Furnace Fan
(NWG-NC).
Non-Weatherized, Condensing FER = 0.044 x QMax + 195
Gas Furnace Fan (NWG-C).
Weatherized Non-Condensing FER = 0.044 x QMax + 199
Gas Furnace Fan (WG-NC).
Non-Weatherized, Non- FER = 0.071 x QMax + 382
Condensing Oil Furnace Fan
(NWO-NC).
Non-Weatherized Electric FER = 0.044 x QMax + 165
Furnace/Modular Blower Fan
(NWEF/NWMB).
Mobile Home Non-Weatherized, FER = 0.071 x QMax + 222
Non-Condensing Gas Furnace
Fan (MH-NWG-NC).
Mobile Home Non-Weatherized, FER = 0.071 x QMax + 240
Condensing Gas Furnace Fan
(MH-NWG-C).
Mobile Home Electric Furnace/ FER = 0.044 x QMax + 101
Modular Blower Fan (MH-EF/
MB).
Mobile Home Non-Weatherized Reserved
Oil Furnace Fan (MH-NWO).
Mobile Home Weatherized Gas Reserved
Furnace Fan (MH-WG) **.
------------------------------------------------------------------------
* Furnace fans incorporated into hydronic air handlers, SDHV modular
blowers, SDHV electric furnaces, and CAC/HP indoor units are not
subject to the standards listed in this table.
** QMax is the airflow, in cfm, at the maximum airflow-control setting
measured using the final DOE test procedure at 10 CFR part 430,
subpart B, appendix AA.
Note: The following will not appear in the Code of Federal
Regulations.
[[Page 38210]]
[GRAPHIC] [TIFF OMITTED] TR03JY14.001
[[Page 38211]]
[GRAPHIC] [TIFF OMITTED] TR03JY14.002
[FR Doc. 2014-15387 Filed 7-2-14; 8:45 am]
BILLING CODE 6450-01-P