Energy Conservation Program: Energy Conservation Standards for Residential Water Heaters, Direct Heating Equipment, and Pool Heaters, 65852-65997 [E9-28774]
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65852
Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
DEPARTMENT OF ENERGY
10 CFR Part 430
[Docket Number EE–2006–BT–STD–0129]
RIN 1904–AA90
Energy Conservation Program: Energy
Conservation Standards for
Residential Water Heaters, Direct
Heating Equipment, and Pool Heaters
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AGENCY: Office of Energy Efficiency and
Renewable Energy, Department of
Energy.
ACTION: Notice of proposed rulemaking
and public meeting.
SUMMARY: The Energy Policy and
Conservation Act (EPCA) prescribes
energy conservation standards for
various consumer products and
commercial and industrial equipment,
including residential water heaters,
direct heating equipment (DHE), and
pool heaters. EPCA also requires the
U.S. Department of Energy (DOE) to
determine whether more stringent,
amended standards for these products
would be technologically feasible and
economically justified, and would save
a significant amount of energy. In this
notice, DOE is proposing amended
energy conservation standards for
residential water heaters (other than
tabletop and electric instantaneous
models), gas-fired DHE, and gas-fired
pool heaters. DOE also is announcing a
public meeting to receive comment on
these proposed standards and associated
analyses and results.
DATES: DOE will hold a public meeting
on Thursday, January 7, 2010, from 9
a.m. to 4 p.m., in Washington, DC. DOE
must receive requests to speak at the
public meeting before 4 p.m.,
Wednesday, December 23, 2009. DOE
must receive a signed original and an
electronic copy of statements to be given
at the public meeting before 4 p.m.,
Wednesday, December 30, 2009.
DOE will accept comments, data, and
information regarding this notice of
proposed rulemaking (NOPR) before and
after the public meeting, but no later
than February 9, 2010. See section VII,
‘‘Public Participation,’’ of this NOPR for
details.
ADDRESSES: The public meeting will be
held at the U.S. Department of Energy,
Forrestal Building, Room 1E–245, 1000
Independence Avenue, SW.,
Washington, DC 20585–0121. To attend
the public meeting, please notify Ms.
Brenda Edwards at (202) 586–2945.
Please note that foreign nationals
visiting DOE Headquarters are subject to
advance security screening procedures.
Any foreign national wishing to
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participate in the meeting should advise
DOE as soon as possible by contacting
Ms. Brenda Edwards to initiate the
necessary procedures.
Any comments submitted must
identify the NOPR for Energy
Conservation Standards for Heating
Products, and provide the docket
number EE–2006–BT–STD–0129 and/or
regulatory information number (RIN)
number 1904–AA90. Comments may be
submitted using any of the following
methods:
1. Federal eRulemaking Portal: https://
www.regulations.gov. Follow the
instructions for submitting comments.
2. E-mail:
ResWaterDirectPoolHtrs@ee.doe.gov.
Include docket number EE–2006–BT–
STD–0129 and/or RIN 1904–AA90 in
the subject line of the message.
3. Mail: Ms. Brenda Edwards, U.S.
Department of Energy, Building
Technologies Program, Mailstop EE–2J,
1000 Independence Avenue, SW.,
Washington, DC 20585–0121. Please
submit one signed paper original.
4. Hand Delivery/Courier: Ms. Brenda
Edwards, U.S. Department of Energy,
Building Technologies Program, 950
L’Enfant Plaza, SW., Suite 600,
Washington, DC 20024. Telephone:
(202) 586–2945. Please submit one
signed paper original.
For detailed instructions on
submitting comments and additional
information on the rulemaking process,
see section VII of this document (Public
Participation).
Docket: For access to the docket to
read background documents or
comments received, visit the U.S.
Department of Energy, Resource Room
of the Building Technologies Program,
950 L’Enfant Plaza, SW., Suite 600,
Washington, DC, (202) 586–2945,
between 9 a.m. and 4 p.m., Monday
through Friday, except Federal holidays.
Please call Ms. Brenda Edwards at the
above telephone number for additional
information regarding visiting the
Resource Room.
FOR FURTHER INFORMATION CONTACT: Mr.
Mohammed Khan, U.S. Department of
Energy, Office of Energy Efficiency and
Renewable Energy, Building
Technologies Program, EE–2J, 1000
Independence Avenue, SW.,
Washington, DC 20585–0121.
Telephone: (202) 586–7892. E-mail:
Mohammed.Khan@ee.doe.gov.
Mr. Eric Stas or Mr. Michael Kido,
U.S. Department of Energy, Office of the
General Counsel, GC–72, 1000
Independence Avenue, SW.,
Washington, DC 20585–0121.
Telephone: (202) 586–9507. E-mail:
Eric.Stas@hq.doe.gov or
Michael.Kido@hq.doe.gov.
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For information on how to submit or
review public comments and on how to
participate in the public meeting,
contact Ms. Brenda Edwards, U.S.
Department of Energy, Office of Energy
Efficiency and Renewable Energy,
Building Technologies Program, EE–2J,
1000 Independence Avenue, SW.,
Washington, DC 20585–0121.
Telephone: (202) 586–2945. E-mail:
Brenda.Edwards@ee.doe.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Summary of the Proposed Rule
II. Introduction
A. Consumer Overview
B. Authority
C. Background
1. Current Standards
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
2. History of Standards Rulemaking for
Water Heaters, Direct Heating
Equipment, and Pool Heaters
III. General Discussion
A. Test Procedures
1. Water Heaters
2. Direct Heating Equipment
3. Standby Mode and Off Mode Energy
Consumption
B. Technological Feasibility
1. General
2. Maximum Technologically Feasible
Levels
C. Energy Savings
1. Determination of Savings
2. Significance of Savings
D. Economic Justification
1. Specific Criteria
a. Economic Impact on Manufacturers and
Consumers
b. Life-Cycle Costs
c. Energy Savings
d. Lessening of Utility or Performance of
Products
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. Consideration of Products for Inclusion
in This Rulemaking
a. Determination of Coverage Under the
Act
b. Covered Products Not Included in This
Rulemaking
2. Definition of Gas Hearth Direct Heating
Equipment
3. Product Classes
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
B. Screening Analysis
1. Comments on the Screening Analysis
a. General Comments
b. Water Heaters
2. Technologies Considered
3. Heat Pump Water Heaters Discussion
a. Consumer Utility
b. Production, Installation, and Servicing
Issues
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c. General Comments
C. Engineering Analysis
1. Representative Products for Analysis
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
2. Ultra-Low NOX Gas-Fired Storage Water
Heaters
3. Efficiency Levels Analyzed
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
4. Cost Assessment Methodology
a. Teardown Analysis
b. Cost Model
c. Manufacturing Production Cost
d. Cost-Efficiency Curves
e. Manufacturer Markup
f. Shipping Costs
g. Manufacturer Interviews
5. Results
6. Scaling to Additional Rated Storage
Capacities for Water Heaters
7. Energy Efficiency Equations
D. Markups to Determine Product Price
E. Life-Cycle Cost and Payback Period
Analyses
1. Product Cost
2. Installation Cost
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
3. Annual Energy Consumption
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
d. Rebound Effect
4. Energy Prices
5. Repair and Maintenance Costs
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
6. Product Lifetime
7. Discount Rates
8. Compliance Date of the Amended
Standards
9. Product Energy Efficiency in the Base
Case
a. Water Heaters
b. DHE
c. Pool Heaters
10. Inputs to Payback Period Analysis
11. Rebuttable-Presumption Payback
Period
F. National Impact Analysis—National
Energy Savings and Net Present Value
Analysis
1. Shipments
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
d. Impacts of Standards on Shipments
2. Other Inputs
a. Base-Case Forecasted Efficiencies
b. Standards-Case Forecasted Efficiencies
c. Annual Energy Consumption
d. Site-to-Source Energy Conversion
e. Total Installed Costs and Operating Costs
f. Discount Rates
3. Other Inputs
a. Effects of Standards on Energy Prices
G. Consumer Subgroup Analysis
H. Manufacturer Impact Analysis
1. Overview
a. Phase 1: Industry Profile
b. Phase 2: Industry Cash-Flow Analysis
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c. Phase 3: Subgroup Impact Analysis
2. GRIM Analysis
a. GRIM Key Inputs
b. GRIM Scenarios
3. Discussion of Comments
a. Responses to General Comments
b. Water Heater Comments
4. Manufacturer Interviews
a. Storage Water Heater Key Issues
b. Gas-Fired Instantaneous Water Heater
Key Issues
c. Direct Heating Equipment Key Issues
(Gas Wall Fan, Gas Wall Gravity, Gas
Floor, and Gas Room Direct Heating
Equipment)
d. Direct Heating Equipment Key Issues
(Gas Hearth Direct Heating Equipment)
e. Pool Heater Key Issues
I. Employment Impact Analysis
J. Utility Impact Analysis
K. Environmental Analysis
1. Impacts of Standards on Emissions
2. Valuation of CO2 Emissions Reductions
3. Valuation of Other Emissions
Reductions
V. Analytical Results
A. Trial Standard Levels
1. Water Heaters
2. Direct Heating Equipment
3. Gas-Fired Pool Heaters
B. Economic Justification and Energy
Savings
1. Economic Impacts on Consumers
a. Life-Cycle Cost and Payback Period
b. Analysis of Consumer Subgroups
c. Rebuttable Presumption Payback
2. Economic Impacts on Manufacturers
a. Water Heater Cash-Flow Analysis
Results
b. Direct Heating Equipment Cash-Flow
Analysis Results
c. Pool Heaters Cash-Flow Analysis Results
d. Impacts on Employment
e. Impacts on Manufacturing Capacity
f. Cumulative Regulatory Burden
g. Impacts on Small Businesses
3. National Impact Analysis
a. Significance of Energy Savings
b. Net Present Value of Consumer Costs
and Benefits
c. Net Present Value of Benefits from
Energy Price Impacts
d. Impacts on Employment
4. Impact on Utility or Performance of
Products
5. Impact of Any Lessening of Competition
6. Need of the Nation to Conserve Energy
7. Other Factors
C. Proposed Standards
1. Water Heaters
2. Direct Heating Equipment
3. Pool Heaters
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Order 12866
B. Review Under the Regulatory Flexibility
Act
1. Water Heater Industry
2. Pool Heater Industry
3. Direct Heating Equipment Industry
Characteristics
a. Description and Estimated Number of
Small Entities Regulated
b. Reasons for the Proposed Rule
c. Objectives of, and Legal Basis for, the
Proposed Rule
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d. Description and Estimate of Compliance
Requirements
e. Duplication, Overlap, and Conflict With
Other Rules and Regulations
f. Significant Alternatives to the Proposed
Rule
C. Review Under the Paperwork Reduction
Act of 1995
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
VII. Public Participation
A. Public Meeting
B. Procedure for Submitting Requests to
Speak
C. Conduct of Public Meeting
D. Submission of Comments
E. Issues on Which DOE Seeks Comment
VIII. Approval of the Office of the Secretary
I. Summary of the Proposed Rule
The Energy Policy and Conservation
Act (42 U.S.C. 6291 et seq.; EPCA or the
Act), as amended, provides that any
new or amended energy conservation
standard DOE prescribes for certain
consumer products, including
residential water heaters, direct heating
equipment (DHE), and pool heaters
(collectively referred to in this
document as the ‘‘three heating
products’’), shall be designed to
‘‘achieve the maximum improvement in
energy efficiency * * * which the
Secretary determines is technologically
feasible and economically justified.’’ (42
U.S.C. 6295(o)(2)(A)) Furthermore, the
new or amended standard must ‘‘result
in 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 the three types of heating
products listed above. Compliance with
the proposed standards would be
required for all residential water heaters
listed in Table I.1 that are manufactured
in or imported into the United States on
or after five years after the date of
publication of the final rule. The
proposed standards would apply to all
DHE and pool heaters listed in Table I.1
that are manufactured in or imported
into the United States on or after three
years after the date of publication of the
final rule. Table I.1 sets forth the
proposed standards for the products that
are the subject of this rulemaking.
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TABLE I.1—PROPOSED AMENDED ENERGY CONSERVATION STANDARDS FOR RESIDENTIAL WATER HEATERS, DIRECT
HEATING EQUIPMENT, AND POOL HEATERS
Product class
Proposed standard level
Residential water heaters *
Gas-fired Storage .................
Electric Storage ....................
For tanks with a Rated Storage Volume at or below 60
gallons: EF = 0.675 ¥ (0.0012 × Rated Storage Volume in gallons).
For tanks with a Rated Storage Volume at or below 80
gallons: EF = 0.96 ¥ (0.0003 × Rated Storage Volume in gallons).
For tanks with a Rated Storage Volume above 60 gallons: EF = 0.717 ¥ (0.0019 × Rated Storage Volume
in gallons).
For tanks with a Rated Storage Volume above 80 gallons: EF = 1.088 ¥ (0.0019 × Rated Storage Volume
in gallons).
EF = 0.68 ¥ (0.0019 × Rated Storage Volume in gallons).
EF = 0.82 ¥ (0.0019 × Rated Storage Volume in gallons).
Oil-fired Storage ...................
Gas-fired Instantaneous .......
Product class
Proposed standard level
Direct heating equipment **
Gas
Gas
Gas
Gas
Gas
Gas
Gas
Gas
Gas
Gas
Gas
Gas
Gas
Gas
Gas
wall fan type up to 42,000 Btu/h .............................................................................................................................
wall fan type over 42,000 Btu/h ..............................................................................................................................
wall gravity type up to 27,000 Btu/h .......................................................................................................................
wall gravity type over 27,000 Btu/h up to 46,000 Btu/h .........................................................................................
wall gravity type over 46,000 Btu/h ........................................................................................................................
floor up to 37,000 Btu/h ..........................................................................................................................................
floor over 37,000 Btu/h ...........................................................................................................................................
room up to 20,000 Btu/h .........................................................................................................................................
room over 20,000 Btu/h up to 27,000 Btu/h ...........................................................................................................
room over 27,000 Btu/h up to 46,000 Btu/h ...........................................................................................................
room over 46,000 Btu/h ..........................................................................................................................................
hearth up to 20,000 Btu/h .......................................................................................................................................
hearth over 20,000 Btu/h and up to 27,000 Btu/h ..................................................................................................
hearth over 27,000 Btu/h and up to 46,000 Btu/h ..................................................................................................
hearth over 46,000 Btu/h ........................................................................................................................................
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
AFUE
=
=
=
=
=
=
=
=
=
=
=
=
=
=
=
76%
77%
70%
71%
72%
57%
58%
62%
67%
68%
69%
61%
66%
67%
68%
Pool heaters
Gas-fired .........................................................................................................................................................................
Thermal Efficiency = 84%
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* EF is the ‘‘energy factor,’’ and the ‘‘Rated Storage Volume’’ equals the water storage capacity of a water heater (in gallons), as specified by
the manufacturer.
** Btu/h is ‘‘British thermal units per hour’’ and AFUE is ‘‘Annual Fuel Utilization Efficiency.’’
DOE’s analyses indicate that the
proposed standards would save a
significant amount of energy—an
estimated 2.85 quads of cumulative
energy over a 30-year period. This
amount is equivalent to 61 days of U.S.
gasoline use. Breaking these figures
down by product type, the national
energy savings of the proposed
standards is estimated to be 2.60 quads
for residential water heaters, 0.22 quads
for DHE, and 0.03 quads for pool
heaters.
The cumulative national net present
value (NPV) of total consumer costs and
savings from the proposed standards (in
2008$) ranges from $5.73 billion (at 7percent discount rate) to $18.1 billion
(at 3-percent discount rate). This is the
estimated total value of future
operating-cost savings minus the
estimated increased product and
installation costs, discounted to 2010.
The NPV of the proposed standards
for water heaters ranges from $4.79
billion (7-percent discount rate) to $15.6
billion (3-percent discount rate). DOE
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estimates the industry net present value
(INPV) for water heaters to be
approximately $1,455 million in 2008$.
If DOE adopts the proposed standards,
it estimates U.S. water heater
manufacturers will lose between 0.2
percent and 5.6 percent of the INPV,
which is approximately ¥$2.4 to
¥$81.0 million. However, the NPV for
consumers (at the 7-percent discount
rate) is 59 to 1996 times larger than the
industry losses due to the proposed
standards with the 7-percent discount
rate, and 193 to 6500 times larger than
the industry losses due to the proposed
standards with the 3-percent discount
rate.
For DHE, the NPV of the proposed
standards ranges from $0.91 billion (7percent discount rate) to $2.22 billion
(3-percent discount rate). DOE estimates
the INPV for DHE to be approximately
$104 million in 2008$. If DOE adopts
the proposed standards, it estimates
U.S. DHE manufacturers will lose
between 1.9 percent and 5.9 percent of
the INPV, which is approximately
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¥$2.0 to ¥$6.2 million. However, the
NPV for consumers (at the 7-percent
discount rate) is 147 to 455 times larger
than the industry losses due to the
proposed standards with the 7-percent
discount rate, and 358 to 1,110 times
larger than the industry losses due to
the proposed standards with the 3percent discount rate.
For pool heaters, the NPV of the
proposed standard ranges from $0.03
billion (7-percent discount rate) to $0.25
billion (3-percent discount rate). DOE
estimates the INPV for pool heaters to be
approximately $61.4 million in 2008$. If
DOE adopts the proposed standards, it
expects the impacts on U.S. pool heater
manufacturers will be between a gain of
0.9 percent and a loss of 12.1 percent of
the INPV, which is approximately
¥$0.5 million to ¥$7.5 million.
However, the NPV for consumers (at the
seven-percent discount rate) is 4 to 60
times larger than the industry losses due
to the proposed standards at the 7percent discount rate, and 33 to 498
times larger than the industry losses due
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to the proposed standards at the 3percent discount rate.
The economic impacts of the
proposed standards on individual
consumers (i.e., the average life-cycle
cost (LCC) savings) are predominately
positive. For water heaters, DOE
projects that the average LCC impact is
a gain of $68 for gas-fired storage water
heaters, $39 for electric storage water
heaters, and $395 for oil-fired storage
water heaters, and no change for gasfired instantaneous water heaters. For
DHE, DOE projects that the average LCC
impact for consumers is a gain of $104
for gas wall fan DHE, $192 for gas wall
gravity DHE, $13 for gas floor DHE, $143
for gas room DHE, and $96 for gas
hearth DHE. For pool heaters, DOE
projects that the average LCC impact for
consumers is a loss of $13 (which
represents only 0.2 percent of the
average total LCC).
In addition, the proposed standards
would be expected to provide
significant environmental benefits. The
proposed standards would potentially
result in cumulative greenhouse gas
emission reductions of 167 million tons
(Mt) of carbon dioxide (CO2) from 2013
to 2045. Specifically, the proposed
standards for water heaters would
reduce CO2 emissions by 154 Mt; the
proposed standards for DHE would
reduce CO2 emissions by 8.5 Mt; and the
proposed standard for pool heaters
would reduce CO2 emissions by 4.2 Mt.
For the three types of heating products
together, DOE estimates that the range of
the monetized value of CO2 emission
reductions based on global estimates of
the value of avoided CO2 is $0.399
billion to $4.386 billion at a 7-percent
discount rate and $0.902 billion to
$9.925 billion at a 3-percent discount
rate.
The proposed standards would also
be expected to result in reduction in
cumulative nitrogen oxides (NOX)
emissions of 129 kilotons (kt).
Specifically, the proposed water heater
standards would result in cumulative
NOX emissions reductions of 118 kt; the
proposed standards for DHE would
result in 7.7 kt of NOX emissions
reductions; and the proposed standard
for pool heaters would result in 3.7 kt
of NOX emissions reductions.
The proposed standards for heating
products would also be expected to
result in power plant mercury (Hg)
emissions reductions. For water heaters,
cumulative Hg emissions would be
reduced by 0.20 tons (t). The proposed
standards for DHE and pool heaters
would be expected to have a negligible
impact on mercury emissions.
The benefits and costs of today’s
proposed rule can also be expressed in
terms of annualized values. The
annualized values refer to consumer
operating cost savings, consumer
incremental product and installation
costs, the quantity of emissions
reductions for CO2, NOX, and Hg, and
the monetary value of emissions
reductions. DOE calculated annualized
values using discount rates of three
percent and seven percent. Although
DOE calculated annualized values, this
does not imply that the time-series of
cost and benefits from which the
annualized values were determined are
a steady stream of payments.
Table I.2, Table I.3, and Table I.4
present the annualized values for the
standards proposed for water heaters,
DHE, and pool heaters, respectively.
The tables also present the annualized
net benefit that results from summing
the two monetary benefits and
subtracting the consumer incremental
product and installation costs. Although
summing the value of operating cost
savings with the value of CO2
reductions (and other emissions
reductions) provides a valuable
perspective, please note the following.
The operating cost savings are domestic
U.S. consumer monetary savings found
in market transactions, but in contrast,
the CO2 value is based on an estimate
of imputed marginal social cost of
carbon (SCC), which is meant to reflect
the global benefits of CO2 reductions. In
addition, the assessments of operating
cost savings and CO2 savings are
performed with different computer
models, leading to different time frames
for analysis. The operating cost savings
are measured for the lifetime of
appliances shipped in 2015–2045 or
2013–2043. The value of CO2, on the
other hand is meant to reflect the
present value of all future climaterelated impacts, even those beyond
2065.
TABLE I.2—ANNUALIZED BENEFITS AND COSTS OF PROPOSED STANDARDS FOR WATER HEATERS (TSL 4)
Primary estimate
(AEO reference case)
Category
Low estimate
(AEO low-growth case)
Unit
7%
High estimate
(AEO high-growth
case)
3%
7%
3%
7%
3%
Benefits
Monetized Operating Cost Savings ........
Quantified Emissions Reductions ...........
1487.1
4.58
3.54
0.009
157.1
1842.4
4.92
3.79
0.008
187.3
1383.7
5.34
4.17
(0.003)
184.8
1708.4
5.28
4.11
(0.011)
222.1
1590.5
0.61
0.58
0.010
20.2
1976.2
1.04
0.92
0.013
41.9
NOX ........................
Hg ...........................
Monetized Avoided Emissions Reductions * (Million 2008$).
Million 2008$ ..........
CO2 (Mt) .................
NOX (kt) ..................
Hg (t) ......................
CO2 (at $20/t) .........
8.2
0.1
9.1
0.1
9.7
(0.1)
10.9
(0.1)
0.4
0.1
1.6
0.2
917.3
894.4
861.7
997.0
973.4
1112.4
674.1
1068.9
613.7
1044.7
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Costs
Monetized Incremental Product and Installation Costs.
Million 2008$ ..........
945.5
Net Benefits
Monetized Value ** ..................................
Million 2008$ ..........
698.8
* For CO2, benefits reflect value of $20/t, which is in the middle of the values considered by DOE for valuing the potential global benefits resulting from reduced CO2 emissions. For NOX and Hg, the benefits reflect values of $2,491/t and $17 million/t, respectively. These values are the
midpoint of the range considered by DOE.
** Monetized Value does not include monetized avoided emissions reductions for NOX and Hg.
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TABLE I.3—ANNUALIZED BENEFITS AND COSTS OF PROPOSED STANDARDS FOR DIRECT HEATING EQUIPMENT (TSL 3)
Primary estimate
(AEO reference case)
Category
Low estimate
(AEO low-growth case)
Unit
7%
3%
7%
3%
High estimate
(AEO high-growth
case)
7%
3%
Benefits
Monetized Operating Cost Savings ........
Quantified Emissions Reductions ...........
Monetized Avoided CO2 Value (at $20/
t) .*
Million 2008$ ..........
CO2 (Mt) .................
NOX (kt) ..................
Hg (t) ......................
Million 2008$ ..........
132.2
0.24
0.22
0.000
8.2
164.4
0.27
0.24
(0.001)
9.8
126.4
0.43
0.36
0.000
2.5
156.9
0.46
0.38
(0.001)
2.9
136.2
0.13
0.14
0.000
21.0
169.6
0.14
0.15
0.000
42.6
40.6
41.8
40.6
41.8
40.6
133.5
87.1
119.2
115.4
171.6
Costs
Monetized Incremental Product and Installation Costs.
Million 2008$ ..........
41.8
Net Benefits
Monetized Value .....................................
Million 2008$ ..........
98.5
* For CO2, benefits reflect value of $20/t, which is in the middle of the values considered by DOE for valuing the potential global benefits resulting from reduced CO2 emissions. For NOX and Hg, the annual benefits are very small and are thus not reported in the table.
TABLE I.4—ANNUALIZED BENEFITS AND COSTS OF PROPOSED STANDARDS FOR POOL HEATERS (TSL 4)
Primary estimate
(AEO reference case)
Category
Low estimate
(AEO low-growth case)
Unit
7%
3%
High estimate
(AEO high-growth
case)
7%
3%
7%
68.79
0.13
0.119
0.000
4.84
57.29
0.16
0.134
(0.000)
5.24
65.66
0.17
0.143
(0.001)
6.08
61.62
0.09
0.085
(0.000)
3.01
70.86
0.10
0.091
0.000
3.47
54.59
56.66
54.59
56.66
54.59
19.04
5.88
17.15
7.97
19.74
3%
Benefits
Monetized Operating Cost Savings ........
Quantified Emissions Reductions ...........
Monetized Avoided CO2 Value (at $20/
t).*
Million 2008$ ..........
CO2 (Mt) .................
NOX (kt) ..................
Hg (t) ......................
Million 2008$ ..........
59.88
0.13
0.112
0.000
4.20
Costs
Monetized Incremental Product and Installation Costs.
2008$ .....................
56.66
Net Benefits
Monetized Value .....................................
Million 2008$ ..........
7.41
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
* For CO2, benefits reflect value of $20/t, which is in the middle of the values considered by DOE for valuing the potential global benefits resulting from reduced CO2 emissions. For NOX and Hg, the annual benefits are very small and are thus not reported in the table.
DOE has tentatively concluded that
the proposed standards represent the
maximum improvement in energy
efficiency that is technologically
feasible and economically justified, and
would result in significant conservation
of energy. Products achieving these
standard levels are already
commercially available. Based on the
analyses culminating in this proposal,
DOE found the benefits to the Nation of
the proposed standards (energy savings,
consumer LCC savings, national NPV
increase, and emission reductions)
outweigh the burdens (loss of INPV and
LCC increases for some consumers).
DOE considered higher efficiency levels
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as trial standard levels, and is still
considering them in this rulemaking;
however, DOE has tentatively
concluded that the burdens of the
higher efficiency levels would outweigh
the benefits. With that said, based on
consideration of public comments DOE
receives in response to this notice and
related information, DOE may adopt
efficiency levels in the final rule that are
either higher or lower than the proposed
standards, or some level(s) in between
the proposed standards and other
efficiency levels presented.
DOE is proposing TSL 4 for
residential water heaters as the level
which it has tentatively concluded meet
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the applicable statutory criteria (i.e., the
highest level that is technologically
feasible, economically justified, and
would result in significant conservation
of energy). Based upon public
comments and any accompanying data
submissions, DOE would strongly
consider other TSLs (as presented in
this NOPR or at some level in between),
some of which might provide an even
higher level of energy savings and
promote a market for advanced water
heating technologies, including heat
pump and condensing water heaters.
Accordingly, DOE is presenting a
variety of issues throughout today’s
notice upon which it is seeking
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comment which will bear upon its
consideration of TSL 5 or TSL 6 for
residential water heaters in the final
rule.
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II. Introduction
A. Consumer Overview
EPCA currently prescribes energy
conservation standards for the three
heating products that are the subject of
this rulemaking. DOE is proposing to
raise the standards for the products
shown in Table I.1. The proposed
standards would apply to residential
water heaters manufactured or imported
on or after five years after the final rule
publication date (i.e., approximately
March 31, 2015). The proposed
standards would apply to DHE and pool
heaters manufactured or imported on or
after three years after the final rule
publication date (i.e., approximately
March 31, 2013).
DOE’s analyses suggest that
consumers would realize benefits from
the proposed standards. Although DOE
expects that the purchase price of the
more-efficient heating products would
be higher than the average prices of
these products today, for most
consumers, the energy efficiency gains
would result in lower energy costs that
would more than offset the higher
purchase price. For water heaters, the
median payback period is 2.7 years for
gas-fired storage water heaters, 5.8 years
for electric storage water heaters, 0.5
years for oil-fired storage water heaters,
and 23.5 years for gas-fired
instantaneous water heaters. For DHE,
the median payback period is 6.0 years
for gas wall fan DHE, 8.3 years for gas
wall gravity DHE, 14.7 years for gas
floor DHE, 5.3 years for gas room DHE
and 0.0 years for gas hearth DHE. (The
reason that the median payback period
for gas hearth DHE is zero is because for
about two-thirds of the consumers, there
is no incremental cost to get to the
proposed standard level). For pool
heaters, the median payback period is
13.0 years.
When the overall net savings are
summed over the lifetime of these
products, water heater consumers will
save, on average, $68 for gas-fired
storage water heaters, $30 for electric
storage water heaters, $305 for oil-fired
storage water heaters, and $0 for gasfired instantaneous water heaters,
compared to their life-cycle
expenditures on base-case water heaters
(i.e., the equipment expected to be
purchased in the absence of revised
energy conservation standards). (For
gas-fired instantaneous water heaters,
the average LCC for the proposed
standard level is the same as the average
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LCC in the base case, so the savings are
zero.) The average LCC impact for DHE
consumers is a gain of $104 for gas wall
fan DHE, $192 for gas wall gravity DHE,
$13 for gas floor DHE, $143 for gas room
DHE, and $96 for gas hearth DHE,
compared to their life-cycle
expenditures on base-case products.
Pool heater consumers will see, on
average, a slight increase in their lifecycle costs, compared to their
expenditures on base-case products.
B. Authority
Title III of EPCA sets forth a variety
of provisions designed to improve
energy efficiency. Part A 1 of Title III (42
U.S.C. 6291–6309) establishes the
Energy Conservation Program for
Consumer Products Other Than
Automobiles. The program covers
consumer products and certain
commercial equipment (referred to
hereafter as ‘‘covered products’’),
including the three types of heating
products that are subject to this
rulemaking. (42 U.S.C. 6292(a)(4), (9)
and (11)) EPCA prescribes energy
conservation standards for the three
heating products. (42 U.S.C. 6295(e)(1)–
(3)) The statute further directs DOE to
conduct two cycles of rulemakings to
determine whether to amend these
standards. (42 U.S.C. 6295(e)(4)) As
explained in further detail in section
II.C, ‘‘Background,’’ this rulemaking
represents the second round of
amendments to the water heater
standards, and the first round of
amendments to the DHE and pool heater
standards.
Under the Act, DOE’s energy
conservation program for covered
products consists essentially of three
parts: (1) Testing; (2) labeling; and (3)
Federal energy conservation standards.
The Federal Trade Commission (FTC) is
responsible for the labeling provisions
for consumer products, and DOE
implements the remainder of the
program. Section 323 of the Act
authorizes DOE, subject to certain
criteria and conditions, to develop test
procedures to measure the energy
efficiency, energy use, or estimated
annual operating cost of each covered
product. Manufacturers of covered
products must use the DOE test
procedure as the basis for certifying to
DOE that their products comply with
applicable energy conservation
standards adopted under EPCA and for
representing the efficiency of those
products. Similarly, DOE must use these
test procedures to determine whether
1 This part was originally titled Part B. It was
redesignated Part A in the United States Code for
editorial reasons.
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the products comply with standards
adopted under EPCA. (42 U.S.C. 6293)
The test procedures for water heaters,
unvented DHE, vented DHE, and pool
heaters appear at Title 10 Code of
Federal Regulations (CFR) part 430,
subpart B, appendices E, G, O, and P,
respectively.
EPCA provides criteria for prescribing
amended standards for covered
products. As indicated above, any
amended 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)) Furthermore,
EPCA precludes DOE from adopting any
standard that would not result in
significant conservation of energy. (42
U.S.C. 6295(o)(3)(B)) Moreover, DOE
may not prescribe a standard for certain
products (including the three heating
products) if no test procedure has been
established. (42 U.S.C. 6295(o)(3)(A))
The Act also provides that, 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 do so 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 imposition
of the standard;
3. The total projected amount of
energy (or, as applicable, water) savings
likely to result directly from the
imposition of the standard;
4. Any lessening of the utility or the
performance of the covered products
likely to result from the imposition of
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 imposition of the
standard;
6. The need for national energy and
water conservation; and
7. Other factors the Secretary
considers relevant.
(42 U.S.C. 6295(o)(2)(B)(i)(I)–(VII))
Furthermore, EPCA contains what is
commonly known as an ‘‘antibacksliding’’ provision, which prohibits
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the Secretary from prescribing any
amended 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 a new or amended
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) with 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))
Under 42 U.S.C. 6295(o)(2)(B)(iii),
EPCA 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. * * *’’
Under 42 U.S.C. 6295(q)(1), EPCA
specifies requirements for promulgation
of a standard for a type or class of
covered product that has two or more
subcategories. DOE must specify a
different standard level than that which
applies generally to such type or class
of products ‘‘for any group of covered
products which have the same function
or intended use, if * * * 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’’ than applies or will apply to
the other products. (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))
Federal energy conservation
requirements generally supersede State
laws or regulations concerning energy
conservation testing, labeling, and
standards. (42 U.S.C. 6297(a)–(c))
However, DOE can grant waivers of
Federal preemption for particular State
laws or regulations in accordance with
the procedures and other provisions of
section 327(d) of the Act. (42 U.S.C.
6297(d))
Finally, section 310(3) of the Energy
Independence and Security Act of 2007
(EISA 2007; Pub. L. 110–140) amended
EPCA to prospectively require that
energy conservation standards address
standby mode and off mode energy use.
Specifically, when DOE adopts new or
amended standards for a covered
product after July 1, 2010, the final rule
must, if justified by the criteria for
adoption of standards in section 325(o)
of EPCA, incorporate standby mode and
off mode energy use into a single
standard if feasible, or otherwise adopt
a separate standard for such energy use
for that product. (42 U.S.C. 6295(gg)(3))
Because the final rule in this rulemaking
is scheduled for adoption by March
2010, this requirement does not apply in
this rulemaking, and DOE has not
attempted to address the standby mode
or off mode energy use here. DOE is
currently working on a test procedure
rulemaking to address standby mode
and off mode energy consumption for
the three types of heating products that
are the subject of this rulemaking.
C. Background
1. Current Standards
a. Water Heaters
On January 17, 2001, DOE prescribed
the current energy conservation
standards for residential water heaters
manufactured on or after January 20,
2004. 66 FR 4474. This final rule
completed the first amended standards
rulemaking for water heaters required
under 42 U.S.C. 6295(e)(4)(A). The
standards consist of minimum energy
factors (EF) that vary based on the
storage volume of the water heater, the
type of energy it uses (i.e., gas, oil, or
electricity), and whether it is a storage,
instantaneous, or tabletop model. 10
CFR 430.32(d). The water heater energy
conservation standards are set forth in
Table II.1 below.
TABLE II.1—CURRENT FEDERAL ENERGY CONSERVATION STANDARDS FOR RESIDENTIAL WATER HEATERS
Product class
1.
2.
3.
4.
5.
6.
Energy factor as of January 20, 2004
Gas-Fired Storage Water Heater .........................................................
Oil-Fired Storage Water Heater ...........................................................
Electric Storage Water Heater .............................................................
Tabletop Water Heater .........................................................................
Gas-Fired Instantaneous Water Heater ...............................................
Instantaneous Electric Water Heater ...................................................
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
b. Direct Heating Equipment
EPCA prescribes the energy
conservation standards for DHE, which
apply to gas-fired products
manufactured on or after January 1,
1990. (42 U.S.C. 6295(e)(3)) These
standards consist of several minimum
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EF
EF
EF
EF
EF
EF
=
=
=
=
=
=
0.67
0.59
0.97
0.93
0.62
0.93
¥
¥
¥
¥
¥
¥
(0.0019 × Rated Storage Volume in gallons).
(0.0019 × Rated Storage Volume in gallons).
(0.00132 × Rated Storage Volume in gallons).
(0.00132 × Rated Storage Volume in gallons).
(0.0019 × Rated Storage Volume in gallons).
(0.00132 × Rated Storage Volume in gallons).
annual fuel utilization efficiency
(AFUE) levels, each of which applies to
units of a particular type (i.e., wall fan,
wall gravity, floor, room) and heating
capacity range. Id. These statutory
standards have been codified in DOE’s
regulations at 10 CFR 430.32(i). The
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DHE energy conservation standards are
set forth in Table II.2 below. DOE notes
that while electric DHE are available,
standards for these products are outside
the scope of today’s rulemaking. See
IV.A.1.b for a more detailed discussion
of DHE coverage under EPCA.
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TABLE II.2—CURRENT FEDERAL ENERGY CONSERVATION STANDARDS FOR DIRECT HEATING EQUIPMENT
Annual fuel
utilization
efficiency, as of
Jan. 1, 1990
%
Direct heating equipment design type
Product class
Btu/h
Gas Wall Fan ...........................................
Up to 42,000 ..............................................................................................................
Over 42,000 ...............................................................................................................
Up to 10,000 ..............................................................................................................
Over 10,000 and up to 12,000 ..................................................................................
Over 12,000 and up to 15,000 ..................................................................................
Over 15,000 and up to 19,000 ..................................................................................
Over 19,000 and up to 27,000 ..................................................................................
Over 27,000 and up to 46,000 ..................................................................................
Over 46,000 ...............................................................................................................
Up to 37,000 ..............................................................................................................
Over 37,000 ...............................................................................................................
Up to 18,000 ..............................................................................................................
Over 18,000 and up to 20,000 ..................................................................................
Over 20,000 and up to 27,000 ..................................................................................
Over 27,000 and up to 46,000 ..................................................................................
Over 46,000 ...............................................................................................................
Gas Wall Gravity .....................................
Gas Floor .................................................
Gas Room ...............................................
c. Pool Heaters
EPCA requires pool heaters
manufactured on or after January 1,
1990 to have a thermal efficiency no less
than 78 percent. The thermal efficiency
for this product is measured by testing
in accordance with the DOE test
procedure for pool heaters codified in
10 CFR 430, subpart B, Appendix P. The
statutory standard for pool heaters has
been codified in DOE’s regulations at 10
CFR 430.32(k).
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
2. History of Standards Rulemaking for
Water Heaters, Direct Heating
Equipment, and Pool Heaters
Before being amended by the National
Appliance Energy Conservation Act of
1987 (NAECA; Pub. L. 100–12), Title III
of EPCA included water heaters and
home heating equipment as covered
products. NAECA’s amendments to
EPCA included replacing the term
‘‘home heating equipment’’ with ‘‘direct
heating equipment,’’ adding pool
heaters as a covered product,
establishing energy conservation
standards for these two products as well
as residential water heaters, and
requiring that DOE determine whether
these standards should be amended. (42
U.S.C. 6295(e)(1)–(4)) As indicated
above, DOE amended the statutorilyprescribed standards for water heaters
in 2001 (66 FR 4474 (Jan. 17, 2001)), but
has not amended the statutory standards
for DHE or pool heaters.
DOE initiated this rulemaking on
September 27, 2006, by publishing on
its Web site its ‘‘Rulemaking Framework
for Residential Water Heaters, Direct
Heating Equipment, and Pool Heaters.’’
(A PDF of the framework document is
available at https://www.eere.energy.gov/
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buildings/appliance_standards/
residential/pdfs/heating_equipment
framework_092706.pdf.) DOE also
published a notice announcing the
availability of the framework document
and a public meeting and requesting
comments on the matters raised in the
document. 71 FR 67825 (Nov. 24, 2006).
The framework document described the
procedural and analytical approaches
that DOE anticipated using to evaluate
potential energy conservation standards
for the three heating products and
identified various issues to be resolved
in conducting the rulemaking.
DOE held the public meeting on
January 16, 2007, where it: Presented
the contents of the framework
document; described the analyses it
planned to conduct during the
rulemaking; sought comments from
interested parties on these subjects; and
in general, sought to inform interested
parties about, and facilitate their
involvement in, the rulemaking.
Interested parties that participated in
the public meeting discussed the
following issues: the scope of coverage
for the rulemaking; product classes;
efficiency levels analyzed in the
engineering analysis; installation,
repair, and maintenance costs; and
product and fuel switching. At the
meeting and during the public comment
period, DOE received many comments
that helped DOE identify and resolve
the issues involved in this rulemaking
to consider amended energy
conservation standards for the three
types of heating products.
DOE then gathered additional
information and performed preliminary
analyses to help develop the potential
energy conservation standards for the
three heating products. This process
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73
74
59
60
61
62
63
64
65
56
57
57
58
63
64
65
culminated in DOE’s announcement of
another public meeting to discuss and
receive comments on the following
matters: The product classes DOE
planned to analyze; the analytical
framework, models, and tools that DOE
has been using to evaluate standards;
the results of the preliminary analyses
DOE performed; and potential standard
levels that DOE could consider. 74 FR
1643 (Jan. 13, 2009) (the January 2009
notice). DOE also invited written
comments on these subjects and
announced the availability of a
preliminary technical support document
(preliminary TSD) to inform interested
parties and enable them to provide
comments. Id. (The preliminary TSD is
available at: https://
www1.eere.energy.gov/buildings/
appliance_standards/residential/water_
pool_heaters_prelim_tsd.html.) DOE
stated its interest in receiving comments
on other relevant issues that
participants believe DOE should address
in this NOPR, which would affect
energy conservation standards for the
three heating products. Id. at 1646.
The preliminary TSD provided an
overview of the activities DOE
undertook in developing potential
standard levels for the three heating
products and discussed the comments
DOE received in response to the
framework document. It also described
the analytical framework that DOE used
(and continues to use in this
rulemaking), including a description of
the methodology, the analytical tools,
and the relationships among the various
analyses that are part of the rulemaking.
The preliminary TSD described in detail
each analysis DOE performed up to that
point, including inputs, sources,
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methodologies, and results. DOE
examined each of the three heating
products in each of the following
analyses:
• A market and technology
assessment addressed the scope of this
rulemaking (i.e., which types of heating
products this rulemaking covers),
identified the potential classes for each
product, characterized the markets for
these products, and reviewed
techniques and approaches for
improving product efficiency.
• A screening analysis reviewed
technology options to improve the
efficiency of each of the three heating
products and weighed these options
against DOE’s four prescribed screening
criteria (i.e., technological feasibility;
practicability to manufacture, install,
and service; adverse impacts on product
utility or product availability; and
adverse impacts on health or safety).
• An engineering analysis estimated
the manufacturer selling prices (MSPs)
associated with more efficient water
heaters, DHE, and pool heaters.
• An energy use analysis estimated
the annual energy use in the field of
each of the three heating products.
• A markups analysis developed
factors to convert estimated MSPs
derived from the engineering analysis to
consumer prices.
• A life-cycle cost 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 a
given standard.
• A payback period (PBP) analysis
estimated the amount of time it takes
consumers to recover the higher
purchase expense of more energy
efficient products through lower
operating costs.
• A shipments analysis estimated
shipments of each of the three heating
products over the time period examined
in the analysis (i.e., 2015–2045 for water
heaters and 2013–2043 for DHE and
pool heaters) under both a base-case
scenario (i.e., assuming no new
standards) and a standards-case scenario
(i.e., assuming new standards at the
various levels under consideration). The
shipments analysis provides key inputs
to the national impact analysis (NIA).
• A national impact analysis assessed
the aggregate impacts at the national
level of potential energy conservation
standards for each of the three heating
products, as measured by the net
present value of total consumer
economic impacts and national energy
savings.
• A preliminary manufacturer impact
analysis took the initial steps in
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evaluating the effects on manufacturers
of potential new efficiency standards.
In the January 2009 notice, DOE
summarized in detail the nature and
function of the following analyses: (1)
Engineering, (2) energy use
characterization, (3) markups to
determine installed prices, (4) LCC and
PBP analyses, and (5) national impact
analysis. 74 FR 1643, 1645–46 (Jan. 13,
2009).
The public meeting announced in the
January 2009 notice took place on
February 9, 2009. At this meeting, DOE
presented the methodologies and results
of the analyses set forth in the
preliminary TSD. The major topics
discussed at the February 2009 public
meeting included the product classes for
the rulemaking, the treatment of ultralow NOX water heaters, heat pump
water heaters screening considerations,
installation costs and concerns for heat
pump water heaters, the manufacturing
costs for max-tech products, pool heater
shipments, the energy-use adjustment
for gas-fired instantaneous water
heaters, and the compliance dates for
amended standards. The comments
received since publication of the
January 2009 notice, including those
received at the February 2009 public
meeting, have contributed to DOE’s
proposed resolution of the issues in this
rulemaking. This NOPR quotes and
summarizes many of these comments,
and responds to the issues they raised.
(A parenthetical reference at the end of
a quotation or paraphrase provides the
location of the relevant source in the
public record.)
III. General Discussion
A. Test Procedures
As noted above, DOE’s current test
procedures for water heaters, vented
DHE, and pool heaters appear at Title 10
Code of Federal Regulations (CFR) part
430, subpart B, appendices E, O, and P,
respectively. DOE uses these test
procedures to determine whether the
products comply with standards
adopted under EPCA. (42 U.S.C. 6293)
1. Water Heaters
During the preliminary analysis, DOE
received a number of comments on the
test procedure for residential water
heaters. Edison Electric Institute (EEI)
stated that DOE should modify the
values for hot water use and the number
of daily draws in the water heater test
procedure to more closely resemble
field conditions (i.e., include more
shorter draws, rather than fewer longer
draws), and SEISCO INTERNATIONAL
(SEISCO) recommended the adoption of
a testing protocol for water heaters that
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can best simulate real world usage
patterns. (EEI, No. 40 at p.5; SEISCO,
No. 41 at p. 3) 2 Southern Company
(Southern), Bock Water Heaters (Bock),
and EEI all stated that DOE needs to
revise the test procedure to account for
the actual performance of gas-fired
instantaneous water heaters. (Southern,
No. 50 at p. 2; Bock, No. 53 at p. 3; EEI,
No. 40 at p. 5)
DOE acknowledges that the actual hot
water use and the number of daily
draws seen in the field can vary greatly
depending upon occupancy and
consumer usage patterns for each type
of water heater. DOE’s test procedure
attempts to normalize the usage across
fuel types by specifying a typical draw
pattern and total hot water usage. DOE
accounts for the variability of these
parameters on the energy consumption
of the water heater using: (1) A hot
water draw model that accounts for field
conditions in a representative sample of
U.S. homes; and (2) data from field
studies of gas-fired instantaneous water
heaters that incorporate a distribution of
correction factors to account for actual
field operation. These adjustments are
used to estimate the impacts on
consumers of amended standards in the
LCC and PBP analysis.
In the past, the issue of whether the
efficiency levels examined by DOE in
this NOPR are achievable using the
current DOE test procedures for
residential water heaters has received
much attention from commenters. In
particular, several manufacturers either
through manufacturer interviews or
docket submissions have expressed
their concern that as efficiencies
increase and approach the theoretical
maximum efficiency for electric
resistance water heating (i.e., 1.0 EF),
the ability to consistently and
repeatedly achieve those efficiencies is
significantly hindered by the variations
and inaccuracies that are inherent in the
current DOE test procedure. During
engineering and manufacturer
interviews, manufacturers have
indicated that this becomes an
increasingly important issue at 0.95 EF.
Rheem Manufacturing Company
(Rheem) commented that the nature of
the DOE test procedure, including test
set-up variations, instrumentation, and
measurement inaccuracies, limits the
attainable energy factor values. Rheem
2 ‘‘EEI, No. 40 at p. 5’’ refers to: (1) To a statement
that was submitted by the Edison Electric Institute.
It was recorded in the Resource Room of the
Building Technologies Program in the docket under
‘‘Energy Conservation Program: Energy
Conservation Standards for Residential Water
Heaters, Direct Heating Equipment, and Pool
Heaters,’’ Docket Number EERE–2006–BT–STD–
0129, as comment number 40; and (2) a passage that
appears on page 5 of that statement.
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stated that DOE should reevaluate the
current test procedure to determine
whether it can accurately measure the
EF levels being proposed for standards,
especially if a standard is set at or near
the theoretically maximum-attainable
EF. (Rheem, No. 49 at pp. 3–4)
DOE agrees with Rheem’s assertion
that as the theoretical limit is reached
for a covered product utilizing a given
technology (e.g., electric resistance
storage water heaters), the limitations
imposed by the instrumentation, test
set-up, and measurement accuracies
become increasingly important. In
response, DOE notes that there are
currently several models in AHRI’s
Directory of certified residential water
heaters that are listed with energy
factors of 0.95 EF over a range of storage
volumes. DOE believes this fact
demonstrates that it is possible for
manufacturers to make products that
can repeatedly achieve an energy factor
of 0.95 and can be certified at this
efficiency level. In order to further
verify the ability of manufacturers to
achieve this efficiency level, DOE
performed its own research, which
consisted of independent third-party
testing of several water heater models
rated at 0.95 EF with rated storage
volumes spanning 30 to 80 gallons. Of
the five models tested that were rated at
0.95 EF, four fell within the acceptable
range of values to be rated and certified
at 0.95 EF, while only one model failed
to achieve an efficiency that would be
acceptable for a 0.95 EF rating. This
further demonstrates the ability of
manufacturers to consistently achieve
0.95 EF, as the large majority of the
sample of models tested did reach an
acceptable value for certification at 0.95
EF.
DOE has tentatively concluded that
the TSLs being considering in the
proposed rule provide ample room for
manufacturers to innovatively design
products which meet the standards
using the existing test procedure. DOE’s
test results further provide evidence that
electric storage water heaters exist at
TSL 4 (0.95 EF at the representative
rated storage capacity) across a range of
storage volumes in the market today. In
addition, DOE notes that once the
product surpasses the theoretical
maximum of a given technology by
utilizing a different design these
problems are mitigated. Consequently,
DOE does not believe commenter’s
concerns regarding the repeatability and
accuracy of the test procedure apply to
TSL 6 and 7, where DOE is considering
advance technology water heaters,
including heat pump water heaters.
The Natural Resources Defense
Council (NRDC) stated that the water
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heater test procedure fails to capture all
of the cost-effective efficiency measures;
the American Council for an EnergyEfficient Economy (ACEEE) and NRDC
both stated that due to test procedure
flaws (e.g., giving no efficiency
advantage for an insulated tank bottom),
manufacturers are generally not willing
to incorporate enhanced efficiency
features because product costs are likely
to rise without improving the rated
energy efficiency. (NRDC, No. 48 at p.
3; ACEEE, No. 35 at p. 4) DOE
acknowledges that the current test
procedure may not reflect recent
advances in technology. DOE believes,
however, that the test procedure
provides satisfactory methods for
measuring performance of the efficiency
levels considered in this rulemaking.
Furthermore, the design paths that can
be used to achieve the considered
efficiency levels are given appropriate
credit by the test procedure. DOE
believes that the appropriate time to
address the concerns raised is during
the next revision of DOE’s test
procedure.
2. Direct Heating Equipment
The energy conservation standards set
by EPCA for DHE are consistent with
the energy efficiency metric described
in the vented home heating equipment
test procedure. On May 12, 1997, DOE
published a final test procedure rule
(the May 1997 final rule) in the Federal
Register that amended the test
procedures for DHE, particularly for
vented home heating equipment. 62 FR
26140. In this rulemaking, DOE
proposes that this test procedure be
applied to establish the efficiency of
vented gas hearth DHE.
3. Standby Mode and Off Mode Energy
Consumption
EPCA, as amended by EISA 2007
requires DOE to amend the test
procedures for the three types of heating
products to include the standby mode
and off mode energy consumption
measurements. (42 U.S.C.
6295(gg)(2)(B)(v)) Consistent with EISA
2007’s statutory deadline for these
changes, DOE intends to amend its test
procedures to incorporate these
measurements by March 31, 2010. DOE
is handling standby mode and off mode
energy use for the three heating
products in a separate rulemaking.
B. Technological Feasibility
1. General
In each energy conservation standards
rulemaking, DOE conducts a screening
analysis, which it bases on information
it has gathered on all current technology
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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 analysis, DOE develops a
list of design options for consideration
in consultation with manufacturers,
design engineers, and other interested
parties. DOE then determines which of
these means for improving efficiency are
technologically feasible. DOE considers
a design option to be technologically
feasible if it is in use by the relevant
industry or if research has progressed to
the development of a working
prototype. ‘‘Technologies incorporated
in commercial products or in working
prototypes will be considered
technologically feasible.’’ 10 CFR 430,
subpart C, appendix A, section 4(a)(4)(i).
Once DOE has determined that
particular design options are
technologically feasible, it evaluates
each design option in light of the
following additional screening criteria:
(1) Practicability to manufacture, install,
or service; (2) adverse impacts on
product utility or availability; and (3)
adverse impacts on health or safety.
Section IV.B of this notice discusses the
results of the screening analysis for the
three types of heating products,
particularly the designs DOE
considered, those it screened out, and
those that are the basis for the efficiency
levels in this rulemaking. For further
details on the screening analysis for this
rulemaking, see chapter 4 of the NOPR
TSD.
2. Maximum Technologically Feasible
Levels
When DOE proposes to adopt (or not
adopt) an amended or new energy
conservation 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, DOE
determined the maximum
technologically feasible (‘‘max-tech’’)
efficiency levels for the three heating
products in the engineering analysis
using the most efficient design
parameters that lead to the creation of
the highest product efficiencies
possible. (See chapter 5 of the NOPR
TSD.)
The max-tech efficiency levels are set
forth in TSL 7 for residential water
heaters, TSL 6 for DHE, and TSL 6 for
pool heaters. For the representative
rated storage volumes and input
capacity ratings within a given product
class, products with these efficiency
levels were or are now being offered for
sale, or there is a prototype that has
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been tested and developed. No products
at higher efficiency levels are currently
available. Table III.1 lists the max-tech
efficiency levels that DOE determined
for this rulemaking.
TABLE III.1—MAX-TECH EFFICIENCY LEVELS FOR THE RESIDENTIAL HEATING PRODUCTS RULEMAKING
Product class
Representative product
Max-tech efficiency level
Residential water heaters
Gas-Fired Storage Water Heater .....................................
Electric Storage Water Heater .........................................
Oil-Fired Storage Water Heater .......................................
Gas-Fired Instantaneous Water Heater ...........................
Rated Storage Volume
Rated Storage Volume
Rated Storage Volume
Rated Storage Volume
ity = 199,999 Btu/h.
=
=
=
=
40 Gallons ..............................
50 Gallons ..............................
32 Gallons ..............................
0 Gallons, Rated Input Capac-
EF
EF
EF
EF
=
=
=
=
0.80
2.2
0.68
0.95
Direct heating equipment
Gas Wall Fan Type ..........................................................
Gas Wall Gravity Type .....................................................
Gas Floor Type ................................................................
Gas Room Type ...............................................................
Gas Hearth Type ..............................................................
Rated Input Capacity = Over 42,000 Btu/h .....................
Rated Input Capacity = Over 27,000 Btu/h and up to
46,000 Btu/h.
Rated Input Capacity = Over 37,000 Btu/h .....................
Rated Input Capacity = Over 27,000 Btu/h and up to
46,000 Btu/h.
Rated Input Capacity = Over 27,000 Btu/h and up to
46,000 Btu/h.
AFUE = 80%
AFUE = 72%
AFUE = 58%
AFUE = 83%
AFUE = 93%
Pool heaters
Gas Fired ..........................................................................
See section IV.C.3 for additional
details of the max-tech efficiency levels
and discussion of related comments
from interested parties on the
preliminary analysis. In this NOPR,
DOE again seeks public comment on the
max-tech efficiency levels identified for
its analyses. Specifically, DOE requests
information about whether the
efficiency levels identified by DOE
would be achievable using the
technologies screened-in during the
screening analysis (see section IV.B),
especially for gas-fired storage water
heaters, and whether even higher
efficiencies would be achievable using
screened-in technologies. (See Issue 1
under ‘‘Issues on Which DOE Seeks
Comment’’ in section VII.E of this
NOPR.)
C. Energy Savings
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1. Determination of Savings
DOE used its NIA spreadsheet to
estimate energy savings expected to
result from amended energy
conservation standards for products that
would be covered under today’s
proposed rule. (Section IV.F of this
notice and chapter 10 of the NOPR TSD
describe the NIA spreadsheet model.)
For each TSL, DOE forecasted energy
savings over the period of analysis
(beginning in 2013 (DHE, pool heaters)
or 2015 (water heaters), the year that
compliance with the amended standards
would be required, and ending 30 years
later) relative to the base case. (The base
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Rated Input Capacity = 250,000 Btu/h ............................
case represents the forecast of energy
consumption in the absence of amended
energy conservation standards.) Stated
another way, DOE quantified the energy
savings attributable to potential
amended energy conservation standards
as the difference in energy consumption
between the standards case and the base
case.
The NIA spreadsheet model calculates
the energy savings in site energy, which
is the energy directly consumed on
location by an individual product. DOE
reports national energy savings on an
annual basis in terms of the aggregated
source (primary) energy savings, which
are the energy savings used to generate
and transmit the energy consumed at
the site. To convert site energy to source
energy, DOE derived conversion factors,
which change with time, from the
Energy Information Agency’s (EIA)
Annual Energy Outlook 2009
(AEO2009).
For results of DOE’s National Energy
Savings (NES) analysis, see section
V.B.3 of this notice or chapter 10 of the
NOPR TSD.
2. Significance of Savings
As noted above, under 42 U.S.C.
6295(o)(3)(B), DOE is prohibited from
adopting a standard for a covered
product if such standard would not
result in ‘‘significant’’ energy savings.
While the term ‘‘significant’’ is not
defined in the Act, the U.S. Court of
Appeals for the District of Columbia
Circuit, in Natural Resources Defense
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Thermal Efficiency = 95%
Council v. Herrington, 768 F.2d 1355,
1373 (D.C. Cir. 1985), indicated that
Congress intended ‘‘significant’’ energy
savings in this context to be savings that
were not ‘‘genuinely trivial.’’ The energy
savings for all of the TSLs considered in
this rulemaking are nontrivial, and,
therefore, DOE considers them
‘‘significant’’ within the meaning of
section 325 of the EPCA.
D. Economic Justification
1. Specific Criteria
As noted in section II.B., 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)) The
following sections discuss how DOE has
addressed each of those seven factors in
this rulemaking.
a. Economic Impact on Manufacturers
and Consumers
EPCA requires DOE to consider the
economic impact on manufacturers and
consumers of products when
determining the economic justification
of a standard. (42 U.S.C.
6295(o)(2)(B)(i)(I)) In determining the
impacts of an amended standard on
manufacturers, DOE first determines the
quantitative impacts using an annual
cash-flow approach. This includes both
a short-term assessment—based on the
cost and capital requirements during the
period between the announcement of a
regulation and when the regulation
comes into effect—and a long-term
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assessment over the 30-year analysis
period. The impacts analyzed include
INPV (which values the industry on the
basis of expected future cash flows),
annual cash flows, changes in revenue
and income, and other measures of
impact, as appropriate. DOE analyzes
and reports the impacts on different
types of manufacturers, paying
particular attention to impacts on small
manufacturers. DOE also considers the
impact of standards on domestic
manufacturer employment and
manufacturing capacity, as well as the
potential for plant closures and loss of
capital investment. Finally, DOE
accounts for cumulative impacts of
different DOE regulations and other
regulatory requirements on
manufacturers.
For consumers, measures of economic
impact include the changes in LCC and
PBP for each TSL. The LCC, which is
also separately specified as one of the
seven factors to be considered in
determining the economic justification
for a new or amended standard (42
U.S.C. 6295(o)(2)(B)(i)(II)), is discussed
in the following section.
For the results of DOE’s analysis of
the economic impacts of potential
standards on manufacturers and
consumers, see section V.B of this
notice and chapters 8 and 12 of the
NOPR TSD.
b. Life-Cycle Costs
The LCC is the sum of the purchase
price of a product (including associated
installation costs) and the operating
expense (including energy,
maintenance, and repair expenditures)
discounted over the lifetime of the
product. In this rulemaking, DOE
calculated both LCC and LCC savings
for various efficiency levels for each
product. The LCC analysis estimated the
LCC for representative heating products
in housing units that represent the
segment of the U.S. housing stock that
uses these appliances. Through the use
of a housing stock sample, DOE
determined for each household in the
sample the energy consumption of the
heating product and the appropriate
energy prices. By using a representative
sample of households, the analysis
captured the wide variability in energy
consumption and energy prices
associated with heating product use. For
each household, DOE sampled the
values of several inputs to the LCC
calculation from probability
distributions. For purposes of the
analysis, DOE assumes that the
consumer purchases the product in the
year the standard becomes effective.
DOE presents the LCC savings as a
distribution, with a mean value and a
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range across the sample for each
product. This approach permits DOE to
identify the percentage of consumers
achieving LCC savings or attaining
certain payback values due to an
amended energy conservation standard,
in addition to the average LCC savings
or average payback for that standard.
For the results of DOE’s LCC and PBP
analyses, see section V.B.1.a of this
notice and chapter 8 of the NOPR TSD.
c. Energy Savings
While significant conservation of
energy is a separate statutory
requirement for adopting an energy
conservation standard, the Act 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 used the NES spreadsheet results
in its consideration of total projected
savings.
For the results of DOE’s energy
savings analyses, see section V.B.3.a of
this notice and chapter 10 of the NOPR
TSD.
d. Lessening of Utility or Performance of
Products
In establishing product classes and
evaluating their potential for improved
energy efficiency, DOE sought to
develop potential standards for the three
types of heating products that would not
lessen the utility or performance of
these products. During the screening
analysis, DOE tentatively concluded
that the efficiency levels being
considered would not necessitate
changes in product design that would
reduce utility or performance of the
three types of heating products that are
the subject of this rulemaking.
Therefore, none of the TSLs presented
in today’s NOPR would reduce the
utility or performance of the products
under consideration. (42 U.S.C.
6295(o)(2)(B)(i)(IV))
For the results of DOE’s analyses
related to the impact of potential
standards on product utility and
performance, see section IV.B of this
notice and chapter 4 of the NOPR TSD,
the screening analysis.
e. Impact of Any Lessening of
Competition
EPCA directs DOE to consider any
lessening of competition likely to result
from standards. It directs the 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, not later than 60 days after
the publication of a proposed rule,
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together with an analysis of the nature
and extent of such impact. (42 U.S.C.
6295(o)(2)(B)(i)(V) and (B)(ii)) DOE has
transmitted a copy of today’s proposed
rule to the Attorney General and has
requested that the U.S. Department of
Justice (DOJ) provide its determination
on this issue. DOE will publish and
address the Attorney General’s
determination in the final rule.
f. Need of the Nation To Conserve
Energy
EPCA directs DOE to consider the
need for national energy and water
conservation as part of its standardsetting process. (42 U.S.C.
6295(o)(2)(B)(i)(VI)) DOE has
preliminarily determined that the nonmonetary benefits of the proposed
standards would likely be reflected in
improvements to the security and
reliability of the Nation’s energy system.
Reductions in the demand for electricity
may result in reduced costs for
maintaining reliability of the Nation’s
electricity system. DOE conducts a
utility impact analysis to estimate how
standards may affect the Nation’s power
generation capacity requirements.
Energy savings from the proposed
standards would also be likely to result
in environmental benefits in the form of
reduced emissions of air pollutants and
greenhouse gases associated with energy
production, and through reduced use of
fossil fuels at the homes where heating
products are used. Although presented
in summary form in section IV.K, DOE
reports the environmental effects from
the proposed standards and all of the
considered TSLs in the environmental
assessment contained in chapter 15 of
the NOPR TSD. DOE also reports
estimates of the economic value of
emissions reductions resulting from the
considered TSLs.
g. Other Factors
The Act allows the Secretary of
Energy, in determining whether a
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)) Under this
provision, DOE considered LCC impacts
on identifiable groups of consumers,
such as seniors and residents of multifamily housing, who may be
disproportionately affected by any
national energy conservation standard
level. In addition, DOE considered the
uncertainties associated with the heat
pump water heater market related to the
ability of manufacturers to ramp up
production of heat pump water heaters
to serve the U.S. market, the ability of
heat pump component manufacturers to
increase production to serve the water
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heater market, and the ability to retrain
enough servicers and installers of water
heaters to serve the market. See section
V.C.1 for an additional discussion of the
uncertainties in the heat pump water
heater market.
For the results of DOE’s LCC subgroup
analysis, see section IV.G of this notice
and chapter 11 of the NOPR TSD. For
a full discussion of the uncertainties
related to heat pump water heaters, see
sections V.C.1 and IV.B.3 of this notice.
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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
standard level 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. The
LCC and PBP analyses generate values
that calculate the payback period for
consumers of potential amended energy
conservation standards. These analyses
include, but are not limited to, the 3year 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). The rebuttable
presumption payback calculation is
discussed in section IV.D of this NOPR
and chapter 8 of the NOPR TSD.
IV. Methodology and Discussion
In November 2006, DOE published a
notice of public meeting and availability
of the framework document. 71 FR
67825 (Nov. 24, 2006). DOE initially
presented its proposed methodology for
the analyses pertaining to the heating
products rulemaking in the framework
document. After receiving comments
from interested parties on the
approaches proposed in the framework
document, DOE modified its
methodology and assumptions, and
performed a preliminary analysis for
heating products. Subsequently, DOE
published a notice of public meeting on
January 13, 2009. 74 FR 1643. In the
Executive Summary of that notice and
preliminary TSD which accompanied it,
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DOE detailed its preliminary analysis
conducted for the heating products
rulemaking, including methodology,
assumptions, and results. After
receiving further comment from
interested parties on the analytical
approach and results of the preliminary
analysis, DOE further refined its
analyses for today’s NOPR.
DOE used two spreadsheet tools to
estimate the impact of today’s proposed
standards. The first spreadsheet
calculates LCCs and PBPs of potential
new energy conservation standards. The
second provides shipments forecasts
and then calculates national energy
savings and net present value impacts of
potential new energy conservation
standards. DOE also assessed
manufacturer impacts, largely through
use of the Government Regulatory
Impact Model (GRIM). These
spreadsheets are available online at:
https://www1.eere.energy.gov/buildings/
appliance_standards/residential/
waterheaters.html.
Additionally, DOE estimated the
impacts on utilities and the
environment of potential energy
efficiency standards for the three
heating products. DOE used a version of
EIA’s National Energy Modeling System
(NEMS) for the utility and
environmental analyses. The NEMS
model simulates the energy sector of the
U.S. economy. EIA uses NEMS to
prepare its AEO, a widely-known energy
forecast for the United States. The EIA
approves the use of the name NEMS to
describe only an AEO version of the
model without any modification to code
or data. For more information on NEMS,
refer to The National Energy Modeling
System: An Overview 1998. DOE/EIA–
0581 (98) (Feb. 1998) (available at:
https://tonto.eia.doe.gov/FTPROOT/
forecasting/058198.pdf).
The version of NEMS used for
appliance standards analysis is called
NEMS–BT. Because the present analysis
entails some minor code modifications
and runs the model under various
policy scenarios that deviate from AEO
assumptions, the name ‘‘NEMS–BT’’
refers to the model as used here. (‘‘BT’’
stands for DOE’s Building Technologies
Program.) NEMS–BT offers a
sophisticated picture of the effect of
standards because it accounts for the
interactions between the various energy
supply and demand sectors and the
economy as a whole.
A. Market and Technology Assessment
1. Consideration of Products for
Inclusion in This Rulemaking
In this subsection, DOE is presenting
its determination of scope and coverage
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for the rulemaking. Specifically, this
subsection addresses whether EPCA
covers certain products and provides
DOE with the authority to adopt
standards for those products. Second, it
addresses certain types of heating
products that are covered under EPCA,
but for which DOE is not proposing
amended standards at this time, due to
other relevant statutory provisions,
technological limitations, or other
considerations.
a. Determination of Coverage Under the
Act
i. Solar-Powered Water Heaters and Pool
Heaters
As indicated above, EPCA directs
DOE to determine whether to amend the
energy conservation standards that the
Act prescribes for residential water
heaters and pool heaters. (42 U.S.C.
6295(e)(4)) Under EPCA, any standard
for residential water heaters and pool
heaters must establish either a
maximum amount of energy use or a
minimum level of efficiency that is
based on energy use (42 U.S.C. 6291(5)–
(6)). EPCA defines ‘‘energy use,’’ in part,
as ‘‘the quantity of energy’’ that the
product consumes. (42 U.S.C. 6291(4))
Further, EPCA covers these two
products as consumer products. (42
U.S.C. 6291(2); 6292(a)(4), (9), and (11))
EPCA defines ‘‘consumer product,’’ in
part, as an article that consumes or is
designed to consume energy. (42 U.S.C.
6291(1)) EPCA defines ‘‘energy’’ as
meaning ‘‘electricity, or fossil fuels,’’ or
other fuels that DOE adds to the
definition, by rule, upon determining
‘‘that such inclusion is necessary or
appropriate to carry out the purposes’’
of EPCA. (42 U.S.C. 6291(3)) DOE does
not have statutory authority to add solar
energy (or any other type of fuel) to
EPCA’s definition of ‘‘energy.’’ Thus,
DOE presently lacks authority to
prescribe standards for these products
when they use the sun’s energy instead
of fossil fuels or electricity because
EPCA currently covers only water
heaters and pool heaters that use
electricity or fossil fuels, and because
any ‘‘energy conservation standard’’
currently adopted under EPCA for these
two products must address or be based
on the quantity of these fuels, but not
solar power, that the product consumes.
As to water heaters, DOE lacks authority
to adopt standards for solar-powered
products for an additional reason.
‘‘Water heater’’ under EPCA currently
means ‘‘a product which utilizes oil,
gas, or electricity to heat potable water,’’
thereby excluding solar water heaters
from coverage. (42 U.S.C. 6291(27); 10
CFR 430.2)
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ii. Add-On Heat Pump Water Heaters
EPCA defines a residential ‘‘water
heater,’’ in part, as a product that
‘‘heat[s] potable water for use outside
the heater upon demand, including
* * * heat pump type units * * *
which are products designed to transfer
thermal energy from one temperature
level to a higher temperature level for
the purpose of heating water, including
all ancillary equipment such as fans,
storage tanks, pumps, or controls
necessary for the device to perform its
function.’’ (42 U.S.C. 6291(27); 10 CFR
430.2) Integral heat pump water heaters
are fully functioning water heaters when
shipped by the manufacturer. They heat
water for use outside the appliance
upon demand and include in a single
packaged product all of the components
required for operation as a water heater.
Therefore, integral units meet EPCA’s
definition of a ‘‘water heater.’’
Another product sold for residential
use is commonly known as an add-on
heat pump water heater. This product
typically is marketed and used as an
add-on component to a separately
manufactured, fully functioning storage
water heater (usually a conventional
electric storage-type unit). The add-on
unit consists of a small pump and a heat
pump system. The pump circulates the
refrigerant from the water heater storage
tank through the heat pump system and
back into the tank. The add-on heat
pump extracts heat from the
surrounding air and transfers it to the
water in a process that is much more
efficient than traditional electric
resistance designs. The unit can be
mounted on top of the storage tank, or
can be separately placed on the floor or
mounted on a wall. Add-on units cannot
by themselves provide hot water on
demand, but rather heat water only after
being added to a storage-type water
heater. Manufacturers do not ship the
product as a fully-functioning water
heating unit or paired with a storage
tank. The add-on device, by itself, is not
capable of heating water and lacks much
of the equipment necessary to operate as
a water heater. As such, it does not meet
EPCA’s definition of a ‘‘water heater’’
and currently is not a covered product.
Consequently, DOE is not proposing in
this rulemaking to adopt energy
conservation standards for such add-on
heat pump units.
iii. Gas-Fired Instantaneous Water
Heaters With Inputs Above and Below
the Levels Specified in Existing
Definitions
Another element of EPCA’s definition
of a residential ‘‘water heater’’ is that it
includes ‘‘instantaneous type units
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which heat water but contain no more
than one gallon of water per 4,000 Btu
[British thermal units (Btu)] per hour of
input, including gas instantaneous
water heaters with an input of 200,000
Btu per hour or less * * *.’’ (42 U.S.C.
6291(27)(B); 10 CFR 430.2) DOE’s test
procedure for residential water heaters
implements and elaborates on this
definition: ‘‘Gas Instantaneous Water
Heater means a water heater that * * *
has an input greater than 50,000 Btu/hr
(53 MJ/h) but less than 200,000 Btu/h
(210 MJ/h) * * *.’’ 10 CFR part 430,
subpart B, appendix E, section 1.7.2.
During the preliminary analysis and as
today’s NOPR was developed, DOE
considered whether to evaluate for
standards gas-fired instantaneous water
heaters with inputs greater than 200,000
Btu/h and less than 50,000 Btu/h.
DOE’s review of product literature
from manufacturers of gas-fired
instantaneous water heaters indicates
that the majority of such products rated
for residential, whole-house use has an
input capacity of 199,000 Btu/h, and,
thus, are covered by this rulemaking.
Given the limitations set by Congress,
residential gas-fired instantaneous water
heaters with inputs greater than 200,000
Btu/h do not meet EPCA’s definition of
a ‘‘water heater.’’ Consequently, DOE is
not proposing in this rulemaking to
adopt energy conservation standards for
such products.
Regarding the lower end of the range,
DOE reviewed Air-Conditioning,
Heating, and Refrigeration Institute’s
(AHRI) 3 Consumers’ Directory of
Certified Efficiency Ratings for Heating
and Water Heating Equipment and
manufacturer literature to determine the
input capacities of products currently
being offered for sale on the U.S.
market. DOE found that the Directory
contains only one gas-fired
instantaneous water heater with an
input capacity less than 50,000 Btu/h.
Moreover, DOE determined that this
product has been discontinued and is
being replaced by a comparable product
that has an input capacity greater than
50,000 Btu/h. Therefore, DOE is not
proposing standards for products with
an input capacity below 50,000 Btu/h.
3 The Air-Conditioning, Heating, and
Refrigeration Institute (AHRI) is the trade
association that represents manufacturers of heating
products. It was formed on January 1, 2008, by the
merger of the Gas Appliance Manufacturers
Association (GAMA), which formerly represented
these manufacturers, and the Air-Conditioning and
Refrigeration Institute. AHRI maintains a
Consumers’ Directory of Certified Product
Performance for water heaters, direct heating
equipment, and pool heaters which can be found on
AHRI’s Web site at https://www.ahridirectory.org/
ahridirectory/pages/home.aspx.
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iv. Input Capacity for Residential Pool
Heaters and Coverage of Spa Heaters
Under EPCA, ‘‘pool heater’’ is defined
as ‘‘an appliance designed for heating
nonpotable water contained at
atmospheric pressure, including heating
water in swimming pools, spas, hot tubs
and similar applications.’’ (42 U.S.C.
6291(25); 10 CFR 430.2) During a
preliminary phase of this rulemaking,
DOE considered excluding from
consideration pool heaters with an
input capacity greater than 1 million
Btu/h, based on its understanding that
manufacturers market such pool heaters
as light industrial or commercial
products. Subsequently, two
manufacturers advised DOE that the
industry defines residential pool heaters
as having an input capacity of less than
or equal to 400,000 Btu/h. These
comments suggested that DOE should
use this capacity limit in its definition
of residential pool heaters and for
determining the scope of coverage of
this product under EPCA.
As indicated by its definition of ‘‘pool
heater,’’ quoted above, EPCA places no
capacity limit on the pool heaters it
covers. (42 U.S.C. 6291(25))
Furthermore, EPCA covers pool heaters
as a ‘‘consumer product,’’ (42 U.S.C.
6291(2), 6292(a)(11)) and defines
‘‘consumer product,’’ in part, as an
article that ‘‘to any significant extent, is
distributed in commerce for personal
use or consumption by individuals.’’ (42
U.S.C. 6291(1)) These provisions
establish that EPCA, and standards
adopted under it, apply to any pool
heater distributed to any significant
extent as a consumer product for
residential use, regardless of input
capacity; pool heaters marketed as
commercial equipment, which contain
additional design modifications related
to safety requirements for installation in
commercial buildings, are not covered
by this standard. Therefore, DOE has
tentatively concluded that an input
capacity limit is neither necessary nor
appropriate to determine the scope of
coverage of this product under EPCA.
Regarding whether spa heaters, which
heat the water in spas, are covered
products, DOE notes that EPCA defines
a ‘‘pool heater’’ to include appliances
‘‘designed for * * * heating water in
* * * spas.’’ (42 U.S.C. 6291(25); 10
CFR 430.2) As the definition
encompasses spa heaters, they are
covered by EPCA as well as by the
current standards for pool heaters, and
DOE has included them in this
rulemaking. Because spa heaters and
pool heaters perform similar functions,
include similar features, and lack
performance or operating features that
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would cause them to have inherently
different energy efficiencies, DOE has
not created a separate product class for
such units.
v. Vented Hearth Products
As discussed in section II.C.2 above,
before the enactment of NAECA, EPCA
included ‘‘home heating equipment’’ in
DOE’s appliance standards program.
EPCA did not define ‘‘home heating
equipment.’’ NAECA’s amendments to
EPCA included replacing the term
‘‘home heating equipment’’ with ‘‘direct
heating equipment,’’ and specified
energy conservation standards for
‘‘direct heating equipment.’’ However,
EPCA did not define this term, and
subsequent legislation has not amended
EPCA to provide a definition of ‘‘direct
heating equipment.’’
DOE defined ‘‘home heating
equipment’’ and related terms in its
regulations. These definitions inform
the meaning of ‘‘direct heating
equipment.’’ 10 CFR 430.2. Specifically,
DOE defines ‘‘home heating equipment’’
as meaning ‘‘vented home heating
equipment and unvented home heating
equipment,’’ and defines each of these
two terms. Id. The definition of ‘‘vented
home heating equipment,’’ relevant
here, is as follows:
* * * a class of home heating equipment, not
including furnaces, designed to furnish
warmed air to the living space of a residence,
directly from the device, without duct
connections (except that boots not to exceed
10 inches beyond the casing may be
permitted) and includes: vented wall furnace,
vented floor furnace, and vented room
heater.’’ Id.
DOE also defines the last three terms in
this definition. Id. In order to provide
additional clarity for interested parties,
DOE is proposing to define the term
‘‘direct heating equipment’’ in today’s
rulemaking. Specifically, DOE is
proposing to add the following
definition in 10 CFR 430.2:
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Direct heating equipment means vented
home heating equipment and unvented home
heating equipment.
Given that background, the following
addresses the issue of vented hearth
products.
Vented hearth products include gasfired products such as fireplaces,
fireplace inserts, stoves, and log sets
that typically include aesthetic features
such as a yellow flame. Consumers
typically purchase these products to add
aesthetic qualities and ambiance to a
room, and the products also provide
space heating. They provide such
heating by furnishing warmed air to the
living space of a residence directly from
the device without duct connections.
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There are two types of vented hearth
product designs: (1) Recessed and (2)
non-recessed. Recessed products are
typically incorporated into or attached
to a wall, whereas non-recessed
products are typically free-standing and
not attached to a wall. Both may include
fireplace or hearth aesthetics, and the
recessed product may include a
surrounding mantle.
Vented hearth products meet DOE’s
definition of ‘‘vented home heating
equipment,’’ because they are designed
to furnish warmed air to the living space
of a residence without duct connections.
Furthermore, recessed and non-recessed
vented hearth products are similar in
design to some of the direct heating
products for which EPCA prescribes
standards, namely gas wall fan and
gravity-type furnaces in the case of
recessed products, and room heaters in
the case of non-recessed products.
In sum, DOE has tentatively
concluded that vented hearth products
are covered products under EPCA,
because they meet DOE’s definition for
‘‘vented home heating equipment’’ and,
therefore, are classified as DHE. Thus,
DOE proposes to establish standards for
these products in this rulemaking and
subject these products to the existing
testing and certification provisions for
DHE. See section IV.2 and IV.3, below,
for additional discussion on DOE’s
proposal for establishing coverage of
hearth products and the product classes
for the rulemaking analyses. If DOE
finalizes this rulemaking as proposed
for hearth type DHE, manufacturers of
these products would be subject to the
provisions in 10 CFR parts 430.23,
430.24, 430.27, 430.32, 430.33, 430.40
through 430.49, 430.50 through 430.57,
430.60 through 430.65, and 430.70
through 430.75, which currently apply
to DHE. DOE seeks comment on the
potential burdens to manufacturers of
hearth-type DHE as a result of the
testing, certification, reporting, and
enforcement provisions in these
sections. (See Issue 2 under ‘‘Issues on
Which DOE Seeks Comment’’ in section
VII.E of this NOPR.)
been amended, and they are codified in
10 CFR part 430, subpart B, appendices
G and O, respectively. The new energy
conservation standards for this
equipment in NAECA’s amendments to
EPCA in 1987 were only for gas
products, however, and used the AFUE
descriptor, which applies to vented but
not unvented equipment. (42 U.S.C.
6295(e)(3)) The AFUE descriptor is
generally a measure of the amount of
heat provided by the product compared
to the amount of fuel supplied.
Subsequent DOE actions concerning
DHE—first in a NOPR proposing
standards for eight separate products, 59
FR 10464 (March 4, 1994), and then in
a final rule adopting test procedure
amendments for DHE, 62 FR 26140
(May 12, 1997)—have focused solely on
vented products. This approach reflects
DOE’s understanding that because
unvented heating products dissipate any
heat losses directly into the conditioned
space rather than elsewhere through a
vent, the amount of energy losses from
these products is minimal.
The current test procedure for
unvented equipment includes neither a
method for measuring energy efficiency
nor a descriptor for representing the
efficiency of unvented home heating
equipment. Instead, the current test
procedure focuses on a method to
measure and calculate the annual
energy consumption of unvented
equipment.10 CFR part 430, subpart B,
appendix G. Nevertheless, it remains the
case that the unvented products in
question would dissipate any heat
losses directly into the conditioned
space, thereby resulting in minimal
overall energy losses. Thus, DOE sees
little benefit from setting a minimum
efficiency level for these products and
believes that it would be unnecessary to
do so, given the extremely limited
energy savings that could be achieved
by such a standard. For these reasons,
and consistent with previous
rulemakings in which it has addressed
DHE, DOE has not evaluated unvented
products in this rulemaking and is not
proposing standards for them at this
time.
b. Covered Products Not Included in
This Rulemaking
ii. Electric Pool Heaters
EPCA’s definition of ‘‘pool heater,’’
quoted above, is not limited to
appliances that use a particular type or
types of fuel. (42 U.S.C. 6291(25); 10
CFR 430.2) Thus, EPCA covers both gasfired pool heaters and electric pool
heaters, including heat pump pool
heaters. EPCA also specifies that the
energy efficiency descriptor for
residential pool heaters is thermal
efficiency. (42 U.S.C. 6291(22)(E)).
Lastly, EPCA defines the term ‘‘thermal
i. Unvented Direct Heating Equipment
(Including Electric Equivalents to GasFired Products)
When EPCA included ‘‘home heating
equipment’’ as a covered product, DOE
construed this term as including
unvented as well as vented products,
and prescribed a separate test procedure
for each one. 43 FR 20128 (May 10,
1978); 43 FR 20147 (May 10, 1978).
Each of these test procedures has since
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efficiency of pool heaters’’ as ‘‘a
measure of the heat in the water
delivered at the heater outlet divided by
the heat input of the pool heater as
measured under test conditions
specified in section 2.8.1 of the
American National Standard for Gas
Fired Pool Heaters, Z21.56–1986, or as
may be prescribed by the Secretary.’’ (42
U.S.C. 6291(26))
Currently, DOE’s test procedures
specify only a method for testing gasfired pool heaters (10 CFR part 430,
subpart B, appendix P), and the current
energy conservation standard for pool
heaters is a minimum level of thermal
efficiency that applies only to gas-fired
products. In order for DOE to consider
an energy conservation standard for
electric pool heaters, DOE would first
need to establish a test procedure for
electric pool heaters using the thermal
efficiency metric required by EPCA.
DOE seeks comments from interested
parties on how DOE could address
EPCA’s efficiency descriptor
requirements in a future potential test
procedure revision for electric pool
heaters. For this reason, DOE is
proposing amended standards for gasfired pool heaters only and is not
considering standards for electric pool
heaters. This is identified as Issue 3 in
Section VII.E, ‘‘Issues on Which DOE
Seeks Comment.’’
iii. Tabletop and Electric Instantaneous
Water Heaters
Standards are currently applicable to
tabletop and electric instantaneous
water heaters. (10 CFR 430.32(d)) These
products meet EPCA’s definition of
‘‘water heater’’ (42 U.S.C. 6291(27); 10
CFR 430.2) and are covered by the Act
because they utilize electricity to heat
potable water for use outside the heater
upon demand. However, for the reasons
explained below, DOE has not analyzed
tabletop water heaters and electric
instantaneous water heaters in this
rulemaking, and is not proposing
amended standards for them, because of
the limited potential for energy savings
from higher standards for these
products.
Tabletop products are primarily
electric and are relatively small units
because they are designed to be located
underneath tabletops in highly
specialized applications. The only
means of which DOE is aware for
manufacturers to increase the energy
efficiency of tabletop units is to increase
the thickness of their insulation, which
would make them larger. Manufacturers
already maximize the size of these water
heaters in order to meet the currently
required minimum energy factors, and
size restrictions do not allow the units
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to be any larger. Thus, DOE is unaware
of any means to make tabletop water
heaters more energy efficient. Put
another way, if DOE were to adopt a
higher efficiency standard for this
product, it would force this class of
covered product off the market, in
violation of 42 U.S.C. 6295(o)(4). For
these reasons, DOE has not evaluated
tabletop products in this rulemaking
and is not proposing standards for them.
Regarding electric instantaneous
water heaters, DOE notes that the energy
efficiency metric for electric
instantaneous water heaters (and all
other water heaters) is a combination of
recovery efficiency and standby losses.
All electric water heaters, including
instantaneous products, have minor
losses in recovery efficiency. Moreover,
electric instantaneous water heaters
have negligible standby losses because
they store no more than two gallons of
hot water. In addition, many of the
electric instantaneous products
currently on the market perform well
above the existing applicable energy
conservation standard and use available
technologies to produce negligible
standby losses. Therefore, DOE has not
evaluated electric instantaneous water
heaters in this rulemaking and is not
proposing standards for them.
iv. Combination Water Heating/Space
Heating Products
EPCA authorizes DOE to set more
than one standard for any product that
performs more than one major function
by setting one energy conservation
standard for each major function. (42
U.S.C. 6295(o)(5)) Some products on the
market provide both water heating and
space heating. To the extent such
combination products meet EPCA’s
criteria for coverage, DOE could set
standards for them, including a separate
standard for each of those functions. Id.
However, because DOE’s current test
procedure cannot handle combination
appliances and DOE has not yet adopted
a test procedure to determine the energy
efficiency of these combination
appliances, DOE has not evaluated them
in this rulemaking and is not proposing
standards for them.
2. Definition of Gas Hearth Direct
Heating Equipment
In the preliminary analysis, DOE
stated that vented hearth products can
be used to provide residential space
heating. When used to furnish heat to a
living space, DOE reasoned that these
products provide the same function and
utility as vented heaters. DOE stated in
the preliminary analysis that hearth
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heaters also provide the same utility and
function as gas wall furnaces or gas
room heaters, and do not use any
unique technologies. See chapter 2 of
the preliminary TSD. Additionally,
AHRI’s Consumers’ Directory
categorizes fireplace heaters as either
room heaters or wall furnaces. DOE
treated gas hearth DHE as either a room
heater or a wall furnace for the purposes
of the preliminary analysis and
requested comment in the Executive
Summary to the preliminary TSD on the
need for a separate product definition
and class for gas hearth DHE.
AHRI stated that gas-fired hearth
heaters need a unique definition but
that they can be included within the
room heater DHE product class. AHRI
further stated that DOE should use the
safety standard in the American
National Standards Institute (ANSI)
Standard Z.21–88, Vented Fireplace
Heaters as a reference for developing a
fireplace heater definition. (AHRI,
Public Meeting Transcript, No. 34.4 at p.
36)
DOE agrees with AHRI and has
decided to establish a separate
definition for ‘‘hearth direct heating
equipment’’ to allow manufacturers to
easily determine coverage under DOE’s
regulations. DOE has determined that
hearth DHE should not be included with
room heater DHE (the alternative
suggested by AHRI) due to the unique
constraints on hearth products that are
not applicable to room heaters because
of the former’s aesthetic appeal to
consumers (e.g., glass viewing panes,
yellow flames, and ceramic log sets).
DOE reviewed the ‘‘vented gas fireplace
heater’’ definition in ANSI Standard
Z.21–88, as suggested by AHRI. The
‘‘vented gas fireplace heater’’ definition
in ANSI Standard Z.21–88 reads as
follows:
Vented gas fireplace heater is a vented
appliance which simulates a solid fuel
fireplace and furnishes warm air, with our
without duct connections, to the space in
which it is installed. A vented gas fireplace
heater is such that it may be controlled by
an automatic thermostat. The circulation of
heating room air may be by gravity or
mechanical means. A vented gas fireplace
heater may be freestanding, recessed, zero
clearance, or a gas fireplace insert.
Part of the ‘‘vented gas fireplace
heater’’ definition specified by ANSI
Standard Z.21–88 would conflict with
DOE’s definition of ‘‘home heating
equipment.’’ 10 CFR 430.2. Specifically,
all types of home heating equipment
under DOE’s regulations must function
without duct connections (although
boots not to exceed 10 inches beyond
the casing may be permitted). Therefore,
DOE is modifying the definition of
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‘‘vented gas fireplace heater’’ in ANSI
Standard Z.21–88 to be consistent with
the types of equipment covered under
DOE’s authority for home heating
equipment. Consequently, in order to
account for hearth DHE, DOE is
proposing a definition of ‘‘vented hearth
heater’’ in section 430.2 to read as
follows:
Vented hearth heater means a vented,
freestanding, recessed, zero clearance
fireplace heater, a gas fireplace insert or a
gas-stove, which simulates a solid fuel
fireplace and is designed to furnish warm air,
without ducts to the space in which it is
installed.
DOE seeks comment on its definition for
‘‘vented hearth heater.’’ (See Issue 4
under ‘‘Issues on Which DOE Seeks
Comment’’ in section VII.E of this
NOPR.)
3. Product Classes
In evaluating and establishing energy
conservation standards, DOE generally
divides covered products into classes by
the type of energy used or by capacity
or other performance-related feature that
justifies a different standard for
products having such feature. (See 42
U.S.C. 6295(q)) In deciding whether a
feature justifies a different standard,
DOE must consider factors such as the
utility of the feature to users. Id. DOE
normally establishes different energy
conservation standards for different
product classes based on these criteria.
Table IV.1 presents the product
classes for the three types of heating
products under consideration in this
rulemaking. The subsections below
provide additional details, discussion of
comments relating to the product
classes for the three heating products, as
well as identified issues on which DOE
is seeking comments.
TABLE IV.1—PROPOSED PRODUCT CLASSES FOR THE THREE HEATING PRODUCTS
Residential water heater type
Characteristics
Gas-Fired Storage Type ...........................................................................
Nominal input of 75,000 Btu/h or less; rated storage volume from 20 to
100 gallons.
Nominal input of 105,000 Btu/h or less; rated storage volume of 50 gallons or less.
Nominal input of 12 kW (40,956 Btu/h) or less; rated storage volume
from 20 to 120 gallons.
Nominal input of over 50,000 Btu/h up to 200,000 Btu/h; rated storage
volume of 2 gallons or less.
Oil-Fired Storage Type .............................................................................
Electric Storage Type ...............................................................................
Gas-Fired Instantaneous ..........................................................................
Direct heating equipment type
Heating capacity (Btu/h)
Gas Wall Fan Type ..................................................................................
Gas Wall Gravity Type .............................................................................
Gas Floor ..................................................................................................
Gas Room ................................................................................................
Gas Hearth ...............................................................................................
Pool heater type
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up to 46,000.
up to 27,000.
up to 46,000.
up to 27,000.
up to 46,000.
Characteristics
Residential Pool Heaters ..........................................................................
a. Water Heaters
Residential water heaters can be
divided into various product classes
categorized by physical characteristics
that affect product efficiency. Key
characteristics affecting the energy
efficiency of the residential water heater
are the type of energy used and the
volume of the storage tank.
Up to 42,000.
Over 42,000.
Up to 27,000.
Over 27,000 and
Over 46,000.
Up to 37,000
Over 37,000.
Up to 20,000.
Over 20,000 and
Over 27,000 and
Over 46,000.
Up to 20,000.
Over 20,000 and
Over 27,000 and
Over 46,000.
Gas-fired.
The existing Federal energy
conservation standards for residential
water heaters correspond to the
efficiency levels promulgated by the
January 2001 final rule, as shown in 10
CFR 430.32(d). These product classes
are differentiated by the type of energy
used (i.e., electric, gas, or oil) and the
type of storage for the water heater (i.e.,
storage, tabletop, or instantaneous). In
this rulemaking, DOE has excluded
tabletop water heaters and electric
instantaneous water heaters from
consideration for the reasons discussed
above. Table IV.2 shows the four
product classes presented in the
preliminary analysis for consideration
in today’s rulemaking.
TABLE IV.2—PRODUCT CLASSES FOR RESIDENTIAL WATER HEATERS DESCRIBED IN THE PRELIMINARY ANALYSIS *
Residential water heater type
Characteristics
Gas-Fired Storage Type ...........................................................................
Nominal input of 75,000 Btu/h or less; rated storage volume from 20 to
100 gallons.
Nominal input of 105,000 Btu/h or less; rated storage volume of 50 gallons or less.
Oil-Fired Storage Type .............................................................................
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TABLE IV.2—PRODUCT CLASSES FOR RESIDENTIAL WATER HEATERS DESCRIBED IN THE PRELIMINARY ANALYSIS *—
Continued
Residential water heater type
Characteristics
Electric Storage Type ...............................................................................
Nominal input of 12 kW (40,956 Btu/h) or less; rated storage volume
from 20 to 120 gallons.
Nominal input of over 50,000 Btu/h up to 200,000 Btu/h; rated storage
volume of 2 gallons or less.
Gas-Fired Instantaneous ..........................................................................
* Only the product classes covered by this rulemaking are shown. The table does not include tabletop and instantaneous electric water
heaters.
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In response to the preliminary
analysis, DOE received several
comments from interested parties about
DOE’s potential product classes and
their organization. These comments are
summarized and addressed immediately
below.
i. Gas-Fired and Electric Instantaneous
Water Heaters
EEI suggested that DOE should revisit
the parameters for the input capacity
range for gas-fired and electric
instantaneous water heaters.
Specifically, EEI stated that some gasfired instantaneous water heaters on the
market have an input capacity higher
than 200,000 Btu/h, and some electric
instantaneous water heaters have an
input capacity much higher than 12 kW.
(EEI, No. 40 at p. 2) Northwest Energy
Efficiency Alliance (NEEA) and
Northwest Power and Conservation
Council (NPCC) recommended
combining gas-fired storage and gasfired instantaneous water heaters into
one product class, because this would
simplify the rulemaking, and the
commenters do not believe
manufacturers will reduce the efficiency
of the products they offer now (most of
which have EF ratings above 0.80) in
response. (NEEA and NPCC, No. 42 at
p. 4) SEISCO commented that DOE
should establish a separate product
class and definition for ‘‘electric
instantaneous water heaters’’. SEISCO
recommended creating a definition for
‘‘whole house electric instantaneous
water heaters’’ and amending the
current 12 kilowatt (kW) maximum to a
more reasonable 18 to 36 kW maximum
to more accurately reflect the
marketplace. (SEISCO, No. 41 at p. 1)
In response, DOE notes that EPCA’s
definition of ‘‘water heater,’’ establishes
the input capacity limits for residential
instantaneous water heaters.
Specifically, the term ‘‘water heater’’
means ‘‘a product which utilizes oil,
gas, or electricity to heat potable water
for use outside the heater upon demand,
including * * * (B) instantaneous type
units which heat water but contain no
more than one gallon of water per 4,000
Btu per hour of input, including gas
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instantaneous water heaters with an
input of 200,000 Btu per hour or less,
oil instantaneous water heaters with an
input of 210,000 Btu per hour or less,
and electric instantaneous water heaters
with an input of 12 kilowatts or less
* * *’’ (42 U.S.C. 6291(27)) As noted
above, this statutory definition
demonstrates that residential, gas-fired
instantaneous water heaters with inputs
greater than 200,000 Btu/h and
residential, electric instantaneous water
heaters with inputs greater than 12 kW
do not meet the definitions of a ‘‘water
heater’’ under EPCA. Accordingly,
instantaneous water heaters outside the
specified capacity range are not covered
products under EPCA and are outside
DOE’s authority for standard setting
pursuant to 42 U.S.C. 6295(e)(4). The
input capacity ranges for gas-fired
instantaneous water heaters and electric
instantaneous water heaters are
discussed further in sections IV.A.1.a
and IV.A.1.b, respectively, of today’s
NOPR.
Additionally, DOE disagrees with the
suggestion from NEEA and NPCC that
DOE should combine the gas-fired
storage and gas-fired instantaneous
water heater product classes for this
rulemaking. As noted earlier in this
section, storage capacity is a key
characteristic affecting the energy
efficiency of water heaters, and it is
within DOE’s authority to divide
products into classes based on capacity.
(42 U.S.C. 6295(q)) Thus, DOE is
maintaining separate product classes for
gas-fired storage and gas-fired
instantaneous water heaters for today’s
NOPR.
ii. Low-Boy Water Heaters
AHRI recommended establishing a
separate product class for low-boy
heaters since they must fit under a 36inch counter, be less than 34 inches
high, and have a jacket diameter of less
than 26 inches. AHRI stated that lowboy heaters provide a specific utility to
space-constrained residences and that
these products cannot be made any
larger. Low-boy heaters account for
approximately 18 percent of the
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residential market. (AHRI, No. 43 at p.
3)
DOE does not agree that a separate
product class needs to be established for
low-boy water heaters. In evaluating and
establishing energy conservation
standards, DOE generally divides
covered products into classes by the
type of energy used, or by capacity or
another performance-related feature that
justifies a different standard. (See 42
U.S.C. 6295(q)) DOE notes that low-boy
water heaters use the same type of
energy (i.e., gas or electricity) and are
offered in a range of storage volumes.
Thus, the type of energy used and the
functionality of low-boy units are
similar to other types of water heaters,
and the size constraints of these units
do not appear to impact energy
efficiency, since many ‘‘low-boy’’
models have efficiencies that are
comparable to standard-size water
heaters currently available on the
market.
DOE seeks comment on its product
classes for water heaters. In particular,
DOE is seeking further comment about
the need for a separate product class for
low-boy water heaters. (See Issue 5
under ‘‘Issues on Which DOE Seeks
Comment’’ in section VII.E of this
NOPR.)
iii. Ultra-Low NOX Water Heaters
In the preliminary analysis, DOE did
not distinguish ultra-low NOX gas-fired
storage water heaters from traditional
gas-fired storage water heaters with
standard burners. AHRI recommended
establishing a separate product class.
AHRI argued that these water heaters
employ unique burners, designed to
meet the ultra-low NOX requirements
(imposed by local air quality
management districts to limit NOX
emissions of certain products), but
which limit the manufacturer’s options
to increase efficiency. (AHRI, No. 43 at
p. 2)
Rheem commented that instantaneous
gas-fired water heater ultra-low NOX
requirements from local air quality
management districts will commence in
2012 and that this product design
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should be included in the analysis.
(Rheem, No. 49 at p. 7)
DOE does not agree that a separate
product class needs to be established for
ultra-low NOX gas-fired storage water
heaters. As noted above, in evaluating
and establishing energy conservation
standards, DOE generally divides
covered products into classes by the
type of energy used, or by capacity or
other performance-related feature that
justifies a different standard for
products having such feature. (See 42
U.S.C. 6295(q)) Ultra-low NOX gas-fired
storage water heaters use the same type
of energy (i.e., gas) and are offered in
comparable storage volumes to
traditional gas-fired storage water
heaters using standard burners. In
deciding whether the product
incorporates a performance feature that
justifies a different standard, DOE must
consider factors such as the utility of the
feature to users. Id. In terms of water
heating, DOE believes ultra-low NOX
water heaters provide the same utility to
the consumer. However, DOE also notes
that ultra-low NOX water heaters do
incorporate a specific burner
technology, allowing these units to meet
the strict emissions requirements of
local air quality management districts.
Consequently, DOE developed an
analysis on ultra-low NOX gas-fired
storage water heaters. See section IV.C.2
for additional details. DOE requests
comment from interested parties
regarding the approach to the analysis
for ultra-low NOX gas-fired storage
water heaters. As indicated in section
VII.E under Issue 6, DOE also seeks
further comment about the need for a
separate product class for ultra-low NOX
water heaters.
iv. Gas-Fired and Electric Storage Water
Heaters Product Class Divisions
DOE received two comments about
the product class divisions for gas-fired
and electric storage water heaters.
ACEEE stated that DOE should consider
capacity-based product classes for gasfired and electric storage water heaters.
ACEEE stated that EPCA directs DOE to
divide covered products into product
classes by the type of energy used or by
capacity or other performance-related
features that affect efficiency. (42 U.S.C.
6295(q)) ACEEE also stated that DOE’s
energy efficiency equations demonstrate
that capacity (i.e., rated storage volume)
is one determinant of efficiency.
Accordingly, ACEEE recommended
separating gas-fired and electric storage
water heaters into two product classes,
including ‘‘very large’’ and ‘‘other.’’
(ACEEE, No. 35 at p. 2) ACEEE
expressed its belief that DOE will not
adequately reflect the potential of the
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product classes without considering
larger and smaller products as separate
product classes. (ACEEE, Public
Meeting Transcript, No. 34.4 at
pp. 66–67)
ACEEE suggested that gas-fired
storage water heaters with an input
capacity greater than 65,000 Btu/h and
electric storage water heaters with a
rated storage volume greater than 75
gallons could be in the very large
category. (ACEEE, No. 35 at p. 2) ACEEE
commented that for heat pump water
heaters, impacts such as air flow in
small residences are much different for
a 50-gallon model than a 30-gallon
model. (ACEEE, Public Meeting
Transcript, No. 34.4 at pp. 66–67)
In light of the above, ACEEE
recommended that DOE should propose
energy conservation standards for
electric storage water heater products in
the very large category requiring a
minimum EF of 1.7, which would move
the largest electric water heaters to
utilize heat pump water heater
technologies. ACEEE recommended that
DOE should propose standards for the
very large product class of gas-fired
storage water heaters requiring a
minimum EF of 0.77, which
corresponds to the least-efficient
condensing product. (ACEEE, No. 35 at
p. 1)
Pacific Gas and Electric Company
(PG&E), San Diego Gas and Electric
(SDGE), and Southern California Gas
Company (SoCal Gas) filed a joint
comment and urged DOE to subdivide
gas-fired storage water heaters and
electric storage water heaters into
subclasses based on rated storage
volume. (PG&E, SDGE, and SoCal Gas,
No. 38 at p. 3)
DOE believes considering separate
efficiency levels for different rated
storage volumes could offer a way for
DOE to capture additional potential
energy savings. Instead of dividing gasfired and electric storage water heaters
into separate product classes by rated
storage volume or input capacity as
ACEEE suggested, however, DOE is
using energy efficiency equations that
vary with rated storage volume to
describe the relationship between rated
storage volume and energy factor.
Historically, DOE has used the energy
efficiency equations to account for the
variability in performance resulting
from tank size; these equations consider
the increases in standby losses as tank
volume increases. DOE is using the
energy efficiency equations along with
TSL pairings to consider different
amended standards in the proposed
rule. DOE further discusses the energy
efficiency equations and the proposed
modifications in section IV.C.7. DOE is
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requesting comment from interested
parties on the energy efficiency
equations developed for gas-fired and
electric storage water heaters (See
section IV.C.7 and Issue 7 under ‘‘Issues
on Which DOE Seeks Comment’’ in
section VII.E of this NOPR for more
information.) In addition, DOE further
discusses the trial standard levels,
which are comprised of various
efficiency level pairings across the full
range of rated storage volumes, in
section V.A.
v. Heat Pump Water Heaters
In response to DOE’s treatment of heat
pump water heaters as a design option
for electric storage water heaters in the
preliminary analysis, DOE received
several comments from interested
parties. All of the commenters urged
DOE to establish separate product
classes for traditional electric resistance
storage water heaters and heat pump
water heaters. Their specific comments
and DOE’s response are presented
below.
A.O. Smith stated DOE should
separate the electric storage water heater
product class into two products
classes—one for electric resistance
heaters and one for heat pump water
heaters. A.O. Smith noted that DOE
separated the two classes in the
ENERGY STAR criteria. A.O. Smith
further stated that since heat pump
water heaters may not even fit in 30
percent of the installations that
currently have resistance electric
heaters, they cannot be considered to be
a truly interchangeable technology.
(A.O. Smith, No. 37 at p. 9)
AHRI agreed with some of the
concerns DOE noted in the preliminary
screening analysis for heat pump water
heaters. Specifically, AHRI pointed to
previous DOE studies, which found
size-related installation issues with
replacing an electric storage water
heater with a heat pump water heater.
To AHRI’s knowledge, the heat pump
water heater market has not changed
significantly since DOE’s 2001 water
heater rulemaking, even with the recent
initiation of the ENERGY STAR program
and the enactment of legislation that
provides a significant tax credit for the
installation of these systems. With this
in mind, AHRI recommended that DOE
establish a separate product class for
heat pump water heaters because its
energy source is different than that of an
electric water heater. While a heat pump
water heater does use electricity to
operate certain components, the actual
energy source that heats the water is air.
AHRI noted that an analogous situation
exists for electric furnaces, which are
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not subject to the same standards as heat
pump systems. (AHRI, No. 43 at p. 4)
Rheem also maintains that heat pump
water heaters require a separate product
class. (Rheem, No. 49 at p. 5) Rheem
commented that heat pump water heater
designs require unique installations, air
flow, space, condensate drain, service,
and operational provisions that are
considerably different from
conventional electric storage water
heaters. Rheem also stated that
installation and air flow conditions will
affect energy efficiency, and that heat
pump water heaters cannot replace all
electric storage type water heaters, as
space and air flow constraints are quite
common. Furthermore, Rheem
commented that heat pump water heater
technology depends largely on the
operating environment; this represents a
special performance-related
consideration that warrants defining a
separate product class for heat pump
water heaters. (Rheem, No. 49 at p. 6)
Rheem commented that the utility heat
pump water heaters provide is not
equivalent to other electric storage water
heaters across the entire range of rated
storage volumes. Rheem stated that the
reduced delivery performance was
recognized by ENERGY STAR, which
requires a minimum first-hour rating of
50 gallons, instead of 67 gallons for
common conventional technologies. The
difference in utility will result in
differing sizing guidelines to meet
equivalent capacities. Rheem
commented that while the primary fuel
source for heat pump water heaters is
assumed to be electricity, the
technology attains an economic benefit
by moving energy from one location to
another. According to Rheem, it is
conceivable that a heat pump water
heater may operate and be designed
with gas as a primary back-up fuel.
Rheem noted that with energy factors
exceeding 2.0, it can be argued that
electricity is no longer the dominant
fuel source. Rheem commented that
these differences support the argument
that heat pump water heaters are not
simply an extension of conventional
resistance-type electric storage water
heaters. (Rheem, No. 49 at pp. 5–6)
While DOE acknowledges some of the
challenges associated with heat pump
water heaters, DOE does not agree that
they require a separate product class.
Specifically, DOE does not believe heat
pump water heaters provide a different
utility from traditional electric
resistance water heaters. Heat pump
water heaters provide hot water to a
residence just as a traditional electric
storage water heater. In addition, both
heat pump water heaters and traditional
electric resistance storage water heaters
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use electricity as the primary fuel
source. DOE believes heat pump water
heaters can replace traditional electric
resistance storage water heaters in most
residences, although the installation
requirements may be quite costly. DOE
further addresses heat pump water
heaters in the screening analysis at
section IV.B.3 and the installation
requirements in section IV.E.2.a.
DOE seeks further comment on the
need for a separate product class for
heat pump water heaters. In particular,
DOE is interested in receiving
comments and data on whether a heat
pump water heater can be used as a
direct replacement for an electric
resistance water heater, and the types
and frequency of installations where a
heat pump water heater cannot be used
as a direct replacement for an electric
resistance water heater. (See Issue 8
under ‘‘Issues on Which DOE Seeks
Comment’’ in section VII.E of this
NOPR.)
b. Direct Heating Equipment
DHE can be divided into various
product classes categorized by physical
characteristics and rated input capacity,
both of which affect product efficiency
and function. Key characteristics
affecting the energy efficiency of DHE
are the physical construction (i.e., fan
wall units contain circulation blowers),
intended installation (i.e., floor furnaces
are installed with the majority of the
unit outside of the conditioned space),
and input capacity.
In the preliminary analysis, DOE
examined the possibility of
consolidating product classes for DHE.
(See chapter 3 of the preliminary TSD.)
NAECA originally established the
Federal energy conservation standards,
which are differentiated by input
capacity range. Thus, to determine
whether consolidation of existing
product classes is appropriate, DOE
examined the relationship between
AFUE and input rating for DHE. The
results of this inquiry are presented
below.
i. Gas Wall Fan-Type Direct Heating
Equipment
For fan-type wall furnaces, DOE
surveyed AHRI’s Consumers’ Directory
and available product literature. DOE
identified available products ranging
from 8,000 to 65,000 Btu/h. The market
data demonstrate two separate trends for
fan-type wall furnaces based on the
efficiency range of the products. For
higher-efficiency products (i.e., 78
percent AFUE and higher), DOE noticed
that efficiency decreases as capacity
increases. For lower-efficiency products
(i.e., 73 to 77 percent AFUE), DOE
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65871
noticed that efficiency increases as
capacity increases. Therefore, because of
the differing trends between capacity
and efficiency, DOE proposes that the
two product classes for gas wall fan-type
DHE should remain.
ii. Gas Wall Gravity-Type Direct Heating
Equipment
DOE examined the relationship
between AFUE and input rating for
gravity-type wall furnaces by reviewing
AHRI’s Consumers’ Directory and
available product literature. DOE
identified products with input
capacities ranging from 5,000 to 50,000
Btu/h. The Federal energy conservation
standards for gas wall gravity-type
furnaces divide these products into
seven product classes based on input
capacity ranges. The seven product
classes are differentiated by one AFUE
percentage point increase for each
increase in input capacity range (i.e., the
larger the input capacity, the higher the
AFUE requirements). The market data
for gas wall gravity-type furnaces
indicate that manufacturers are not
offering products over the entire input
capacity range. Therefore, some product
classes may be unnecessary. DOE
proposes that five product classes (up to
10,000 Btu/h, over 10,000 and up to
12,000 Btu/h, over 12,000 and up to
15,000 Btu/h, over 15,000 and up to
19,000 Btu/h, and over 19,000 and up to
27,000 Btu/h) be consolidated into a
single product class labeled up to
27,000 Btu/h, leaving three product
classes for gas wall gravity-type
furnaces.
iii. Gas Floor-Type Direct Heating
Equipment
DOE surveyed the current market for
gas floor furnaces by reviewing AHRI’s
Consumers’ Directory and available
product literature. The AHRI directory
lists 23 products. The Federal energy
conservation standard includes two
product classes divided by input
ratings, one above and one at or below
37,000 Btu/h. According to the AHRI
directory, more than 75 percent of
products are rated above 37,000 Btu/h.
When comparing the models with the
highest AFUE rating between the two
product classes in the preliminary
analysis, however, DOE found that the
energy savings potential increases as the
input capacity range increases. This fact
suggests that input capacity affects the
AFUE of gas floor-type furnaces.
Therefore, DOE proposes that the two
product classes for gas floor-type DHE
should remain.
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iv. Gas Room-Type Direct Heating
Equipment
DOE examined currently available
room heaters by reviewing AHRI’s
Consumers’ Directory and product
literature. DOE found that room heaters
have inputs ranging from 20,000 to
70,000 Btu/h. DOE also determined that
the relationship between AFUE and
input rating established by the Federal
energy conservation standards is
generally similar to the trend found
among products listed in the AHRI
directory. The market data show a
general trend of increasing AFUE with
input capacity range. DOE is proposing
to consolidate the two lower input
capacity ranges into a single product
class (i.e., input ratings up to 20,000
Btu/h), because there are no products in
the AHRI directory under 20,000 Btu/h
and all products at this input rating
have the same efficiency. As a result,
DOE is proposing only four product
classes for gas room heaters.
Overall, DOE only received one
comment in response to its product
class consolidation for the existing DHE
product types in the preliminary
analysis. AHRI agreed that the number
of product classes (i.e., divisions by
input capacity) for DHE product classes
can be reduced. (AHRI, Public Meeting
Transcript, No. 34.4 at p. 43)
Therefore, for the NOPR, DOE is
proposing to reduce the number of
product classes as suggested in the
preliminary analysis and described
above. DOE is seeking comments on the
proposed product classes. (See Issue 9
under ‘‘Issues on Which DOE Seeks
Comment’’ in section VII.E of this
NOPR.)
v. Gas Hearth Direct Heating Equipment
DOE is proposing to add new product
classes for gas hearth DHE, which are
distinguished by input heating capacity.
DOE modeled the product class
divisions for gas hearth DHE after the
proposed product class divisions for
room heaters. DOE is seeking comments
on the proposed product class divisions
for gas hearth DHE. (See Issue 10 under
‘‘Issues on Which DOE Seeks Comment’’
in section VII.E of this NOPR.)
Table IV.3 presents the proposed
product classes for DHE being
considered for this rulemaking.
TABLE IV.3—PROPOSED PRODUCT CLASSES FOR DIRECT HEATING EQUIPMENT
Input heating capacity
Btu/h
Direct heating equipment type
Gas Wall Fan Type ...........................................................................................................................................
Gas Wall Gravity Type ......................................................................................................................................
Gas Floor ..........................................................................................................................................................
Gas Room .........................................................................................................................................................
Gas Hearth ........................................................................................................................................................
c. Pool Heaters
As discussed above, the existing
Federal energy conservation standards
for pool heaters correspond to the
efficiency levels specified by EPCA, as
amended (42 U.S.C. 6295(e)(2)), and
codified in 10 CFR 430.32(k), classifying
residential pool heaters with one
product class. This product class is
distinguished by fuel input type (i.e.,
gas-fired). DOE notes there are currently
electric heat pump pool heaters on the
market, which are not being considering
in today’s rulemaking, as discussed in
section IV.A.1.b.
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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:
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1. Technological feasibility. DOE will
consider technologies incorporated in
commercial products or in working
prototypes to be technologically
feasible.
2. Practicability to manufacture,
install, and service. If mass production
and reliable installation and servicing of
a technology in commercial products
could be achieved on the scale
necessary to serve the relevant market at
the time the standard comes into effect,
then DOE will consider that technology
practicable to manufacture, install, and
service.
3. Adverse impacts on product utility
or product availability. If DOE
determines a technology would have a
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
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Up to 42,000.
Over 42,000.
Up to 27,000.
Over 27,000 and
Over 46,000.
Up to 37,000.
Over 37,000.
Up to 20,000.
Over 20,000 and
Over 27,000 and
Over 46,000.
Up to 20,000.
Over 20,000 and
Over 27,000 and
Over 46,000.
up to 46,000.
up to 27,000.
up to 46,000.
up to 27,000.
up to 46,000.
(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 consider this
technology further.
4. Adverse impacts on health or
safety. If DOE determines that a
technology will have significant adverse
impacts on health or safety, it will not
consider this technology further.
10 CFR part 430, subpart C, appendix
A, 4(a)(4) and 5(b).
In the preliminary analysis, DOE
initially identified the technology
options that could improve the
efficiency of the three types of heating
products that are the subject of this
rulemaking. These technologies are
listed in Table IV.4. See chapter 3 of the
NOPR TSD for a detailed description of
each technology option.
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TABLE IV.4—TECHNOLOGIES DOE CONSIDERED FOR HEATING PRODUCTS
Water heaters
Direct heating equipment
Pool heaters
Heat Traps
Insulation Improvements
Power Vent (Gas-Fired and Oil-Fired Only)
Heat Exchanger Improvements
Electronic Ignition
Thermal Vent Damper
Heat Exchanger Improvements
Flue Damper (Electromechanical)
Side-Arm Heater
Electronic (or Interrupted) Ignition
Heat Pump Water Heater (Electric Only)
CO2 Heat Pump Water Heater
Flue Damper (Buoyancy Operated)
Directly-Fired
Condensing
Condensing Pulse Combustion
Thermophotovoltaic and Thermoelectric Generators
Reduced Burner Size (Slow Recovery)
Timer Control
Two-Phase Thermosiphon (tpts)
Modulating Controls
Intelligent Controls
Self-Cleaning
Electrical Vent Damper
Power Burner
Induced Draft
Two Stage and Modulating Operation
Improved Fan or Blower Motor Efficiency
Increased Insulation (Floor Furnaces Only)
Condensing
Condensing Pulse Combustion
Air Circulation Fan
Sealed Combustion
In response to DOE’s request for
comments at the preliminary analysis
stage of the rulemaking, DOE did not
receive any comments suggesting
additional technologies beyond those
technology options presented in the
preliminary analysis. Therefore, DOE
Electronic Ignition
Improved Heat Exchanger Design
More Effective Insulation (Combustion Chamber)
Power Venting
Sealed Combustion
Condensing Pulse Combustion
Condensing
considered the same technology options
for the NOPR screening analysis.
of the screening criteria described
above. The technology options that were
screened out, along with the reasons for
their exclusion, are shown below in
Table IV.5. For greater detail regarding
each technology option, please see
Chapters 3 and 4 of the TSD
accompanying today’s notice.
1. Comments on the Screening Analysis
In the preliminary analysis, DOE
excluded several of the technologies
listed in Table IV.4 from consideration
in this rulemaking based on one or more
TABLE IV.5—SUMMARY OF SCREENED-OUT TECHNOLOGY OPTIONS
Reasons for exclusion
Applicable product types
Excluded technology option
Technological
feasibility
Practicability to
manufacture, install, and service
Adverse impacts
on product utility
Adverse impacts
on health of
safety
Water Heaters ..........................
Side-Arm Heater .......................
Advanced Insulation .................
Thermophotovoltaic and Thermoelectric Generators.
U-Tube Flue Design .................
CO2 Heat Pump Water Heaters
Two-Phase Thermosiphons ......
Reduced Burner Size (Slow
Recovery).
Directly Fired Water Heater ......
Flue Damper (Buoyancy Operated).
Condensing Pulse Combustion
Increased Heat Transfer Coefficient.
Power Burner ............................
Improved Fan Blower Motors ...
Condensing Pulse Combustion
Condensing Pulse Combustion
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Pool Heaters .............................
In response to the screening analysis
performed for the preliminary analysis,
DOE received feedback from several
interested parties.
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a. General Comments
NRDC commented generally that
screening technologies because they
have not penetrated the market for the
covered product is a flawed approach.
NDRC stated that determining if a
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product is practical to manufacture does
not require someone to already be
manufacturing it. Instead, NRDC stated
that when determining whether a
product is practical to manufacture,
DOE should consider identified
technology options even if they are not
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currently used in covered products.
NRDC stated that DOE should gather
data to determine whether technologies
used in other products would be useful
in the products in question. (NRDC, No.
48 at p. 3)
In response, as part of every
rulemaking, DOE reviews the markets
and technologies of the appliances
under consideration using primary and
secondary research. DOE considers
prototype designs in the analysis that
have not yet fully penetrated the market.
In the case of a prototype design (or any
design that has not penetrated the
market at the time of the analysis) that
is not being manufactured on a large
scale, DOE examines the practicality of
manufacturing, installing, and servicing
the design, if it were required to be
implemented on a larger scale by the
anticipated compliance date of a
standard, and accepts the product or
screens it out of the analysis on that
basis. DOE requires demonstration of a
technology in at least a working
prototype, because even though
technologies may be proven for other
applications, it may not translate to a
different product type for a variety of
reasons. NRDC did not point to specific
examples of technologies DOE should
consider, and hence, it is more difficult
for DOE to specifically address the
comment.
AHRI commented that DOE should
recognize that many DHE products do
not require electricity. AHRI stated that
such designs allow consumers to use
these products for emergency heat
during power outages, which provides a
real utility that needs to be factored into
DOE’s analysis. (AHRI, Public Meeting
Transcript, No. 34.4 at p. 21)
DOE considers the impact of any
lessening of utility from standards
during the screening analysis. If DOE
determines 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 consider this
technology further. DOE considered
several technology options for DHE that
require electricity for the NOPR
analyses, including electronic ignition
systems and blowers or fans. Blowers
and fans are generally not necessary for
the products to operate and, because the
equipment can be operated without
them, do not impact the utility of being
able to use the equipment for emergency
heat during a power outage. For models
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with electronic ignition systems,
electricity is required to light the
burner, and, thus, required for product
operation. In the case of a power failure,
however, many products employ battery
backup systems that can provide the
electrical power needed to light the
burner (or the pilot in the case of
intermittent pilot ignitions) during the
power outage. Because of this, an
electronic ignition system with battery
backup would not cause any lessening
of utility as compared to a traditional
standing pilot system for DHE.
Therefore, DOE did not screen out these
technologies.
b. Water Heaters
NEEA and NPCC stated that tank
bottom insulation is an effective means
of improving product efficiency.
Accordingly, NEEA and NPCC urged
DOE to consider this as a technology
option for electric storage water heaters
because field data from the Pacific
Northwest suggest that tank bottom
insulation decreases standby energy
loss, especially when the tank is located
on a concrete slab. (NEEA and NPCC,
No. 42 at p. 4)
DOE considered various
improvements in insulation for storage
water heaters during the screening
analysis, including tank bottom
insulation. (See chapter 3 of the NOPR
TSD for a full description of the
insulation improvements DOE
considered.) DOE notes that tank bottom
insulation was not screened out during
the screening analysis, which is in
contrast to advanced forms of insulation
which were screened out as unproven
(e.g., vacuum panels, aerogels). When
listing the potential technology options
at each efficiency level (see section
IV.C.3), DOE shows only those
technologies most commonly used in
manufacturing, although specific
implementation details vary by
manufacturer. Manufacturers currently
do not use increased tank bottom
insulation as a primary means of
increasing efficiency; therefore, it was
not listed as one of the technologies
used in achieving these efficiency levels
for storage water heaters. Hence, DOE
agrees with NEEA and NPCC that tank
bottom insulation is an effective means
of improving the energy factor of storage
water heaters.
NEEA and NPCC also urged DOE to
include as technology options heat
pump water heaters that use CO2 as the
refrigerant. NEEA and NPCC
commented that CO2 heat pump water
heaters have been sold and serviced by
hundreds of thousands of manufacturers
in Southeast Asia and elsewhere over
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the last 5 to 10 years. (NEEA and NPCC,
No. 42 at pp. 4–5)
DOE is not considering CO2-based
heat pump water heaters because DOE
research suggests U.S. manufacturers do
not have the necessary infrastructure to
support manufacturing, installation, and
service of CO2 heat pump water heaters
on the scale necessary to serve the
relevant market by the compliance date
of an amended energy conservation
standard. DOE also does not believe
manufacturers would be able to develop
the necessary infrastructure before the
compliance date of an amended energy
conservation standard because these
products have not penetrated the U.S.
market.
ACEEE commented that DOE should
revisit the preliminary conclusions
presented in the screening analysis,
including the tentative decision to not
further consider thermophotovoltaic
and thermoelectric generators. (ACEEE,
No. 35 at pp. 3–4) The commenter stated
that the inclusion of thermophotovoltaic
and thermoelectric generators would
make other technologies such as sidearm themosiphons more feasible.
ACEEE asserted that in the case of
thermophotovoltaic and thermoelectric
generators, DOE assumes that line
voltage or 24-volt power cannot be
required for gas-fired storage water
heaters. DOE research suggests that the
amount of power that can be generated
by thermophotovoltaic and
thermoelectric generators in a
residential storage water application is
quite limited. Commercially-available
thermoelectric elements for water
heaters typically produce less than 0.05
Watts of power, and so-called
thermopiles can reach as high as 0.75
Watts. While it is theoretically possible
to power devices other than the
customary gas valves with
thermoelectric power sources, DOE is
unaware of an external device that has
an impact on energy efficiency whose
power demands are low enough to allow
it to be powered by such generators.
DOE is also unaware of any
thermophotovoltaic power generators
that have been developed to the point
where they could be incorporated by the
compliance date of the rulemaking, nor
of any role that such generators would
play in increasing the energy efficiency
of gas-fired storage water heaters.
Rheem commented that DOE should
recognize the special utility of selfpowered water heaters. (Rheem, No. 49
at p. 4) DOE acknowledges that most
gas-fired storage-water heaters on the
market today do not require an electrical
connection to operate (i.e., they are selfpowered). Typically, the gas valves on
these units incorporate a thermoelectric
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element that is impinged on by a
standing pilot flame. The minute power
generated by the thermoelectric element
opens the gas supply in the valve
assembly via a low-power solenoid.
Thus, thermoelectric elements typically
act as a safety device. They do not
provide sufficient power to run fan
blower motors and other high-powered
devices. Therefore, DOE has tentatively
decided to continue to exclude
thermophotovoltaic and thermoelectric
generators from its analysis, because
they are not an effective means of
improving the efficiency of water
heaters.
ACEEE also stated that DOE should
revisit the preliminary conclusions
presented in the screening analysis
regarding flue dampers since
electromechanical dampers were
common on furnaces and boilers and
appear to be available for residential
boilers today. (ACEEE, No. 35 at pp. 3–
4) DOE research suggests that there are
no residential storage water heaters on
the market today that incorporate such
dampers.
Although electromechanical dampers
may be found on some furnaces, boilers,
and commercial water heaters, their
benefit in a residential water heater
application is unknown because no
manufacturer incorporates them in their
products. All products that incorporate
electromechanical dampers of which
DOE is aware require line power to
operate them. Thus, such dampers may
not be practicable for all consumers.
Additionally, DOE researched damper
systems that do not require electrical
power to operate. Typically, such
systems are based on a bi-metal damper
installed on top of the flue pipe outlet
that opens when heated and closes as it
cools. DOE research suggests that such
non-electrically-actuated dampers pose
potential health and safety problems.
For example, such dampers can fail in
the closed position, which could cause
the exhaust gases to be stuck in the flue.
Furthermore, they rely on hot air
impingement to open. However, when
the water heater begins its combustion
cycle, the flue and its baffles are
relatively cold, and flue gas
temperatures may require some time
until they reach the point where they
will open a bi-metal damper quickly
and completely. This is especially true
for flammable vapor ignition resistant
(FVIR) water heaters (which all
residential water heaters are) whose
natural draft is already restricted by
FVIR components. With the flue shut or
mostly shut on start-up, water heater
combustion can be impacted in a
number of ways, including nuisance
lockouts, increased carbon monoxide
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production, and flue gases spilling into
living spaces. For these reasons, nonelectromechanical dampers were
screened out.
ACEEE commented that DOE should
revisit the preliminary conclusions
presented in the screening analysis
regarding advanced forms of insulation,
which resulted in DOE’s tentative
decision to screen out those
technologies. (ACEEE, No. 35 at pp. 3–
4) In response, DOE research suggests
that emerging technologies such as
vacuum-insulated-panels (VIPs) may
allow manufacturers to reduce heat loss,
but such technologies have yet to find
application in storage water heaters.
DOE notes that ACEEE did not provide
any new rationale or data to support
why DOE should reconsider its original
conclusion presented in the preliminary
screening analysis that advanced forms
of insulation have not been
demonstrated as practical to
manufacture and install. Hence, DOE
screened out advanced forms of
insulation from the NOPR analyses.
ACEEE also stated that DOE should
revisit its preliminary conclusions
regarding sidearm heaters and twophase thermosiphons (TPTS) which
resulted in DOE’s tentative decision to
screen out those technologies. (ACEEE,
No. 35 at pp. 3–4) Regarding two-phase
thermosiphons, ACEEE did not provide
any explanation in its comment as to
why DOE should reconsider its initial
conclusion that it is not practicable to
manufacture, install, and service this
technology on the scale necessary to
serve the relevant market at the time
compliance with the standard is
required. TPTSs require a drastic
redesign of the water heater and are
typically not practical for indoor
installation. Therefore, DOE has
continued to screen out this technology.
Regarding side-arm heaters, ACEEE
commented that sidearm heaters are
more feasible with access to 24-volt
power, which would allow them to be
located above or below the unit. This
assertion does not address DOE’s
concerns about sidearm heaters
presented in the preliminary analysis.
DOE research did not reveal any
working prototypes for gas-fired or oilfired storage water heaters, and
manufacturers seem to no longer use
this technology. Therefore, this
technology is not feasible and not
practical to manufacture, install, and
service side-arm storage water heaters
on the scale necessary to serve the
relevant market at the time of the
compliance date of the standard, and
was not considered further in the
analysis. See chapter 4 of the NOPR
TSD, Screening Analysis, for more
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65875
details about DOE’s assessment of twophase thermosiphons and sidearm
heaters.
For the reasons listed above, DOE still
believes that thermophotovoltaic and
thermoelectric generators, side-arm
heaters, and advanced forms of
insulation are not technologically
feasible and are impractical to
manufacture, repair, and install; that
two-phase thermosiphons are
impractical to manufacture, repair, and
install; and that buoyancy operated flue
dampers have an adverse impact on the
safety of these products.
Bradford White Corporation (BWC)
stated that using multiple flues for gasfired storage water heaters is difficult,
costly, and impractical to produce on
residential water heater tank production
lines. (BWC, No. 46 at p. 2)
In response, DOE research suggests
that multi-flue storage water heaters can
be produced at a higher production
scale than is commonly done now. The
current low shipment-volume
techniques are commonly used in
commercial gas-fired and oil-fired water
heater designs. Solutions for highervolume production of such heaters
would require significant investments
but are not technically infeasible. Thus,
DOE believes multiple flue designs
could be implemented on residential
storage water heaters and are a viable
technology for improving the efficiency
of oil-fired storage water heaters.
In summary, none of the comments
DOE received on the screening analysis
led DOE to reconsider its determination
for any of the technologies that were
excluded from the preliminary analysis.
Therefore, DOE excluded the same
technologies in the NOPR analysis.
Chapter 4 of the NOPR TSD provides
more details about the technologies that
DOE screened out.
2. Technologies Considered
Based upon the totality of the
available information, DOE has
tentatively concluded that: (1) All of the
efficiency levels discussed in today’s
notice are technologically feasible; (2)
products at these efficiency levels could
be manufactured, installed, and serviced
on a scale needed to serve the relevant
markets; (3) these efficiency levels
would not force manufacturers to use
technologies that would adversely affect
product utility or availability; and (4)
these efficiency levels would not
adversely affect consumer health or
safety. Thus, the efficiency levels that
DOE analyzed and is discussing in this
notice are all achievable through
technology options ‘‘screened in’’
during the screening analysis. The
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technologies DOE considered are shown
in Table IV.6 through Table IV.8.
TABLE IV.6—TECHNOLOGIES DOE CONSIDERED FOR THE WATER HEATER ENGINEERING ANALYSIS
Water heater type by Fuel Source
Technology
Storage
Instantaneous
Gas-fired
Increased Jacket Insulation .............................................................
Foam Insulation ...............................................................................
Improve/Increased Heat Exchanger Surface Area ..........................
Enhanced Flue Baffle ......................................................................
Direct-Vent (Concentric Venting) .....................................................
Power Vent ......................................................................................
Electronic (or Interrupted) Ignition ...................................................
Heat Pump Water Heater ................................................................
Condensing ......................................................................................
TABLE IV.7—TECHNOLOGIES DOE
CONSIDERED FOR THE DIRECT
HEATING EQUIPMENT ENGINEERING
ANALYSIS
Technology
Increased Heat Exchanger Surface Area.
Direct-Vent (Concentric Venting).
Electronic Ignition.
Induced Draft.
Two Stage and Modulating Operation.
Condensing.
TABLE IV.8—TECHNOLOGIES DOE
CONSIDERED FOR THE POOL HEATER ENGINEERING ANALYSIS
Technology
Increased Heat Exchanger Surface Area.
More Effective Insulation (Combustion Chamber).
Power Venting.
Sealed Combustion.
Condensing.
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3. Heat Pump Water Heaters Discussion
For the preliminary analysis, DOE
considered heat pump water heaters as
a viable technology option for
improving the efficiency of electric
storage water heaters. DOE posted the
preliminary TSD for residential heating
products on its Web site on January 5,
2009 (for more information see https://
www1.eere.energy.gov/buildings/
appliance_standards/residential/
water_pool_heaters_prelim_tsd.html).
Pages 2–21 to 2–29 of chapter 2 of the
preliminary TSD contain an extensive
discussion of heat pump water heaters
and the significant issues pertaining to
the consideration of heat pump water
heaters in this rulemaking. In the
executive summary to the preliminary
TSD, DOE sought comments on the
viability of heat pump water heaters as
a technology for electric storage water
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Oil-fired
Gas-fired
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heaters and whether these water heaters
would be practicable to manufacture,
service, and install on a scale necessary
to serve the relevant market by the
compliance date of any amended
standard, which would be five years
after publication of the final rule.
In addition, DOE sought comment on
several other issues regarding integral
heat pump water heaters: (1) Whether
manufacturers would be able to finance
the investment costs necessary to
convert their existing product lines to
heat pump water heaters by the
compliance date of an amended
standard; (2) what percentage of
manufacturers’ product lines would be
converted to heat pump water heaters
by the compliance date of an amended
standard (e.g., if standards did not reach
the levels provided by heat pump water
heaters); (3) how the market for heat
pump water heaters has changed since
the January 2001 final rule, and the
number of installations that would incur
a significant increase in cost due to
extensive modifications that will have
to be made to a residence to
accommodate a heat pump water heater;
and (4) heat pump water heater
programs that have been conducted
since the January 2001 final rule.
In response to the preliminary
analysis, DOE received a multitude of
comments from interested parties, both
at the public meeting and in written
responses during the preliminary
analysis comment period. A summary of
the comments received and DOE’s
responses are presented below.
a. Consumer Utility
Southern stated that DOE needs to
address issues regarding cold air
produced by heat pump water heaters.
According to Southern, simply
increasing a residence’s heat output is
not an appropriate way to compensate
for the cold air a heat pump water
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heater generates. Southern also asserted
that constantly blowing cold air will
create uneven temperatures within the
dwelling space, leading to utility and
comfort issues. (Southern, Public
Meeting Transcript, No. 34.4 at p. 22)
Southern noted that a heat pump water
heater could provide supplemental
cooling during a home’s cooling hours;
however, concentrated cooling at a
particular location would result in
uneven temperatures in a home, thereby
being incompatible with the home’s
temperature needs. Southern stated that
this would reduce the utility and
performance of a home’s HVAC system,
and that there is no practical solution.
(Southern, No. 50 at p. 2) The
commenter stated that an HVAC supply
vent near the unit would not help
mitigating cold air issues. Southern
commented that although a vent may
cancel the effect of the cool air supplied
in the winter (by supplying heat),
during the cooling season, the supply
vent (now supplying cool air) would
exacerbate the temperature imbalance in
the area of the heat pump water heater.
(Southern, No. 50 at p. 2)
DOE agrees with Southern that cold
air production of heat pump water
heaters should be considered in the
analysis. While DOE believes most
consumers would choose to increase the
use of their space heating system to deal
with the increased heating load, DOE
did account for the possibility that some
consumers would choose to install
ductwork to vent cold air away from the
space surrounding the water heater to
the outdoors to overcome uneven
temperature problems. The increased
installation costs of venting cold air
away from a conditioned space, along
with the increased cost of space heating
for consumers who choose not to vent
cold air away from the conditioned
space, are accounted for in DOE’s
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analysis for certain percentages of
consumers (see section IV.E.2).
Southern also commented on noise
issues. Southern stated that is difficult
to comment on a hypothetical product
where no specifications exist, but that
existing electric storage water heaters
are often located in utility closets close
to bedrooms and living areas. The
commenter asserted that even if the
product generates decibel levels similar
to a refrigerator, such noise is a matter
of greater concern because a heat pump
water heater would tend to be in closer
proximity to a bedroom or other quiet
living area, as compared to a refrigerator
located in a kitchen. Noise dampening
would not be practical because louvered
doors would be required to allow
adequate air flow for the heat pump
water heater. Southern cited the EPCA
criteria, stating that there would be a
significant impact on the utility or
performance of the appliance if
excessive noise disturbs the consumer.
(Southern, No. 50 at p. 2)
DOE does not agree that the
additional noise from a compressor used
for a heat pump water heater would
affect consumer utility for two reasons.
First, as Southern points out, noise from
a heat pump water heater compressor
may be comparable in decibel level to
the noise created by a refrigerator
compressor, which has not been found
to adversely affect consumer utility.
Second, while the actual impact of
excess noise created by a compressor
may vary greatly based on the location
of the appliance installation, DOE does
not have any reason to believe that
water heaters are any more likely to be
installed near a bedroom than a
refrigerator. Water heaters are typically
not installed in consumers’ bedrooms or
living spaces, but instead are usually
installed in garages, closets, basements,
attics, or other locations away from the
living space. Thus, DOE believes that
noise created by a compressor would
not significantly impact consumer
utility.
b. Production, Installation, and
Servicing Issues
DOE received numerous comments in
response to the preliminary analysis on
the practicality of manufacturing,
installing, and servicing heat pump
water heaters.
Southern stated that it is difficult to
determine whether heat pump water
heaters would be practical to install and
service and if they are reliable, because
at the time Southern submitted this
comment, there were no products on the
market to compare against. (DOE notes
several heat pump water heaters have
recently become available on the
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market). Also, no product exists yet that
could be mass produced and available
in 2015 in response to a heat pump
water heater energy efficiency standard.
(Southern, Public Meeting Transcript,
No. 34.4 at pp. 58–59) Further, Southern
commented that installation of heat
pump water heaters in new construction
is still problematic for multifamily
housing, although the issues are less
severe than in replacement installations.
In multifamily housing, interior
locations are preferred for mechanical
systems, and perimeter locations (e.g.,
windows and balconies) are preferred
for exterior exposures. Southern stated
that a heat pump water heater could be
installed in an interior, but the addition
of supply and return vents to the
outdoors would be expensive. Southern
also stated that placing the heat pump
water heater at a perimeter location is
possible, but would reduce the
architectural options available for
builders. (Southern, No. 50 at pp. 2–3)
Finally, Southern commented that it is
very concerned about the possible
selection of an amended conservation
standard at an efficiency level that
would require heat pump water heaters.
Southern strongly encourages the use of
heat pump water heaters, but it argued
that given operational differences, they
are not suitable for some consumers due
to the need for very expensive building
modifications. (Southern, No. 50 at p. 1)
BWC noted that the owner or installer
can return a water heater to the
manufacturer if a defect is claimed.
BWC stated that in these cases, units are
tested and typically there is no actual
defect. According to BWC, if heat pump
water heaters are introduced on a larger
scale, it is likely that more water heaters
will be returned to the manufacturer
without servicing because many
traditional plumbers (who would install
the heat pump water heaters) have no
HVAC training and no refrigerant
licenses. (BWC, No. 46 at p. 2) BWC
stated that training and education costs
associated with heat pump water
heaters were overlooked in the previous
rulemaking and have been overlooked
in the current rulemaking as well.
(BWC, No. 46 at p. 2)
GE stated that it will be producing a
heat pump water heater sometime in the
near future, and asserted that it is
practical to manufacturer, install, and
service heat pump water heaters.
Further, GE added that it has the
facilities to both manufacture and
service these products. It is GE’s
opinion that there will be a great deal
of consumer interest in such products,
and that this market will increase and
be much larger than the current market.
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(GE, Public Meeting Transcript, No. 34.4
at p. 63)
In its written submission, GE also
commented on the practicality of
installation and service. GE stated that
its heat pump water heater occupies the
exact footprint of a standard water
heater and requires the same electrical
and plumbing connections. (GE, No. 51
at p. 2) According to GE, the vast
majority of installations would be
simple and straightforward, and
consumers would achieve significant
energy savings and often may obtain
collateral installation benefits such as
dehumidified basements or cooler attics.
(GE, No. 51 at p. 2) GE argued that heat
pump water heaters installed in humid
locations could eliminate the need for a
separate dehumidifier, which could
save consumers both capital and energy.
(GE, No. 51 at p. 2) GE acknowledged
that a heat pump water heater produces
a small amount of condensate. However,
GE commented that this would not
require any building modifications, as
condensate is easily drained to a floor
drain that should accompany each water
heater for leakage or overflow. (GE, No.
51 at p. 2) Alternatively, GE commented
that for heat pump water heaters that are
not installed near a floor drain, a small
condensate pump (similar to those used
for HVAC installations) can be installed
to pump condensate to a suitable drain.
(GE, No. 51 at p. 2) GE did state that
heat pump water heater installation in
confined spaces with very small areas
and no ventilation may present
challenges. (GE, No. 51 at p. 2)
Regarding the reliability issues
surrounding heat pump water heaters,
ACEEE stated that the historical record
of failures for heat pump water heaters
arises from the fact that initial models
were brought to market by laboratorybased applied research and
development companies and
commercial niche companies, rather
than the major consumer appliance
companies that are currently
announcing heat pump water heater
products. ACEE stated that an analysis
which ignores the nature of the
manufacturer is bound to misrepresent
the potential of the heat pump water
heater. (ACEEE, Public Meeting
Transcript, No. 34.4 at pp. 65–66) NEEA
and NPCC acknowledged the failure
issues discussed in the preliminary
analyses, but they argued that the
failures have been attributable to the
control boards, which other markets
have experienced. NEEA and NPCC
stated that the control board failures are
not characteristic of the heat pump
water heaters, but of the electronics
industry itself, and replacement is a
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simple and inexpensive remedy. (NEEA
and NPCC, No. 42 at p. 5)
In response to the comments provided
by Southern, BWC, GE, ACEEE, NEEA,
and NPCC, DOE believes that heat pump
water heaters could potentially be
installed and serviced on the scale
necessary for the residential market
before the potential compliance date of
an amended energy conservation
standard for water heaters. Although
servicing heat pump water heaters will
require significantly more training than
servicing traditional electric storage
water heater technologies, DOE notes
that many domestic appliances are
being installed and repaired today
which feature compressors (i.e.,
refrigerators, room air conditioners, and
similar appliances). DOE believes that,
given the 5-year delay between the
issuance of the final rule and the
compliance date and the fact that many
manufacturers already have these
products under development, it is
unclear whether manufacturers would
be able to retrain installers and service
technicians to install and service heat
pump water heater technology. DOE
estimated the additional costs that
would be incurred as a result of
increased certification requirements to
install and service heat pump water
heaters in its analyses. See section
IV.E.2 for details.
A.O. Smith asserted that heat pump
water heaters are a viable technology to
serve a portion of the water heater
market, but that they are only practical
for a small, niche part of the market and
should never be considered when
setting the ‘‘efficiency floor’’ of the
electric water heater market. A.O. Smith
argued that manufacturers could make
the investment needed for the small
volumes of heat pump water heaters
that manufacturers believe are practical,
but the cost of changing every line
completely over to heat pump water
heaters would be prohibitive. In
addition, A.O. Smith stated that the
percentage of heat pump water heaters
to penetrate the market will be small
and will be driven by market incentives
such as tax credits and rebates. (A.O.
Smith, No. 37 at p. 8) BWC stated that
it could likely convert some of its
product lines to heat pump water
heaters by the compliance date of the
standard. BWC also commented that
without knowing the cost to retrofit
current production lines and the cost of
heat pump water heaters, it cannot
comment on what percentage could be
converted by the compliance date.
(BWC, No. 46 at p. 1) Edison Electric
Institute stated that heat pump water
heaters are different from standard
electric storage water heaters and cannot
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be considered for direct replacements
due to technology, size, and other
issues. EEI also stated its concern that
industry would not be able to increase
production from under 10,000 units per
year to 4.5 million units per year by the
compliance date of the standard.
According to EEI, if DOE does not create
a separate product class for heat pump
water heaters, DOE should screen out
this technology from this rulemaking.
(EEI, No. 40 at p. 3)
DOE acknowledges there could be
issues with converting entire production
lines to manufacture heat pump water
heaters before the compliance date of
this standard. However, DOE also notes
that significant portions of heat pump
water heaters are expected to remain
very similar in design to current
standard electric storage water heaters.
Manufacturers could choose to produce
the heat pump portion of the water
heater in-house or purchase it from a
supplier. GE has already announced that
a heat pump water heater will be
available sometime this year, and other
major manufacturers are also developing
heat pump water heaters. Given the 5year delay in compliance date from the
issuance of the final rule, and the fact
that many manufacturers are already
developing heat pump water heaters,
DOE believes manufacturers may be
able to convert their entire product lines
before the compliance date of an
amended energy conservation standard.
However, DOE also recognizes there
would likely be significant impacts on
manufacturers. DOE considers those
impacts in the MIA section of this
NOPR (section IV.H).
DOE is seeking comment on the
manufacturability of heat pump water
heaters and the capability of
manufacturers to ramp up production.
DOE is specifically seeking comment on
how long it would take, and how much
it would cost, for manufacturers to
convert all product lines to heat pump
water heaters if it were required by an
amended energy conservation standard.
Additionally, DOE is seeking comment
about the capability of water heater
installers and servicers to meet the
unique demands created by heat pump
water heaters. DOE is requesting
comment about how long it would take
to train installers and servicers to be
able to serve the market created if heat
pump water heaters were required by an
amended energy conservation standard.
DOE will consider all of these factors as
it weighs the benefits and burdens of
each TSL. (See Issue 11 under ‘‘Issues
on Which DOE Seeks Comment’’ in
section VII.E of this NOPR.)
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c. General Comments
DOE received several general
comments about the current condition
of heat pump water heater technology
and the market for this product. These
comments are discussed immediately
below.
Southern commented that, although
not desirable, it would be less
objectionable to require heat pump
water heaters if the electric storage
water heater class could be split at 40
gallons, with products larger than 40
gallons having a heat pump water heater
efficiency level requirement, and
products smaller than 40 gallons having
a higher electric resistance efficiency
level. (Southern, No. 50 at p. 4)
EEI stated that there is a Federal tax
credit for heat pump water heaters. (EEI,
Public Meeting Transcript, No. 34.4 at p.
60) AHRI stated that the ENERGY STAR
program has been established since the
previous rulemaking, creating greater
recognition by all interested parties
about the need to save energy. AHRI
commented that every manufacturer is
probably investigating whether it can
maintain a feasible business providing
heat pump water heaters. However,
AHRI also commented that DOE should
not consider heat pump water heaters as
an energy conservation standard for
2015. According to the commenter, the
water heater industry and American
consumers are experiencing difficult
economic conditions, and consumers
are not likely to purchase heat pump
water heaters that are expensive. AHRI
also stated that resistance-type electric
storage water heaters are near their
maximum efficiencies and need to
evolve. AHRI commented that current
conditions prohibit setting an efficiency
minimum that would require a heat
pump water heater. (AHRI, Public
Meeting Transcript, No. 34.4 at pp. 60–
62)
AHRI stated that current market
conditions and the introduction of heat
pump water heater models by water
heater manufacturers are allowing heat
pump water heaters to take root in the
market. Further, AHRI asserted that the
heat pump water heater market needs to
mature and that DOE should allow the
market and consumers to respond to the
availability of higher-technology electric
storage water heaters that are reliable
and meet consumer utility needs.
(AHRI, Public Meeting Transcript, No.
34.4 at pp. 64–65)
ACEEE stated that ENERGY STAR’s
water heater program demonstrates that
heat pump water heaters are viable. The
commenter stated that three major
manufacturers have announced or told
ACEEE about a qualifying heat pump
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water heater to be marketed to
consumers in 2009, which is more than
5 years before energy conservation
standard would take effect. (ACEEE, No.
35 at pp. 4–5) ACEEE asserted that costeffectiveness should be examined
because profits are likely to be greater
for more expensive heat pump water
heaters, even in a very competitive
market, and that these higher cost
products may benefit the industry in the
current economic conditions. According
to ACEEE, consumer preference can be
very strong, and market studies show
that consumers have a very
sophisticated understanding of the
benefits of very expensive heat pump
water heaters. ACEEE noted that
consumer preference has been seen for
gas-condensing furnaces and other highpriced products in other markets that
are considered commodity markets.
(ACEEE, Public Meeting Transcript, No.
34.4 at p. 66)
PG&E, SDGE, and SoCal Gas
supported DOE’s decision to include
integral heat pump water heaters as a
max-tech efficiency level for electric
storage water heaters. PG&E, SDGE, and
SoCal Gas believe the heat pump water
heater technology has made important
advances in recent years and pointed to
the actions of General Electric as a major
manufacturer speaking to the viability of
this technology. (PG&E, No. 38 at p. 2)
NEEA and NPCC also agreed with the
inclusion of heat pump water heaters in
the rulemaking analyses, while
acknowledging the failures issues
discussed in the preliminary analyses.
(NEEA and NPCC, No. 42 at p. 5) The
American Gas Association (AGA)
commented that there appear to be no
significant barriers to including heat
pump water heaters in the design
options under consideration for electric
storage water heaters. (AGA, No. 44 at
p. 2)
GE commented that heat pump water
heaters have significant potential for
increasing the energy efficiency of
electric storage water heaters, but that
shipments are currently very low (0.1
percent of all water heaters shipped).
According to GE, heat pump water
heaters should be encouraged through
ENERGY STAR and other consumer
incentives to allow time for heat pump
water heaters to penetrate the market
and prove themselves in terms of energy
cost savings and reliability. GE stated
that the heat pump water heater market
is too new to consider establishing a
minimum standard at a level that would
require heat pump water heater
technology at this time. (GE, No. 51 at
pp. 1–2) Southern also commented that
levels requiring heat pump water heater
technology are not appropriate as an
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amended energy conservation standard
level at this time. (Southern, No. 50 at
p. 4)
DOE believes that the ENERGY STAR
program and Federal tax credit program,
along with recent developments in heat
pump water heater technology due to
manufacturers’ efforts, have made heat
pump water heaters a much more viable
technology for improving energy
efficiency. As such, DOE is tentatively
proposing to consider heat pump water
heaters in this analysis as a design
option for improving the efficiency of
conventional electric storage water
heaters. DOE considers the possibility of
fuel switching resulting from heat pump
water heater standards for electric
storage water heaters in its shipments
analysis (see section IV.F.1).
The technologies evaluated in the
screening analysis all have been used or
are in use in commercially-available
products, or exist in working
prototypes. These technologies all
incorporate materials and components
that are commercially available in
today’s supply markets for the products
covered by this NOPR. Therefore, DOE
believes all of the efficiency levels
evaluated in this notice are
technologically feasible.
C. Engineering Analysis
The engineering analysis develops
cost-efficiency relationships to show the
manufacturing costs of achieving
increased efficiency. DOE has identified
the following three methodologies to
generate the manufacturing costs
needed for the engineering analysis: (1)
The design-option approach, which
provides the incremental costs of adding
to a baseline model design options that
will improve its efficiency; (2) the
efficiency-level approach, which
provides the relative costs of achieving
increases in energy efficiency levels,
without regard to the particular design
options used to achieve such increases;
and (3) the cost-assessment (or reverseengineering) approach, which provides
‘‘bottom-up’’ manufacturing cost
assessments for achieving various levels
of increased efficiency, based on
detailed data as to costs for parts and
material, labor, shipping/packaging, and
investment for models that operate at
particular efficiency levels.
For the preliminary analysis, DOE
conducted the engineering analysis
using both the efficiency level approach
to identify incremental improvements in
efficiency for each product and the costassessment approach to develop a cost
for each efficiency level. DOE identified
the most common residential heating
products on the market and determined
their corresponding efficiency levels,
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the component specifications, and the
distinguishing technology features
associated with those levels. After
identifying the most common products
that represent a cross section of the
market, DOE gathered additional
information using reverse-engineering
methodologies; product information
from manufacturer catalogs; and
discussions with manufacturers and
other experts of water heaters, DHE, and
pool heaters. This approach provided
useful information, including
identification of potential technology
paths manufacturers use to increase
energy efficiency.
DOE generated a bill of materials
(BOM) by disassembling multiple
manufacturers’ products that span a
range of efficiency levels for each of the
three product categories. The BOMs
describe the product in detail, including
all manufacturing steps required to
make and/or assemble each part.
Subsequently, DOE developed a cost
model that converted the BOMs and
efficiency levels into manufacturer
production costs (MPCs). By applying
derived manufacturer markups to the
MPCs, DOE calculated the manufacturer
selling prices and constructed industry
cost-efficiency curves.
DOE received several comments from
interested parties on the approach to the
engineering analysis. Rheem stated its
support for DOE’s product teardown
plan and evaluation of insulations
levels. (Rheem, No. 49 at p. 4) Southern
agreed overall with the technical and
engineering assumptions in the TSD.
(Southern, No. 50 at p.1)
Because DOE did not receive any
comments from interested parties
opposing its general approach to the
engineering analysis, DOE continued to
use the same approach for the NOPR
phase of this rulemaking. However, DOE
did receive specific comments from
interested parties on certain aspects of
the engineering analysis. A brief
overview of the methodology, a
discussion of the comments DOE
received, DOE’s response to those
comments, and any adjustments DOE
made to the engineering analysis
methodology or assumptions as a result
of those comments is presented in the
sections below. See chapter 5 of the
NOPR TSD for additional details about
the engineering analysis.
1. Representative Products for Analysis
For the engineering analysis, DOE
reviewed all of the product classes of
residential water heaters (storage-type
and instantaneous), DHE, and pool
heaters. Since the storage volume and
input capacity affect the energy
efficiency of residential heating
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products, DOE examined each product
type separately. Within each product
type, DOE chose units for analysis that
represent a cross section of the
residential heating products market. The
analysis of these representative products
and product classes allowed DOE to
identify specific characteristics that
could be applied to all of the products
across a range of storage and input
capacities, as appropriate.
a. Water Heaters
For residential, storage-type water
heaters, the volume of the tank
significantly affects the amount of
energy consumed, because it takes more
energy to heat a larger volume of water
from a given temperature to a higher
temperature than it does to do the same
for a smaller volume of water. Also, an
increase in the tank volume can create
an increase in the tank surface area,
leading to higher standby losses of two
otherwise identical tanks (i.e., same
insulation thickness, same materials).
For the preliminary analysis, DOE
examined specific storage volumes for
gas-fired, oil-fired, and electric storage
water heaters (referred to as
representative storage volumes and
shown in Table IV.9) because the energy
efficiency equations for residential
water heaters established by EPCA are a
function of each product’s storage
volume. DOE reviewed the shipments
data AHRI provided to determine the
storage volume corresponding to the
highest number of shipments for gasfired water heaters, oil-fired water
heaters, and electric water heaters. DOE
conducted a similar review of shipment
data for instantaneous gas-fired water
heaters and determined the input rating
corresponding to the highest number of
shipments (i.e., 199,000 Btu/h, as shown
in Table IV.9) since storage volume does
not vary for this product class.
DOE did not receive any comments in
response to the preliminary analysis on
the representative units for residential
water heaters, and as such, used the
same approach to determining
representative units for the NOPR
analysis. However, on review of the
shipments for oil-fired storage water
heaters for the NOPR analysis, DOE
determined that oil-fired storage water
heaters with 32 gallons of storage
volume have a higher number of
shipments than those with 30 gallons,
and adjusted the representative unit
accordingly.
TABLE IV.9—REPRESENTATIVE RESIDENTIAL WATER HEATERS ANALYZED
Residential water heater class
Representative storage volume
(gallons)
Gas-Fired Storage Type ............................................................................................................................................
Electric Storage Type ................................................................................................................................................
Oil-fired Storage Type ...............................................................................................................................................
Instantaneous Gas Fired ...........................................................................................................................................
40
50
32
0
(199,000 Btu/h input capacity)
Once DOE conducted the primary
analysis on the representative rated
storage volumes for each of the product
classes, DOE extended the analysis to
other rated storage volumes using the
cost model and the energy efficiency
equations. See section IV.C.7 for
additional details. For gas-fired
instantaneous water heaters, DOE used
the analysis for the 199 kBtu/h input
capacity and applied it to all products
within the product class.
b. Direct Heating Equipment
Current energy conservation
standards for DHE are not determined
by an equation, but by input capacity
ranges. DOE examined one specific
input capacity range for gas wall fan, gas
wall gravity, gas floor, and gas room
DHE in the preliminary analysis. In
addition, DOE examined one specific
input capacity range for gas hearth DHE
in the NOPR analysis. The specific
input ranges DOE analyzed are referred
to as representative input rating ranges.
DOE reviewed the DHE (including
vented hearth products) shipment data
AHRI and HPBA provided for this
rulemaking and found the input rating
range corresponding to the highest
number of shipments for gas wall fan,
gas wall gravity, gas floor, and gas room
DHE. DOE did not receive any
comments from interested parties in
response to the preliminary analysis on
the representative ranges for traditional
DHE, and used the same approach to
determine the ranges for the NOPR
analysis. DOE did not receive shipments
data categorized by capacity ranges for
gas hearth DHE, and, therefore,
determined the representative capacity
range based on the number of models
available on the market in each capacity
range. DOE added a representative range
for gas hearth DHE for the NOPR
analysis. In addition, after reorganizing
the DHE product classes, DOE reviewed
gas room DHE shipments for the NOPR,
and changed the representative input
range for gas room DHE from over
46,000 Btu/h to between 27,000 and
46,000 Btu/h. DOE found the input
range between 27,000 and 46,000 Btu/h
contained the highest number of models
for gas room DHE when the gas hearth
DHE were removed from consideration.
Table IV.10 presents the representative
rated input rating ranges for residential
DHE. For the remaining DHE product
classes (i.e., wall fan, wall gravity, and
floor), DOE did not receive any
comments in response to the
preliminary analysis on the
representative units, and, therefore,
used the same units for the NOPR
analysis.
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TABLE IV.10—REPRESENTATIVE RESIDENTIAL DIRECT HEATING EQUIPMENT PRODUCTS AS DESCRIBED BY INPUT
CAPACITY AND DEFINED BY BTU/H
Direct heating equipment design type
Gas
Gas
Gas
Gas
Gas
Representative input rating range (Btu/h)
Wall Fan ............................................................................................
Wall Gravity ......................................................................................
Floor ..................................................................................................
Room ................................................................................................
Hearth ...............................................................................................
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Over
Over
Over
Over
Over
42,000.
27,000 and up to 46,000.
37,000.
27,000 and up to 46,000.
27,000 and up to 46,000.
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After analyzing the representative
product class (i.e., input rating range),
DOE applied the analysis to the
remaining product classes for each
residential DHE type. Unlike storage
water heaters, an equation is not applied
to relate the range of input ratings.
Instead, DOE proposes to maintain the
AFUE difference between each input
rating range as established by EPCA.
That is, if the amended energy
conservation standard is increased by
two AFUE percentage points for the
representative product class, for
example, the amended energy
conservation standards for the other
product classes within this product type
would all rise by two AFUE percentage
points. The stringency resulting from an
amended standard is constant across the
range of inputs for a given product type.
This approach appears to be consistent
with the relationship between input
capacity and efficiency exhibited by
models currently available on the
market based on DOE’s review of the
AHRI directory for DHE. In addition,
DOE notes that the larger DHE units
usually contain larger heat exchangers
to get higher efficiencies. These larger
heat exchangers have increased surface
area, which also increases the convected
losses to the surroundings. The
increased losses result in lower AFUEs.
Based on the market assessment and
engineering principles, DOE believes
the approach for maintaining the AFUE
difference between each input rating
range is reasonable.
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c. Pool Heaters
There is only one product class for
residential gas-fired pool heaters, but
this product class covers a wide range
of input ratings. Although within the
same product class, the variation in
input rating is large enough to create
variations in pool heater design (e.g.,
large variations in input will vary
material usage and MPC). Therefore, for
the preliminary analysis, DOE reviewed
the shipment data from AHRI and found
the input rating corresponding to the
highest number of shipments, which
was 250,000 Btu/h input rating. Because
DOE did not receive any comments on
the representative input rating in the
preliminary analysis, DOE used the
same approach for the NOPR analysis.
Consequently, DOE used 250,000 Btu/h
as the representative input rating for
residential pool heaters in the NOPR
analysis.
The engineering analysis results for
the representative product classes are
used in the remaining DOE analyses,
including the life-cycle cost analysis
and the national impact analysis.
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2. Ultra-Low NOX Gas-Fired Storage
Water Heaters
In the preliminary analysis, DOE did
not address ultra-low NOX gas-fired
storage water heaters separately from
gas-fired storage water heaters with
standard burners (i.e., non-ultra-low
NOX burner). DOE developed a single
cost-efficiency curve for all gas-fired
storage water heaters. However, DOE
received several comments in response
to the preliminary analysis on the cost
of ultra-low NOX gas-fired storage water
heaters. As discussed in section IV.A.3.a
above, several local air quality
management districts (mostly in
California) limit the allowable NOX
emissions from residential water
heaters.
BWC commented that there is a
substantial cost increase to comply with
the ultra-low NOX requirements. (BWC,
No. 46 at p.1) Rheem commented that
the MPC and MSP did not capture
higher costs and prices associated with
models that comply with ultra-low NOX
requirements. (Rheem, No. 49 at pp. 4,
7) Rheem stated that although DOE
included the costs associated with
Flammable Vapor Ignition Resistant
(FVIR) technology, DOE did not, but
should have, included the costs
associated with ultra-low NOX
emissions requirements in its analysis.
Further, Rheem stated that given the
continued adoption of ultra-low NOX
requirements in highly-populated
regions such as California and Texas,
DOE should revise its baseline cost
estimates and include weighting for the
population subject to ultra-low NOX
regulations. (Rheem, No. 49 at p. 7)
A.O. Smith stated that the types of
burners currently used to comply with
the ultra-low NOX requirements in an
atmospheric water heater are much
more restrictive (i.e., produce higher
pressure drops) than conventional
burners. According to the commenter,
since gas-fired storage water heaters
complying with the ultra-low NOX
requirements also must comply with
FVIR requirements, the units must also
have flame arrestors on the air inlet,
which further restricts the system. To
boost the efficiency of ultra-low NOX
gas-fired storage water heaters,
manufacturers typically make the flue
baffle more effective. In certain
instances, given these additional
restrictions, the only way for some of
these units to continue to meet the
energy conservation standards is to add
a blower and/or power burner to the
heater, which would greatly increase the
manufacturing and installation costs.
(A.O. Smith, No. 37 at p. 9) SoCal Gas
agreed with the storage manufacturers,
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65881
stating that ultra-low NOX requirements
similar to those in the Southern
California Air Quality Management
District are being implemented in other
regions. SoCal Gas stated that ultra-low
NOX requirements necessitate a
different type of product, which creates
a cost issue because product costs and
cost increases are dramatically higher.
(SoCal Gas, Public Meeting Transcript,
No. 34.4 at pp. 41–42)
In response to the comments on the
preliminary analysis, DOE developed a
separate analysis for ultra-low NOX gasfired storage water heaters. DOE
developed cost-efficiency curves for
ultra-low NOX gas-fired storage water
heaters by performing a teardown
analysis (section IV.C.4.a) of several
ultra-low NOX products from a variety
of manufacturers at several efficiency
levels. More specifically, DOE analyzed
ultra-low NOX gas-fired storage water
heaters at a 40-gallon representative
storage volume, as was done for gasfired storage water heaters with a
standard burner. DOE then compared
the ultra-low NOX gas-fired storage
water heaters to the comparable gasfired storage water heaters that use
standard burner technology (i.e., not
ultra-low NOX compliant). DOE also
considered the impact of ultra-low NOX
regulations for the cumulative
regulatory burden (see section V.B.2.f).
DOE used the cost-efficiency curves
for ultra-low NOX gas-fired storage
water heaters in the downstream
analysis, including the LCC. DOE
distributed the costs based on those
geographical areas with ultra-low NOX
regulations. See chapter 5 of the NOPR
TSD for the cost-efficiency curves for
ultra-low NOX gas-fired storage water
heaters.
3. Efficiency Levels Analyzed
For each of the representative
products, DOE analyzed multiple
efficiency levels and estimated
manufacturer production costs at each
efficiency level. The following
subsections provide a description of the
full efficiency level range DOE analyzed
from the baseline efficiency level to the
maximum technologically feasible (maxtech) efficiency level for each product
class. In some cases, the highest
efficiency level was identified through
review of available product literature or
prototypes for products not
commercially available.
For each product class, DOE selected
baseline units as reference points,
against which DOE measured changes
resulting from potential amended
energy conservation standards.
Generally, the baseline unit in each
product class: (1) Represents the basic
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characteristics of equipment in that
class; (2) just meets current Federal
energy conservation standards; and (3)
provides basic consumer utility.
DOE conducted a survey of the
residential heating products market to
determine what types of products are
available to consumers and to identify
the efficiency levels corresponding to
the highest number of models. Then,
DOE established intermediate energy
efficiency levels for each of the product
classes that are representative of
efficiencies that are typically available
on the market or correspond to
voluntary program targets such as
ENERGY STAR. DOE reviewed AHRI’s
product certification directory,
manufacturer catalogs, and other
publicly-available literature to
determine which efficiency levels are
the most prevalent for each
representative product class.
DOE determined the maximum
improvement in energy efficiency that is
technologically feasible (max-tech) for
water heaters, DHE, and pool heaters, as
required by section 325(o) of EPCA. (42
U.S.C. 6295(o)). For the representative
product within a given product class,
DOE could not identify any working
products or prototypes at higher
efficiency levels that were currently
available beyond the identified maxtech level at the time the analysis was
performed. DOE seeks comment on its
max-tech efficiency levels.
Rheem commented generally in
response to the preliminary analysis
about the water heater max-tech levels
DOE identified. Rheem asserted that
there is little to no presence of max-tech
water heating products in the United
States. Further, Rheem commented that
it supports the growth of max-tech
products through ENERGY STAR,
which helps to distinguish topperforming products and to stimulate
market transformation, but the
commenter stated that max-tech should
not be considered for a Federal
minimum standard. (Rheem, No. 49 at
p. 2)
NRDC commented that max-tech
levels face issues that are similar for all
emerging technologies. It noted that: (1)
Max-tech products are only produced
and deployed on small scales, thereby
limiting available data; (2) reliability is
a concern, possibly due to small scale
production; (3) costs are high but
projected to decrease as production
increases, although timing is unknown;
(4) consumer reaction to new
technologies and their amenities is
unknown; and (5) units are more useful
only in certain applications due to size,
venting, or other inherent attributes.
NRDC notes that DOE must consider all
of these concerns when making a
decision. (NRDC, No. 48 at pp. 1–2)
As stated above, EPCA requires DOE
to determine the maximum
improvement in energy efficiency or
maximum reduction in energy use that
is technologically feasible for each class
of covered products. (42 U.S.C. 6295(o)).
Therefore, DOE must consider and
include an analysis of max-tech levels
for residential heating products in this
rulemaking. However, DOE notes that
consideration of the max-tech level does
not necessarily mean that it will be
adopted as the level in the energy
conservation standard for that product,
because DOE must consider, in turn, all
of the other statutory factors under 42
U.S.C. 6295(o).
In addition to identifying efficiency
levels for each product class, DOE
identified a particular technology or
combination of technologies associated
with each efficiency level in order to
make the engineering analysis more
transparent to interested parties. For
each efficiency level, DOE lists
technology and design changes
manufacturers could use to improve
product energy efficiency to achieve the
given efficiency level. These
technologies provide methods to
increase product energy and are
representative of technologies found in
a typical model at a given efficiency
level. While DOE recognizes that
manufacturers use many different
technologies and approaches to increase
the energy efficiency of residential
heating products, the presented
technologies and combinations of
technologies and their ordering are
simply possible paths manufacturers
could use to reach higher efficiency
levels.
a. Water Heaters
The current Federal minimum energy
conservation standards define the
baseline efficiencies for residential
water heaters as measured by the energy
factor. These standards became effective
on January 20, 2004. (10 CFR Part
430.32(d)) For water heaters, DOE
applied the representative storage
capacity to the energy efficiency
equations in 10 CFR Part 430.32(d) to
calculate the EFs of the baseline units.
i. Gas-Fired Storage Water Heaters
As described in section IV.C.2, DOE
performed a separate analysis for gasfired water heaters with a standard
burner and gas-fired water heaters with
an ultra-low NOX burner for this NOPR.
Table IV.11 and Table IV.12 show the
efficiency levels DOE considered for
gas-fired storage water heaters, along
with the technologies that
manufacturers could use to achieve the
listed efficiencies. The technologies for
standard burner gas-fired water heaters
and ultra-low NOX gas-fired water
heaters vary due to differences in the
operating characteristics of the burners.
Ultra-low NOX burners typically reduce
the pressure in the flue, which can
create problems if the pressures
required to properly vent combustion
products are not maintained. To
mitigate these problems, manufacturers
may reduce the amount of baffling or
other airflow restrictions to ensure
proper venting, which in turn may
result in decreased efficiency. To
overcome these issues, manufacturers
must use power venting technology to
achieve energy factors that are
comparable to what they would achieve
with a standard burner gas-fired storage
water heater that can contain more
baffling. Therefore, the technologies
associated with ultra-low NOX gas-fired
water heaters are implemented at lower
efficiency levels and yield a lower
energy factor than the same technologies
associated with gas-fired storage water
heaters that use a standard burner.
TABLE IV.11—FORTY-GALLON GAS-FIRED STORAGE WATER HEATER, STANDARD BURNER
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Efficiency level (EF)
Technology
Baseline (EF = 0.59) ................................................................................
Efficiency Level 1 (EF = 0.62) ..................................................................
Efficiency Level 2 (EF = 0.63) ..................................................................
Efficiency Level 3 (EF = 0.64) ..................................................................
Efficiency Level 4 (EF = 0.65) ..................................................................
Efficiency Level 5 (EF = 0.67) ..................................................................
Efficiency Level 6¥Max-Tech (EF = 0.80) ..............................................
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Standing Pilot and 1″ Insulation.
Standing Pilot and 1.5″ Insulation.
Standing Pilot and 2.0″ Insulation.
Electronic Ignition, Power Vent and 1″ Insulation.
Electronic Ignition, Power Vent and 1.5″ Insulation.
Electronic Ignition, Power Vent and 2″ Insulation.
Condensing, Power Vent, 2″ Insulation.
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TABLE IV.12—FORTY-GALLON GAS-FIRED STORAGE WATER HEATER, ULTRA-LOW NOX BURNER
Efficiency level (EF)
Technology
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Baseline (EF = 0.59) ................................................................................
Efficiency Level 1 (EF = 0.62) ..................................................................
Efficiency Level 2 (EF = 0.63) ..................................................................
Efficiency Level 3 (EF = 0.64) ..................................................................
Efficiency Level 4 (EF = 0.65) ..................................................................
Efficiency Level 5 (EF = 0.67) ..................................................................
Efficiency Level 6¥Max-Tech (EF = 0.80) ..............................................
DOE found gas-fired storage water
heaters capable of condensing
operations at the highest efficiency level
(i.e., max-tech). More energy can be
extracted by condensing the combustion
products in the flue gas, which extracts
more heat in the form of latent energy,
leading to an increase in the thermal
efficiency of the gas-fired storage water
heater. In the preliminary analysis, DOE
identified the max-tech EF for
condensing gas-fired storage water
heaters as 0.77. DOE received several
comments from interested parties
(discussed below) which have caused
DOE to revise its estimate upwards to
0.80 EF for condensing units.
NRDC stated that condensing gas-fired
water heaters are the future of gas-fired
storage water heaters. (NRDC, No. 48 at
p. 1) ACEEE commented that the maxtech efficiency level DOE considered for
gas-fired storage water heaters is lower
than the ENERGY STAR level for the
condensing storage water heater
category, which is set at 0.80 EF. ACEEE
stated that selecting 0.77 EF from a
range of identified energy factors for
condensing gas-fired storage water
heaters ranging from 0.77 to 0.82 EF will
bias the results of the analysis and that
the five percentage points of the energy
factor correspond to less gas usage.
ACEEE expressed concern with such a
divergence between ENERGY STAR and
the energy conservation standards
rulemaking. (ACEEE, Public Meeting
Transcript, No. 34.4 at p. 75–76)
Further, ACEEE recommended that DOE
analyze efficiency levels at 0.77 EF, 0.80
EF, and 0.82 EF for gas-fired storage
water heaters (ACEEE, No. 35 at p. 3)
ASAP stated that DOE’s analysis may be
missing some efficiency levels. For gasfired storage water heaters in particular,
ASAP commented that condensing units
may span a range of efficiencies, and a
0.77 EF may be an intermediate level
that is not max-tech. (ASAP, Public
Meeting Transcript, No. 34.4 at p. 92)
A.O. Smith stated its support for the
max-tech efficiency levels for water
heaters as shown in the preliminary
engineering analysis. Specifically, A.O.
Smith supports a 0.77 EF for gas-fired
condensing water heaters, which meets
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Standing Pilot and 2″ Insulation.
Electronic Ignition, Power Vent, and 1″ Insulation.
Electronic Ignition, Power Vent and 1.5″ Insulation.
Electronic Ignition, Power Vent and 2″ Insulation.
Not Attainable (would go to condensing).
Condensing, Power Vent, 2″ Insulation.
DOE’s criteria of being technically
feasible. (A.O. Smith, No. 37 at p. 3)
In selecting the efficiency level for the
max-tech condensing gas-fired water
heater for the NOPR analysis, DOE
carefully considered all comments from
interested parties regarding this issue.
There are no products currently
available on the residential gas-fired
storage water heater market that can
achieve the efficiencies that will be
made possible by condensing
technology, and, therefore, it is difficult
to determine the highest possible EF
that can be achieved using this
technology. Although condensing gasfired storage water heaters are not
currently available on the market in
residential sizes, they are available in
commercial sizes that could be scaled
down for residential use. Commercial
condensing gas-fired storage water
heaters have efficiencies of up to 96
percent thermal efficiency. There is no
direct mathematical conversion that can
be used to derive energy factor (the
efficiency metric for residential water
heaters) from thermal efficiency (the
efficiency metric used for commercial
water heaters). Therefore, in making the
determination of a max-tech level for
gas-fired storage water heaters, DOE
considered feedback from interested
parties, information gathered during
manufacturer interviews, available
reports and literature, and its own
technical expertise. As a result, DOE has
revised the max-tech water heater
efficiency to 0.80 EF for the NOPR
analysis. This level is cited as the maxtech for condensing water heaters in
several reports reviewed by DOE
(described in more detail below), and
DOE believes it is the maximum
possible energy factor that can possibly
be achieved by a gas-fired storage water
heater at this time. DOE notes that A.O.
Smith presentation given at the 2009
ACEEE Hot Water Forum identifies 0.80
EF as the maximum possible EF for
residential condensing gas-fired water
heaters. For more information visit
https://www.aceee.org; the presentation
is available at: https://www.aceee.org/
conf/09whforum/PlenarySession1AdamsPresentation.pdf.
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In addition, the Super Efficient Gas
Water Heating Appliance Initiative
(SEGWHAI) Final Project Report (April
2007) identified efficiency factors at
0.80 and above as achievable
condensing efficiency levels for gasfired storage water heaters, although
these levels were based on theoretical
modeling of gas-fired water heaters and
have never been demonstrated in
working prototypes. For more
information, visit https://
www.segwhai.org. A 0.80 EF level is also
consistent with the max-tech level
identified by ENERGY STAR in its
determination of an appropriate
efficiency level for gas-fired storage
water heaters utilizing condensing
technology. For more information, visit
https://www.energystar.gov. As
explained above, DOE seeks comment
on the max-tech efficiency levels
identified for the analyses, especially
those for gas-fired water heaters. (See
Issue 1 under ‘‘Issues on Which DOE
Seeks Comment’’ in section VII.E of this
NOPR.)
DOE received several comments about
the other efficiency levels and
technologies identified for the
preliminary analysis.
Southern commented on the
technologies for efficiency level 3 for
gas-fired storage water heaters, stating
its belief that adding electronic ignition
would not require manufacturers to use
power vent systems. (Southern, Public
Meeting Transcript, No. 34.4 at p. 87)
DOE agrees with Southern’s comment,
because an assessment of the current
market demonstrates that gas-fired
storage water heaters using electronic
ignition systems do not always include
power vent technologies. However, DOE
believes many manufacturers that use
power vent technologies to reach
efficiency level 3, 4, and 5 also use
electronic ignition systems since the fan
already requires electricity. Therefore,
DOE paired electronic ignition and
power venting technologies with one
inch of insulation as a potential
approach to achieving efficiency level 3.
DOE believes that manufacturers
implement designs that have both
electronic ignition and power vent
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technology at this efficiency level. At
efficiency levels 1 and 2, DOE used
standing pilot systems for gas-fired
storage water heaters, which do not
require line electricity. Even though
efficiency level 3 and above for gas-fired
storage water heaters would require
consumers to have an external electrical
connection, DOE has determined that
consumers would continue to have
other non-electrical alternatives such as
other types of gas-fired water heaters
(e.g., gas-fired instantaneous water
heaters).
ACEEE stated that DOE should
include an efficiency level that
considers flue and vent damper
technologies instead of power vent
technology. The commenter stated that
this may not significantly affect the
energy factor because the test procedure
does not account for the value of
entrained bypass air. ACEEE asserted
that flue and vent dampers may have
much lower costs than power vents and
may have less entrained air. Further,
ACEEE stated that flue and vent
dampers do not require exhaust
temperatures to be reduced to a level
that can be handled by PVC plastics.
(ACEEE, Public Meeting Transcript, No.
34.4 at p. 88)
DOE focused its analysis on
technologies that would impact
efficiency, as measured by the DOE test
procedure. DOE discussed its
consideration of damper technologies as
part of the screening analysis in section
IV.B.1.a. For the engineering analysis,
DOE examined the most common
methods used by manufacturers to
improve energy factor, as determined
using DOE’s test procedures specified in
10 CFR part 430, subpart B, appendix E.
Through its reverse-engineering
analysis, and review of manufacturer
literature, DOE found that
manufacturers most often use power
vent technology to achieve higher
efficiency for gas-fired storage water
heaters. Thus, DOE considered
efficiency levels that are typically
achieved using a power vent design in
the NOPR analysis.
Rheem commented that at the
preliminary analysis efficiency level 5
(i.e., 0.66 EF), gas-fired storage water
heaters may require operation at and
near condensing efficiency levels,
which can be undesirable. (Rheem, No.
49 at p. 4)
DOE notes that several manufacturers
already manufacture water heaters at
0.66 EF, making gas-fired storage water
heaters at 0.66 EF practical to
manufacture, install, and service, and
technologically feasible. DOE is
unaware of any adverse impacts to
either product utility or health and
safety that would result from a water
heater at 0.66 EF. DOE reviewed the
market for gas-fired water heaters at 0.66
EF and 0.67 EF. DOE did not find any
products currently on the market, which
incorporate features to accommodate
condensing operation. Therefore, DOE
sees no reason to eliminate that
efficiency level from consideration.
However, DOE did revise efficiency
level 5 from 0.66 EF for the preliminary
analysis to 0.67 EF for the NOPR
analysis to maintain consistency with
the ENERGY STAR Program. DOE notes
there are also products currently offered
with a 0.67 EF at the representative
volume size.
Rheem also stated that the
technologies identified to increase
energy efficiency for gas-fired storage
water heaters are appropriate. However,
Rheem asserted that the insulation
thicknesses that would be required to
achieve efficiency levels 1, 2, and 3 are
understated. Rheem commented that
efficiency level 1 requires 2 to 2.5
inches of insulation, for example.
(Rheem, No. 49 at p. 4)
DOE research suggests that the tank
thicknesses listed at various efficiency
levels are consistent with products
available on the market. DOE reviewed
manufacturer literature, which typically
includes information on energy factor
and insulation thicknesses. For the
preliminary analysis, DOE reverseengineered several gas-fired water
heaters to verify the technologies used
to improve energy efficiency, including
insulation thicknesses. Since the
preliminary analysis, DOE also hired an
independent testing facility to
determine the EF of a representative
sample of water heaters across multiple
efficiency levels for the NOPR. These
water heaters were subsequently
disassembled to verify the technologies
used to increase energy efficiency. In
the end, DOE came to the same
conclusions as in the preliminary
analysis regarding insulation
thicknesses. Therefore, DOE believes the
results of its assessment of insulation
thicknesses at various efficiency levels
are accurate.
Rheem also commented that baseline
technologies for 40-gallon gas-fired
storage water heaters do not apply
uniformly for the entire range of rated
storage volumes, and as such, DOE
should account for the additional
manufacturing, installation, and
shipping costs for larger size water
heaters. (Rheem, No. 49 at p. 4)
For the NOPR engineering analysis,
DOE performed teardowns of models at
multiple nominal capacities and noted
any differences (including minor
differences) that occurred. DOE used the
knowledge gained from these teardowns
when it extended the cost analysis to
the other capacity (gallon) sizes. As part
of its analysis, DOE accounted for
additional installation costs and
shipping costs of larger units (see
sections IV.E.2.a and IV.C.4.f,
respectively).
ii. Electric Storage Water Heaters
Table IV.13 shows the efficiency
levels considered for electric storage
water heaters, along with their
corresponding potential technologies
that could be used to achieve those
levels.
TABLE IV.13—FIFTY-GALLON ELECTRIC STORAGE WATER HEATER
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Efficiency level (EF)
Technology
Baseline (EF = 0.90) ................................................................................
Efficiency Level 1 (EF = 0.91) ..................................................................
Efficiency Level 2 (EF = 0.92) ..................................................................
Efficiency Level 3 (EF = 0.93) ..................................................................
Efficiency Level 4 (EF = 0.94) ..................................................................
Efficiency Level 5 (EF = 0.95) ..................................................................
Efficiency Level 6 (EF = 2.0) ....................................................................
Efficiency Level 7¥Max-Tech (EF = 2.2) ................................................
For electric storage water heaters,
although no integrated heat pump water
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1.5″ Foam Insulation.
2″ Foam Insulation.
2.25″ Foam Insulation.
2.5″ Foam Insulation.
3″ Foam Insulation.
4″ Foam Insulation.
Heat Pump Water Heater.
Heat Pump Water Heater, More Efficient Compressor.
heaters were available on the market at
the time the analysis was developed,
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such products had been developed and
manufactured in the past, three models
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have been certified under the ENERGY
STAR program, and others are currently
under development by other water
heater manufacturers. DOE found
electric heat pump water heaters
capable of obtaining EFs of 2.2 in the
preliminary analysis and retained this
level as the max-tech level in the NOPR
analysis. DOE received several
comments on the efficiency levels and
technologies presented in the
preliminary analysis.
NRDC commented that heat pump
water heaters are the future of electric
storage water heater technology. (NRDC,
No. 48 at p. 1) ASAP stated that DOE
may be missing some efficiency levels
in its analysis. ASAP commented that
an efficiency level between efficiency
level 5 and the max-tech for electric
storage water heaters may merit
analysis, particularly if ENERGY STAR
has a heat pump water heater at 2.0 EF.
(ASAP, Public Meeting Transcript, No.
34.4 at p. 92) Similarly, ACEEE
recommended DOE analyze levels at 1.7
EF, 2.0 EF, and 2.2 EF. (ACEEE, No. 35
at p. 3) Additionally, ACEEE stated that
prior analyses have been conducted for
heat pump water heaters at 2.5 EF,
although further specifics were not
provided. (ACEEE, Public Meeting
Transcript, No. 34.4 at p. 94) BWC
referred DOE to comments made during
the previous residential water heater
rulemaking on July 18, 1994. (BWC, No.
46 at p. 2) BWC asserted that the
previous rulemaking stated a reasonable
energy factor of 1.50, but that the
current rulemaking does not. BWC
stated its belief that 1.5 EF is still a
reasonable EF for heat pump water
heaters. (BWC, No. 46 at p. 2)
In response to these comments, DOE
revised the efficiency levels considered
for electric storage water heaters to
include an intermediate heat pump
water heater efficiency level at 2.0 EF
for the NOPR analysis. This is not the
max-tech level, but it does represent a
significant change in technology and
increase in efficiency over the
traditional electric storage heater
technology. This technology would also
be easier for manufacturers to achieve
than the max-tech 2.2 EF. DOE notes
this efficiency level also corresponds to
the level set forth by the ENERGY STAR
program. DOE did not find any heat
pump water heaters currently available
or in the research stage with a 1.7 EF.
In addition, DOE believes it is unlikely
that manufacturers will offer products
below the ENERGY STAR level, which
is at 2.0 EF. Currently, there are also
Federal tax credits for heat pump water
heaters with an energy factor greater
than or equal to 2.0 EF. Additionally,
DOE maintained 2.2 EF as the max-tech
efficiency level. Although ACEEE
commented that analysis has been
performed on heat pump water heaters
with EFs of up to 2.5, ACEEE did not
indicate the source of this analysis, and
DOE could not identify any heat pump
water heaters at 2.5 EF through its
research efforts. The highest EF
obtained in prototype designs currently
being developed is 2.2 EF.
In response to the technology options
presented in the preliminary analysis,
AHRI stated that increasing the
insulation on an electric storage water
heater from 3 to 4 inches would not
increase the energy factor of such
magnitude by 0.01 EF point. AHRI does
not believe that an increase in the
energy factor would be seen using
DOE’s test procedure when only the
insulation thickness is increased and no
other design changes are made to
eliminate many of the thermal short
65885
circuits present in a water heater.
(AHRI, Public Meeting Transcript, No.
34.4 at pp. 90–91) Rheem also
commented that DOE should recognize
that there are diminishing returns for
added foam insulation, adding that it is
unclear how the efficiency levels for
electric storage water heaters with 3 and
4 inches of insulation were evaluated to
yield the proposed efficiency levels.
(Rheem, No. 49 at p. 3)
DOE research determined the
technology options manufacturers
typically use to improve product
efficiency, and was based on multiple
data sources including manufacturer
literature, which usually includes
information on energy factor and
insulation thicknesses. DOE also
conducted a teardown analysis of
electric storage water heaters for the
preliminary analysis. For the NOPR
analysis, DOE tested the EF of water
heaters and then performed a teardown
analysis on those water heaters across
various EF ratings to confirm the
technologies used for increasing
efficiency. Although insulation
thickness is not the only design change,
DOE believes it is the driving factor in
increasing the EF for electric storage
water heaters, and, therefore, is listed as
a commonly used technology option.
For these reasons, DOE did not revise
the technology options for EL4 and EL
5 for electric storage water heaters for
the NOPR analysis.
iii. Oil-Fired Storage Water Heaters
Table IV.14 presents the efficiency
levels DOE considered for oil-fired
storage water heaters, along with the
technology options that manufacturers
could use to achieve the listed
efficiency.
TABLE IV.14—THIRTY-TWO-GALLON OIL-FIRED STORAGE WATER HEATER WITH BURNER ASSEMBLY
Efficiency level (EF)
Technology
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Baseline (EF = 0.53) ................................................................................
Efficiency Level 1 (EF = 0.54) ..................................................................
Efficiency Level 2 (EF = 0.56) ..................................................................
Efficiency Level 3 (EF = 0.58) ..................................................................
Efficiency Level 4 (EF = 0.60) ..................................................................
Efficiency Level 5 (EF = 0.62) ..................................................................
Efficiency Level 6 (EF = 0.66) ..................................................................
Efficiency Level 7¥Max-Tech (EF = 0.68) ..............................................
The most efficient residential oil-fired
storage water heater on the market has
an EF of 0.68 and includes electronic
ignition, foam insulation, and enhanced
flue baffles. DOE considered this
efficiency level in the preliminary
analysis and did not revise it for the
NOPR analysis. However, DOE has
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1″ Fiberglass Insulation.
1.5″ Fiberglass Insulation.
2″ Fiberglass Insulation.
2.5″ Fiberglass Insulation.
2″ Foam Insulation.
2.5″ Foam Insulation.
1″ Fiberglass Insulation, and Multi Flue Design.
1″ Foam Insulation, and Multi Flue Design.
determined that all oil-fired water
heaters currently manufactured at the
max-tech efficiency level incorporate a
proprietary design. While DOE typically
does not consider proprietary designs in
its analysis due to impacts on
competition likely to result from setting
a minimum standard an efficiency level
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that is only achievable using a
proprietary design, the agency has
determined through discussions with
manufacturers and its own technical
expertise that the max-tech level for oilfired storage water heaters is achievable
using alternative approaches that are not
proprietary. Therefore, DOE included
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this efficiency level in the NOPR
analysis. DOE believes manufacturers of
oil-fired storage water heaters could
achieve an EF of 0.68 by using a
multiple flue design consisting of
several flues to increase the heat transfer
area, instead of a single, central flue that
is standard on nearly all residential gasfired and oil-fired storage water heaters.
DOE revised its cost analysis for a 0.66
EF and 0.68 EF to represent a nonproprietary, multiple flue design.
DOE did not receive any comments in
response to the preliminary analysis on
the max-tech efficiency level or the
other efficiency levels DOE considered
for oil-fired storage water heaters. See
chapter 5 of the NOPR TSD for more
information about the efficiency levels
DOE analyzed for oil-fired storage water
heaters.
iv. Gas-Fired Instantaneous Water
Heaters
Table IV.15 presents the efficiency
levels DOE considered for gas-fired
instantaneous water heaters, along with
their corresponding potential
technologies.
TABLE IV.15—ZERO-GALLON GAS-FIRED INSTANTANEOUS WATER HEATER, 199,000 BTU/H INPUT CAPACITY
Efficiency level (EF)
Technology
Baseline (EF = 0.62) ................................................................................
Efficiency Level 1 (EF = 0.69) ..................................................................
Efficiency Level 2 (EF = 0.78) ..................................................................
Efficiency Level 3 (EF = 0.80) ..................................................................
Efficiency Level 4 (EF = 0.82) ..................................................................
Efficiency Level 5 (EF = 0.84) ..................................................................
Efficiency Level 6 (EF = 0.85) ..................................................................
Standing Pilot.
Standing Pilot and Improved Heat Exchanger Area.
Electronic Ignition and Improved Heat Exchanger.
Electronic Ignition and Power Vent.
Electronic Ignition, Power Vent, Improved Heat Exchanger Area.
Electronic Ignition, Power Vent, and Improved Heat Exchanger Area.
Electronic Ignition, Power Vent, Direct Vent, and Improved Heat Exchanger Area.
Electronic Ignition, Power Vent, Direct Vent, Condensing.
Electronic Ignition, Power Vent, Direct Vent, Condensing (Max-Tech).
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Efficiency Level 7 (EF = 0.92) ..................................................................
Efficiency Level 8 ¥ Max Tech (EF = 0.95) ............................................
For the preliminary analysis, DOE
identified a gas-fired instantaneous
water heater capable of condensing with
an EF of 0.92 as the max-tech level. DOE
did not receive any comments on the
max-tech gas-fired instantaneous water
heaters. However, on reviewing the gasfired instantaneous water heater market,
DOE identified a new max-tech level at
0.95 EF for instantaneous gas-fired
water heaters that use condensing
technology.
DOE received several comments on
the potential technologies incorporated
at each efficiency level for gas-fired
instantaneous water heaters that were
presented in its preliminary engineering
analysis. For the preliminary analysis,
DOE considered the baseline to be the
current Federal minimum standard (i.e.,
0.62 EF). Also, DOE did not incorporate
the need to handle condensate into the
installed cost estimates until products
reached the 0.92 efficiency level for the
preliminary analysis.
A.O. Smith suggested using a higher
EF as the baseline efficiency level for
gas-fired instantaneous water heaters.
A.O. Smith noted that the vast majority
of models available (per the AHRI
Directory) are already well above the
Federal minimum energy conservation
standards of 0.62 EF. Since the majority
of shipments in the current market for
tank-type water heaters are at the
Federal minimum energy conservation
standards, DOE should use the same
logic in choosing the baseline efficiency
levels. (A.O. Smith, No. 37 at p. 3)
In response, DOE defines the baseline
efficiency level as representative of the
basic characteristics of equipment in
that class. The characteristics of a gas-
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fired instantaneous water heater that
just meets the 0.62 EF requirement
would be representative of the most
basic design that could be used for a
gas-fired instantaneous water heater.
Therefore, DOE did not change the
baseline efficiency level for gas-fired
instantaneous water heaters in the
NOPR analysis.
At the public meeting for the
preliminary analysis, DOE sought
comment on safety concerns for gasfired instantaneous water heaters at
near-condensing efficiency levels.
Operating at near-condensing levels
may result in corrosive condensation
formation, which may occur when the
combustion products (which include
water vapor) cool and condense.
Manufacturers stated during engineering
interviews that there is a safety margin
needed to account for variations due to
manufacturing tolerances, gas quality,
differences in venting configurations,
altitude, ambient conditions, and
installer experience. DOE specifically
requested information about how
manufacturers would change current
designs to mitigate corrosive condensate
formation at near-condensing EF levels
that may be present in some
installations. DOE also requested
comment about how manufacturers
would alter current designs of gas-fired
instantaneous water heaters to achieve
safe operation if a potential amended
standard required all installations to
operate at near-condensing EF levels.
In response, Noritz stated that 0.83 EF
is generally the borderline between
condensing and non-condensing, the
point at which units begin operating in
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condensing mode in at least some
applications. (Noritz, Public Meeting
Transcript, No. 34.4 at p. 113) Noritz
also stated that condensation may occur
in the near condensing range, which
includes 0.83, 0.84, and 0.85 EF, and
that it would change the copper heat
exchanger in its standard product to
stainless steel or better to manage the
acidic condensate. (Noritz, Public
Meeting Transcript, No. 34.4 at pp. 108–
109) Noritz recommends that
contractors install a condensate
collector for instantaneous gas-fired
water heaters with energy factors at 0.82
and 0.83, but acknowledged that the
condensate collector is not included in
a large percentage of installations.
Therefore, Noritz stated that it would
include a stainless steel heat exchanger
with the condensate collector on higher
efficiency products because of the
increased safety issues associated with
condensate management. (Noritz, Public
Meeting Transcript, No. 34.4 at pp. 111–
112) Further, Noritz said it would use
this stainless steel heat exchanger
nationwide for cost considerations and
to keep the product standard. (Noritz,
Public Meeting Transcript, No. 34.4 at
pp. 109–110) Noritz commented that it
handles acidic condensation with a
stainless steel heat exchanger for the
condensing instantaneous gas-fired
water heater that has an energy factor of
0.92 EF, and that the product uses a
primary copper heat exchanger and a
secondary stainless steel heat
exchanger. Noritz commented that some
companies may use titanium, but this
may not be realistic for Noritz because
of the cost. (Noritz, Public Meeting
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Transcript, No. 34.4 at pp. 109–110) In
written comments, Noritz suggested that
DOE’s cost-efficiency curve should be
continuous from 0.62 to 0.82, at which
point there should be a kink in the
curve, and the cost of producing a
product with an EF of 0.83 or higher
would see a steep increase. According to
the commenter, the delineation between
condensing and non-condensing
product gas-fired instantaneous water
heaters is at an EF of 0.83, which is
borderline. Noritz asserted that
manufacturers making products with an
EF of 0.83 or above would need to
design these products to deal with
condensate, thereby requiring more
expensive heat exchanger materials,
condensate drains, and some method of
treating (i.e., neutralizing) the
condensate for safe disposal. (Noritz,
No. 36 at pp. 1–2)
Similar to Noritz’s comments, AHRI
noted that the costs of gas-fired
instantaneous water heaters at nearcondensing efficiency levels (i.e., an EF
of 0.84 and 0.85) need to include the
measures manufacturers would use to
minimize problems associated with
excessive condensate in the appliance
or its venting system. Specifically, AHRI
noted that manufacturers must build
safety factors into their designs to
address the wide scope of installation
conditions, such as colder incoming
water temperatures or various venting
systems. AHRI recommended that DOE
model the heat exchanger using more
corrosive-resistant materials, specifying
a venting system using stainless steel,
and adding a means to collect and
dispose of condensate. (AHRI, No. 43 at
p. 2) Regarding manufacturing products
that operate near their condensing
levels, AHRI stated that manufacturers
want to build products that can be sold
anywhere in the United States.
However, there are parts of the United
States where the incoming water is
colder than the water specified by the
test procedure, and this may cause precondensing. AHRI asserted that
efficiency levels at these levels create
safety issues, and that manufacturers
would have to rely on manufacturing
and installation skills due to the small
margin between condensing and noncondensing operation. (AHRI, Public
Meeting Transcript, No. 34.4 at pp. 110–
111)
DOE acknowledges that for efficiency
levels associated with near-condensing
operation, a portion of the flue products
may condense, and this percentage may
vary as a function of field conditions.
Additionally, operation where a portion
of the flue gases condense (i.e., nearcondensing operation) creates the same
safety issues associated with fully
condensing operation because corrosive
condensate is introduced into the heat
exchanger and venting system during
both types of operation. Therefore, DOE
determined that for instantaneous gasfired water heater efficiency levels 5 and
6 (energy factors 0.84 and 0.85,
respectively), the costs associated with
condensing operation should be
65887
accounted for in the MPCs. DOE revised
its costs for the NOPR phase of this
analysis for gas-fired instantaneous
water heaters to account for design
changes necessary to handle condensate
at these efficiency levels.
b. Direct Heating Equipment
The baseline efficiencies for DHE are
defined by the current Federal
minimum energy conservation
standards and the representative
characteristics for products on the
market that just meet Federal minimum
energy conservation standards, as
measured by the AFUE, and effective on
January 1, 1990. (10 CFR part 430.32(i))
For DHE, the AFUEs corresponding to
the representative input ratings in 10
CFR 430.32(i) were assigned as the
baseline unit AFUEs.
Table IV.16 through Table IV.20 show
the efficiency levels DOE analyzed for
each product class of DHE, along with
technologies that manufacturers could
use to reach that efficiency level.
In the preliminary analysis, DOE
identified various efficiency levels for
gas wall fan DHE, including max-tech
levels that used electronic ignition and
induced draft combustion systems. DOE
did not receive any comments
pertaining to its efficiency levels or
technologies for the preliminary
analysis. After reviewing the efficiency
levels and technologies for the NOPR
analysis, DOE determined that the same
efficiency levels and technologies are
still appropriate.
TABLE IV.16—GAS WALL FAN-TYPE DHE, OVER 42,000 BTU/H
Efficiency level (AFUE)
Technology
Baseline (AFUE = 74) ..............................................................................
Efficiency Level 1 (AFUE = 75) ................................................................
Efficiency Level 2 (AFUE = 76) ................................................................
Efficiency Level 3 (AFUE = 77) ................................................................
Standing Pilot.
Intermittent Ignition and Two-Speed Blower.
Intermittent Ignition and Improved Heat Exchanger.
Intermittent Ignition, Two-Speed Blower, and Improved Heat Exchanger.
Induced Draft and Electronic Ignition.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Efficiency Level 4¥Max-Tech (AFUE = 80) ............................................
In the preliminary analysis, DOE
identified gas wall gravity efficiency
levels and technology options, which
included a 75-percent AFUE level as the
max-tech that could be achieved using
induced draft. DOE received several
comments in response.
AHRI cautioned that adding too many
electrical devices to gas wall gravitytype DHE will at some point remove
those products from that product class,
because they will get converted into gas
wall fan-type DHE. (AHRI, Public
Meeting Transcript, No. 34.4 at pp. 69–
70) AHRI also stated that an external
electrical supply is required at some of
the higher efficiency levels. AHRI
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asserted that when this occurs, that
product can no longer be classified as a
gravity-type product, but instead would
be a fan-type product. Therefore, AHRI
stated that the efficiency levels
presented in the preliminary analysis
are unrealistic for gas wall gravity-type
DHE. (AHRI, Public Meeting Transcript,
No. 34.4 at pp. 114–115) Additionally,
Bock commented that adding induced
draft technology to a gas wall gravitytype unit would exclude it from this
equipment class. (Bock, Public Meeting
Transcript No. 34.4 at p. 119)
In response to these comments, DOE
further reviewed the gravity-type wall
DHE market and the available products
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and technologies for the NOPR analyses.
A ‘‘vented wall furnace’’ (i.e., gas wall
fan-type or gravity-type DHE) is defined
as a vented heater that furnishes heat air
circulated either by gravity or by a fan.
10 CFR 430.2. Gravity-type and fan-type
wall DHE are differentiated only by the
inclusion (fan-type) or exclusion
(gravity-type) of a fan from the design.
DOE agrees with Bock that the addition
of an induced draft fan (which forces
the combustion products through the
heat exchanger to increase turbulence
and, thus, heat transfer) would cause
those products to be excluded from the
wall gravity product class. Thus, for the
NOPR analysis, DOE removed the
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efficiency level at 75 AFUE that
corresponded to induced draft
technology. Instead, DOE identified 72
AFUE as the max-tech efficiency level,
which can be attained using electronic
ignition technology.
TABLE IV.17—GAS WALL GRAVITY-TYPE DHE, OVER 27,000 BTU/H AND UP TO 46,000 BTU/H
Efficiency level (AFUE)
Technology
Baseline (AFUE = 64) ..............................................................................
Efficiency Level 1 (AFUE = 66) ................................................................
Efficiency Level 2 (AFUE = 68) ................................................................
Efficiency Level 3 (AFUE = 71) ................................................................
Efficiency Level 4¥Max Tech (AFUE = 72) ............................................
In the preliminary analysis, DOE
analyzed several efficiency levels for gas
floor DHE, ranging from 57 AFUE up to
75 AFUE. DOE chose these levels based
on the product availability listings
contained in manufacturer specification
sheets and DOE’s previous analysis for
direct heating equipment. However, for
the NOPR, DOE conducted another
review of the current market and
Standing Pilot.
Standing Pilot and Improved Heat Exchanger.
Standing Pilot and Improved Heat Exchanger.
Standing Pilot and Improved Heat Exchanger.
Electronic Ignition.
determined that the market no longer
offers models above 58 percent AFUE.
This assessment was based on a review
of updated information from AHRI
Directory of Certified Products and
manufacturer specification sheets. In its
review, DOE identified heat exchanger
improvements as a potential design
approach to achieve the max-tech level
58 AFUE. DOE could not find any
prototypes being developed above 58
percent AFUE. Accordingly, DOE based
the efficiency levels for the NOPR
analyses on those levels known to be
technologically feasible for this product
class and DOE only analyzed the
baseline and max-tech efficiency levels,
because no products are available at any
other efficiency levels (See Table
IV.18.).
TABLE IV.18—GAS FLOOR-TYPE DHE, OVER 37,000 BTU/H
Efficiency level (AFUE)
Technology
Baseline (AFUE = 57) ..............................................................................
Efficiency Level 1¥Max Tech (AFUE = 58) ............................................
In the preliminary analysis, DOE
included gas hearth DHE in the analysis
for gas room DHE. For the NOPR
analysis, DOE is establishing a separate
product class for gas hearth DHE.
Consequently, DOE revised the
efficiency levels analyzed for gas room
DHE to represent the market and
technologies available for products,
Standing Pilot.
Standing Pilot and Improved Heat Exchanger.
excluding those that are now gas hearth
DHE, based upon the characteristics of
the fireplace and DOE’s proposed
definition for ‘‘gas hearth DHE.’’ This
resulted in the elimination of several
efficiency levels that were considered in
the preliminary analysis for gas room
DHE. Also, the max-tech efficiency level
has changed for the NOPR because of
this restructuring of the DHE product
classes. For room heaters, the use of
electronic ignition and multiple heat
exchangers has been identified as a
possible approach to reach the max-tech
efficiency level (AFUE = 83). These
technologies are being used in room
heaters that are currently on the market.
TABLE IV.19—GAS ROOM-TYPE DHE, OVER 27,000 BTU/H AND UP TO 46,000 BTU/H
Efficiency level (AFUE)
Technology
Baseline (AFUE = 64) ..............................................................................
Efficiency Level 1 (AFUE = 65) ................................................................
Efficiency Level 2 (AFUE = 66) ................................................................
Efficiency Level 3 (AFUE = 67) ................................................................
Efficiency Level 4 (AFUE = 68) ................................................................
Efficiency Level 5¥Max Tech (AFUE = 83) ............................................
DOE did not analyze a gas hearth DHE
product class separately in the
preliminary analysis. Based upon public
comment, for the NOPR analysis, DOE
Standing Pilot.
Standing Pilot and Improved Heat Exchanger.
Standing Pilot and Improved Heat Exchanger.
Standing Pilot and Improved Heat Exchanger.
Standing Pilot and Improved Heat Exchanger.
Electronic Ignition and Multiple Heat Exchanger Design.
surveyed the residential gas hearth DHE
market to identify technologies and
efficiency levels common to gas hearth
DHE. For gas hearth DHE, DOE
identified products capable of
condensing operations and rated at 93
AFUE as the max-tech level.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
TABLE IV.20—GAS HEARTH DHE, OVER 27,000 BTU/H AND UP TO 46,000 BTU/H
Efficiency level (AFUE)
Technology
Baseline (AFUE = 64) ..............................................................................
Efficiency Level 1 (AFUE = 67) ................................................................
Efficiency Level 2 (AFUE = 72) ................................................................
Efficiency Level 3¥Max Tech (AFUE = 93). ...........................................
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Electronic Ignition.
Fan Assisted.
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c. Pool Heaters
The baseline efficiencies for pool
heaters were defined by the current
Federal minimum energy conservation
standards and the representative
characteristics for products on the
market that just meet Federal minimum
energy conservation standards, as
measured by thermal efficiency and
effective on January 1, 1990. (10 CFR
430.32(k)) For pool heaters, the thermal
efficiency corresponding to the baseline
unit is 78 percent. Id.
DOE analyzed efficiency levels for
pool heaters with standing pilot
ignitions and pool heaters with
electronic ignitions for the preliminary
analysis. DOE distinguished between
the two ignition systems because of the
energy use difference between
electronic ignition and standing pilot
systems. The DOE test procedure does
not fully include the energy use by a
standing pilot systems in the thermal
efficiency metric, but DOE accounted
for the energy use difference between
electronic ignition and standing pilot
systems in its consumer LCC analysis.
DOE did not receive any comments in
response to the preliminary analysis
that opposed this approach, and,
therefore, DOE continues to use it for
65889
the NOPR analysis. After surveying the
pool heater market, DOE determined
that electronic ignition is offered in
products covering the whole range of
efficiencies, while standing pilot
ignition systems are only offered in
products corresponding to the first three
intermediate efficiency levels.
Consequently, DOE developed two
baseline products and two efficiency
pathways for efficiency levels 1 through
3.
For the NOPR analysis, DOE
examined the same efficiency levels as
it did in the preliminary analysis (see
Table IV.21).
TABLE IV.21—GAS-FIRED POOL HEATER, 250,000 BTU/H
Efficiency level (thermal efficiency)
Technology
Baseline (Thermal Efficiency = 78) * ........................................................
Efficiency Level 1 (Thermal Efficiency = 79) * ..........................................
Efficiency Level 2 (Thermal Efficiency = 81) * ..........................................
Efficiency Level 3 (Thermal Efficiency = 82) * ..........................................
Efficiency
Efficiency
Efficiency
Efficiency
Efficiency
Level
Level
Level
Level
Level
4 (Thermal Efficiency = 83) ............................................
5 (Thermal Efficiency = 84) ............................................
6 (Thermal Efficiency = 86) ............................................
7 (Thermal Efficiency = 90) ............................................
8¥Max Tech (Thermal Efficiency = 95) ........................
Improved Heat Exchanger Design.
Improved Heat Exchanger Design.
Improved Heat Exchanger Design, More Effective Insulation (Combustion Chamber).
Power Venting.
Power Venting, Improved Heat Exchanger Design.
Sealed Combustion, Improved Heat Exchanger Design.
Sealed Combustion, Condensing.
Sealed Combustion, Condensing, Improved Heat Exchanger Design.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
* Technologies incorporating either a standing pilot or electronic ignition. Efficiency Levels above 3 include electronic ignition.
In the executive summary to the
preliminary TSD, DOE sought
comments on design changes
manufacturers might use to mitigate the
formation of corrosive condensation at
86 percent thermal efficiency for gasfired pool heaters. DOE also sought
comments on the changes
manufacturers would make to the
product design and the effects on MPC
that would result if the amended energy
conservation standards were at 86
percent thermal efficiency.
Raypak commented that Efficiency
Level 6 (i.e., 86 percent) requires sealed
combustion, which will be a condensing
system. (Raypak, Public Meeting
Transcript, No. 34.4 at pp. 120–121)
AHRI urged DOE to exclude nearcondensing thermal efficiency levels
from its analysis. AHRI pointed out that
manufacturers would need to address a
range of field installations and operating
conditions if a minimum energy
conservation standard level is set in the
near-condensing range. (AHRI No. 43 at
p. 5)
In response, DOE is aware of a pool
heater model on the market at Efficiency
Level 6. According to product literature,
these models do not appear to
incorporate condensate management.
Therefore, DOE did not change the
technology options at Efficiency Level 6
to represent a condensing pool heater.
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However, DOE’s technology option for
Efficiency Level 6 does include sealed
combustion, as Raypak suggested.
4. Cost Assessment Methodology
At the start of the preliminary
engineering analysis, DOE identified the
energy efficiency levels associated with
residential heating products on the
market, as determined in the market
assessment. DOE also identified the
technologies and features that are
typically incorporated into products at
the baseline level and at the various
energy efficiency levels above the
baseline. Next, DOE selected products
for the physical teardown analysis that
corresponded to the representative rated
storage volumes and input capacities.
DOE gathered the information from the
physical teardown analysis to create
bills of materials using a reverse
engineering methodology. After that,
DOE used the physical teardown
analysis to identify the design pathways
manufacturers typically use to increase
the EF of residential water heaters, the
AFUE of residential DHE, or the thermal
efficiency of residential pool heaters.
DOE calculated the MPC for products
spanning the full range of efficiencies
from the baseline to the maximum
technology available at various levels,
and it also identified each technology or
combination of technologies in each
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product that was responsible for
improving the energy efficiency. DOE
determined the cost-effectiveness of
each technology by comparing the
increase in MPC to the increase in
energy efficiency. For the NOPR, DOE
reexamined and revised several of the
steps in its cost assessment
methodology based on additional
teardown analysis and in response to
comments received on the preliminary
analysis.
During the preparation and refining of
the cost-efficiency comparison and
MPCs for the NOPR, DOE also held
interviews with manufacturers to gain
insight into each of the water heating,
direct heating, and pool heating
industries and requested comments on
the engineering approach DOE used.
DOE used the information gathered from
these interviews, along with the
information gathered through additional
teardown analysis and public
comments, to refine efficiency levels
and assumptions in the cost model.
Next, DOE converted the MPCs into
MSPs using publicly-available water
heating, direct heating, and pool heating
industry financial data, in addition to
manufacturers’ feedback. Further
information on comments received and
the revisions to the analysis
methodology is presented in subsections
a through g of this section. For
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additional detail, see chapter 5 of the
NOPR TSD.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
a. Teardown Analysis
To assemble bill of materials (BOMs)
and to calculate the manufacturing costs
of the different components in
residential heating products, DOE
disassembled multiple residential
heating products into their base
components and estimated the
materials, processes, and labor required
for the manufacture of each individual
component, a process referred to as a
‘‘physical teardown.’’ Using the data
gathered from the physical teardowns,
DOE characterized each component
according to its weight, dimensions,
material, quantity, and the
manufacturing processes used to
fabricate and assemble it. DOE also used
a supplementary method, called a
‘‘virtual teardown,’’ which uses
published manufacturer catalogs and
supplementary component data to
estimate the major physical differences
between a product that was physically
disassembled and a similar product that
was not. For supplementary virtual
teardowns, DOE gathered product data
such as dimensions, weight, and design
features from publicly-available
information, such as manufacturer
catalogs. DOE obtained information and
data not typically found in catalogs and
brochures, such as fan motor details, gas
manifold specifications, or assembly
details, from the physical teardowns of
a similar product or through estimates
based on industry knowledge. The
teardown analysis for this engineering
analysis included over 40 physical and
virtual teardowns of water heaters, DHE,
and pool heaters during the preliminary
analysis and over 20 additional
teardowns performed for the NOPR
analysis. The additional teardowns
performed for the NOPR analysis
allowed DOE to further refine the
product components and assumptions
used to develop the MPCs.
The teardown analysis allowed DOE
to identify the technologies that
manufacturers typically incorporate into
residential heating products, along with
the efficiency levels associated with
each technology or combination of
technologies. DOE used the teardown
analysis to create detailed BOMs for
each product class. The BOMs from the
teardown analysis were then placed into
the cost model to calculate the MPC for
the representative product in each
product class. See chapter 5 of the
NOPR TSD for more details on the
teardown analysis.
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b. Cost Model
The end result of each teardown is a
structured BOMs. DOE developed
structured BOMs for each of the
physical and virtual teardowns. The
BOMs incorporate all materials,
components, and fasteners classified as
either raw materials or purchased parts
and assemblies, and characterize the
materials and components by weight,
manufacturing processes used,
dimensions, material, and quantity. The
cost model is a Microsoft Excel
spreadsheet that converts the materials
and components in the BOMs into
dollar values based on the price of
materials, labor rates associated with
manufacturing and assembling, and the
cost of overhead and depreciation. To
convert the information in the BOMs to
dollar values for the preliminary
analysis, DOE collected information on
labor rates, tooling costs, raw material
prices, and other factors. For purchased
parts, the cost model estimates the
purchase price based on volumevariable price quotations and detailed
discussions with manufacturers and
component suppliers. For fabricated
parts, the prices of raw metal materials
(e.g., tube, sheet metal) are estimated on
the basis of 5-year averages. The cost of
transforming the intermediate materials
into finished parts is estimated based on
current industry pricing. For the NOPR
analysis, DOE updated all of the labor
rates, tooling costs, raw material prices,
the costs of resins, and the purchased
parts costs. Chapter 5 of the NOPR TSD
describes DOE’s cost model and
definitions, assumptions, and estimates.
DOE received several comments on
the material prices collected for use in
the cost model, as discussed below.
Bock commented that manufacturer
production costs were calculated
approximately 2 years before the public
meeting for the preliminary analysis.
Bock noted that the price of steel has
increased tremendously and that DOE
should recalculate these costs. (Bock,
Public Meeting Transcript, No. 34.4 at
p. 27) In written comments, Bock
reiterated that because material prices,
particularly for steel, have increased
significantly since DOE completed its
analysis, DOE’s estimated manufacturer
production costs and selling prices
should be adjusted to reflect this trend.
(Bock, No. 53 at p. 1)
In contrast, ACEEE commented that
DOE significantly overestimated the cost
of compliance with amended standards
to the consumer. ACEEE stated that this
was due to the effects of changing
material prices on products and
suggested that it would be appropriate
for DOE to review past rulemakings to
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determine the accuracy of DOE’s
analytical approaches. (ACEEE, Public
Meeting Transcript, No. 34.4 at pp. 81–
82) Southern Company disagreed with
ACEEE regarding the cost to the
consumer and referenced the most
recent residential air conditioner
rulemaking which was done when
commodity prices were depressed.
Southern stated that because of the
depressed commodity prices, the actual
costs were higher than DOE’s
projections. (Southern, Public Meeting
Transcript, No. 34.4 at p. 82) Further,
Southern commented that a 5-year
rolling average of commodity prices
would be appropriate for this
rulemaking. (Southern, Public Meeting
Transcript, No. 34.4 at p. 83) Rheem
agreed with Southern regarding
commodity prices. Regarding the
residential central air conditioner
rulemaking, Rheem stated that the
results were devastating to the industry
and domestic manufacturers, and the
company urged DOE to be very careful
in estimating the cost to consumers
because of the potential for a
significantly adverse impact on
domestic manufacturing jobs. (Rheem,
Public Meeting Transcript, No. 34.4 at
pp. 83–84) In its written comments,
Rheem noted that manufacturer
production costs were derived from
material prices that were based on 5year averages from 2003 to 2007. Rheem
urged DOE to revise material prices due
to their drastic increases and volatility
driven by global demand. (Rheem, No.
49 at pp. 2–3) A.O. Smith agreed that
using material prices from 2003 through
2007 to determine a normalized average
may be understating actual prices,
which continued to fluctuate but
generally increased in 2008. (A.O.
Smith, No. 37 at p. 4)
Because all interested parties agreed
with DOE’s approach to use 5-year
rolling average material prices in the
engineering analysis, DOE used the
same approach in the NOPR analysis.
DOE acknowledges Bock’s, Rheem’s,
and A.O. Smith’s concerns about the
timing of the production cost
calculations because the majority of
manufacturer production cost can
typically be attributed to materials,
which can fluctuate greatly from year to
year. DOE uses a 5-year span to
normalize the fluctuating prices
experienced in the metal commodities
markets to screen out temporary dips or
spikes. DOE believes a 5-year span is the
longest span that would still provide
appropriate weighting to current prices
experienced in the market. DOE updates
the 5-year span for metal prices based
on a review of updated commodity
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pricing data, which point to continued
increases. Considering the significant
amount of steel and copper in the
different heating products at issue in
this rulemaking, incorporating
commodity prices that reflect 5-year
average prices as close to current
conditions would best reflect overall
market conditions. Consequently, DOE
calculated a new 5-year average
materials price using the U.S.
Department of Labor’s Bureau of Labor
Statistics (BLS) Producer Price Indices
(PPIs) for various raw metal materials
from 2005 to 2009 to calculate new
averages, which incorporate the changes
within each material industry and
inflation. DOE also used BLS PPI data
to update current market pricing for
other input materials such as plastic
resins and purchased parts. Finally,
DOE adjusted all averages to 2008$
using the gross domestic product
implicit price deflator.
c. Manufacturing Production Cost
Once the cost estimate for each
teardown unit was finalized, DOE
totaled the cost of materials, labor, and
direct overhead used to manufacture a
product in order to calculate the
manufacturer production cost for the
preliminary analysis. The total cost of
the product was broken down into two
main costs: (1) The full manufacturer
production cost or MPC; and (2) the
non-production cost, which includes
selling, general, and administration
(SG&A) costs, the cost of research and
development, and interest. DOE
estimates the MPC at each efficiency
level considered for each product class,
from the baseline through the max-tech.
After DOE incorporates all of the
assumptions into the cost model, DOE
calculates the different percentages of
each aspect of production cost (i.e.
materials, labor, depreciation, and
overhead) that make up the total
production cost. The product cost
percentages are used to validate the
assumptions by comparing them to
manufacturers’ actual financial data
published in annual reports, along with
feedback from manufacturers during
interviews. DOE uses these production
cost percentages in the MIA (see section
IV.H).
For the NOPR analysis, DOE revised
the assumptions in the cost model based
on additional teardown analysis,
updated pricing, and additional
manufacturer feedback, which resulted
in revised MPCs and production cost
percentages. DOE calculated the average
product cost percentages by product
type (i.e., water heater, DHE, pool
heater) as well as by product class (e.g.,
gas-fired storage water heater, electric
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storage water heater) due to the large
variations in production volumes,
fabrication and assembly costs, and
other assumptions that affect the
calculation of the unit’s total MPC.
Chapter 5 of the NOPR TSD shows
DOE’s estimate of the MPCs for the
NOPR phase of this rulemaking, along
with the different percentages for each
aspect of the production costs that make
up the total product MPC.
DOE received various comments in
response to the MPCs presented in its
preliminary analysis, as discussed
below.
For pool heaters, Raypak stated that
the cost difference between the ignition
systems of gas-fired pool heaters should
be more than $3, because the electronic
ignition controls cost more than $3.
Raypak also commented that the
materials used for Efficiency Level 6
must be suitable for condensing
applications, which means that DOE’s
estimate for MPC for Efficiency Level 6
is understated. (Raypak, Public Meeting
Transcript, No. 34.4 at pp. 120–121)
In response, DOE revised all of the
MPCs for residential heating products
for the NOPR analyses. In the case of
pool heaters, DOE reexamined the
component cost assumptions for
electronic ignitions and revised the
estimate of the cost to implement an
electronic ignition design. The revised
cost assumptions for an electronic
ignition are documented in chapter 5 of
the NOPR TSD. DOE also revised the
costs for Efficiency Level 6, but did not
consider the costs associated with
condensate management at that
efficiency level. Some residential pool
heater designs currently on the market
do not appear to accommodate
condensing operations at 86 percent
thermal efficiency, thereby suggesting
that such costs need not be incurred to
reach that efficiency level. Therefore,
DOE did not account for condensate
management in the cost of products at
Efficiency Level 6.
Regarding gas-fired storage water
heaters, Rheem stated that the MPC and
MSP for Efficiency Level 6 should be
higher. (Rheem, No. 49 at p. 4) A.O.
Smith asserted that the estimated
manufacturer production costs in DOE’s
preliminary analysis are too low for
max-tech water heaters (i.e., heat pump
water heaters and condensing gas-fired
water heaters). (A.O. Smith, No. 37 at p.
4) Additionally, A.O. Smith stated that
the baseline MPCs are approximately 11
percent low for gas-fired storage water
heaters and 13 percent low for electric
storage water heaters. (A.O. Smith, No.
37 at p. 6)
On this point, DOE has revised its
cost estimates for storage water heaters
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at all levels, including the baseline and
the max-tech efficiency levels based on
manufacturer feedback obtained during
interviews performed for the MIA (see
section IV.H.4). The resulting cost
estimates for the NOPR analysis are
higher than in the preliminary analysis.
Chapter 5 of the NOPR TSD discusses
DOE’s cost estimates for max-tech
storage water heaters.
BWC commented that the energy
factor for condensing gas-fired storage
water heaters (the max-tech level) was
based on models on the market that are
not classified as residential water
heaters. BWC stated that it is unfair to
use non-residential models to determine
the cost of condensing water heaters,
because non-residential models do not
include components and the associated
costs to make them compliant with
other regulations, such as FVIR and
ultra-low NOX requirements. (BWC, No.
46 at p. 2).
For DOE’s estimate of the
manufacturing cost of condensing gasfired storage water heaters, DOE did
include the additional cost of FVIR in
both the preliminary and NOPR
analyses, which is not found in
commercial water heaters currently on
the market. DOE also based its
condensing water heater design on one
that would be more typical of
residential applications (i.e., 40-gallon
storage volume and 40,000 Btu/h input
capacity). In addition, DOE developed
separate manufacturer production costs
for gas-fired storage water heaters with
standard burners and for gas-fired
storage water heaters with ultra-low
NOX burners (section IV.C.2), including
those gas-fired water heaters that would
have been at the max-tech efficiency
level.
d. Cost-Efficiency Curves
The result of the engineering analysis
is a set of cost-efficiency curves. DOE
created 11 curves representing each
product class examined for this NOPR.
For storage water heaters, the costefficiency curves show the
representative rated storage volumes in
addition to the other storage volumes
analyzed.
Chapter 5 of the NOPR TSD contains
the 11 cost-efficiency curves in the form
of energy efficiency (i.e., EF, AFUE, or
thermal efficiency) versus MPC. The
results show that the cost-efficiency
curves are nonlinear. As efficiency
increases, manufacturing becomes more
difficult and more costly. Large jumps
are evident when efficiencies approach
levels where electronic ignition, blower
motors, power vent, and condensing
operation are included in designs.
Additionally, MPC increases greatly
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when heat pump technology is used as
an alternative to resistive heating for
electric storage water heaters.
The non-linear relationship is
common across all product types. In
addition, DHE and high-efficiency pool
heaters see larger increases in MPC due
to lower production volumes than water
heaters.
In response to the cost-efficiency
curves developed for the preliminary
analysis, ACEEE asserted that DOE’s
cost-efficiency relationship ignores the
potential ‘‘learning-by-doing’’ effects
that have driven down the costs of
technologies for almost all regulated
goods. The commenter argued that more
stringent standards lead to product
redesigns that almost inevitably result
in lower consumer prices for moreefficient goods after the amended
standards have become effective. ACEEE
recommended that DOE balance the
current cost-efficiency development
approach with the historical results of
rulemakings on manufacturer
production costs. (ACEEE, No. 35 at p.
5)
Similarly, NRDC questioned DOE
predictions that more-efficient products
result in escalating costs and stated that
DOE should re-analyze these
projections. NRDC also commented that
this rulemaking addresses products
previously covered and analyzed in
other rulemakings, and asserted that
DOE should evaluate previous analyses
by reviewing its predictions versus the
realized effects of standards so that costs
are not overestimated for this
rulemaking. NRDC stated that an
overestimation of the cost to improve
efficiency could cause DOE to set
standards below the levels that would
be justified if DOE were to determine
costs by more accurate methods, a result
which would fail to meet the
requirements of the statute. (NRDC, No.
48 at p. 4)
DOE does not agree with ACEEE or
NRDC for the following reasons. DOE
recognizes that every change in
minimum energy conservation
standards is an opportunity for
manufacturers to make investments
beyond what would be required to meet
the new standards in order to minimize
costs or to respond to other factors.
However, DOE’s manufacturing cost
estimates seek to gauge the most likely
industry response to meet the
requirements of proposed energy
conservation standards. DOE’s analysis
of manufacturing cost must be based on
currently-available technology that
would provide a nonproprietary
pathway for compliance with a standard
once it becomes effective, and, thus,
DOE cannot speculate on future product
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and market innovation. In response to a
change in energy conservation
standards, manufacturers have made a
number of changes to reduce costs in
the past. For example, DOE understands
manufacturers have re-engineered
products to reduce cost, made changes
to manufacturing process to reduce
labor costs, and moved production to
lower-cost areas to reduce labor costs.
However, these are individual company
decisions, and it is impossible for DOE
to forecast such decisions. DOE does not
know of any data that would allow it to
determine the precise course a
manufacturer may take. Furthermore,
while manufacturers have been able to
reduce the cost of products that meet
previous energy conservation standards,
there are no data to suggest that any
further reductions in cost are possible.
Therefore, it would not be appropriate
to speculate about cost reduction based
upon prior actions of manufacturers of
either the same or other products.
Setting energy conservation standards
upon relevant data is particularly
important given EPCA’s anti-backsliding
provision at 42 U.S.C. 6295(o)(1).
e. Manufacturer Markup
DOE applies a non-production cost
multiplier (the manufacturer markup) to
the full MPC to account for corporate
non-production costs and profit. The
resulting manufacturer selling price is
the price at which the manufacturer can
recover all production and nonproduction costs and earn a profit. To
meet new or amended energy
conservation standards, manufacturers
often introduce design changes to their
product lines that result in increased
manufacturer production costs.
Depending on the competitive
environment for these particular
products, some or all of the increased
production costs may be passed from
manufacturers to retailers and
eventually to customers in the form of
higher purchase prices. As production
costs increase, manufacturers typically
incur additional overhead. The MSP
should be high enough to recover the
full cost of the product (i.e., full
production and non-production costs),
and yield a profit. The manufacturer
markup has an important bearing on
profitability. A high markup under a
standards scenario suggests
manufacturers can pass through the
increased variable costs and some of the
capital and product conversion costs
(the one-time expenditures). A low
markup suggests that manufacturers will
not be able to recover as much of the
necessary investment in plant and
equipment.
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To calculate the manufacturer
markups for the preliminary analysis,
DOE used 10–K reports from publiclyowned residential heating products
companies. (SEC 10–K reports can be
found using the search database at:
https://www.sec.gov/edgar/searchedgar/
webusers.htm.) The financial figures
necessary for calculating the
manufacturer markup are net sales,
costs of sales, and gross profit. For the
preliminary analysis, DOE averaged the
financial figures spanning 2000 to 2006
and then calculated the markups. For
the NOPR analysis, DOE updated the
financial figures using 10–K reports
spanning 2003 to 2008. To calculate the
time-average gross profit margin for
each firm, DOE summed the gross profit
for all the years and then divided the
result by the sum of the net sales for
those years. DOE presented the
calculated markups to manufacturers
during the interviews for the NOPR (see
section IV.H.4). DOE considered the
feedback from manufacturers in order to
supplement the calculated markup, and
refined the markup to better reflect the
residential heating products market.
DOE developed the manufacturer
markup by weighting the feedback from
manufacturers on a market share basis,
since manufacturers with larger market
shares more accurately represent a
greater portion of the market. DOE used
a constant markup to reflect the MSPs
of the baseline products as well as moreefficient products. DOE took this
approach because amended standards
may make high-efficiency products,
which currently are considered
premium products, and make them the
baselines. See chapter 5 of the NOPR
TSD for more details about the markup
calculation.
In response to the preliminary
analysis, Bock commented on the MPC
and MSP for oil-fired storage water
heaters at Efficiency Level 6. Bock
stated that the MPC is reasonable in
terms of considering increased material
costs, but that the MSP is much too low
(implying that DOE’s markup for oilfired storage water heaters is too low).
The commenter stated that the
distribution chain is flawed for some
manufacturers and that, unlike gas-fired
and electric storage water heaters, oilfired storage water heaters require an oil
burner that adds approximately $400 to
the MSP. Based upon the above
reasoning, Bock stated that the MSP for
Efficiency Level 6 is approximately
$1,400. (Bock, No. 53 at p. 1)
The MSP, as defined by DOE, is the
selling price from the manufacturer to
the first step in its distribution chain
(e.g., a wholesaler, a distributor, or a
national retailer). The MSP does not
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include any further markups for the rest
of the distribution chain, but the MPC
for oil-fired storage water heaters
includes the price of the burner.
Therefore, the MSP as defined by DOE
can be significantly lower than the
purchase price for an end-consumer,
which is what DOE believes Bock is
referring to. The purchase price would
depend on the typical markups in each
step of the distribution chain as well as
the number of layers of distribution the
product has to clear before reaching the
end-consumer. Section IV.D of this
notice describes the distribution chain
markups in further detail.
f. Shipping Costs
For the preliminary analysis, DOE
accounted for the shipping costs for
residential heating products as part of
the non-production costs that comprise
the manufacturer markup. This
approach is typical of energy
conservation standards rulemakings for
residential products.
Following the preliminary analysis,
DOE received several comments about
the impact of an amended energy
conservation standard on shipping (i.e.,
freight) costs for storage water heaters.
A.O. Smith commented that freight is
not a manufacturing cost, but it is a
substantial cost incurred for water
heaters, especially tank-type models.
Water heater manufacturers generally
pay for shipping to most customers;
therefore, this cost is added in the
manufacturer’s gross margin calculation.
A.O. Smith noted that an increase in
water heater size will add cost to the
overall manufacture/purchase
transition. (A.O. Smith, No. 37 at p. 4)
Similarly, BWC commented that DOE
underestimated the increase in freight
costs as overall dimensions increase
when larger cavity sizes are used. (BWC,
No. 46 at p. 2).
Although the non-production costs
typically account for freight in the
manufacturer markup, DOE responded
65893
to these comments by separating the
shipping costs from the markup
multiplier for storage water heaters for
the NOPR analysis in order to make the
MSP calculation more transparent. DOE
calculated the MSP for storage water
heaters by multiplying the MPC
determined from the cost model by the
manufacturer markup and adding
shipping costs. More specifically, DOE
calculated shipping costs based on a
typical 53-foot straight frame trailer
with a storage volume of 4,240 cubic
feet. DOE examined the average sizes of
representative water heaters and
determined the number of units that
would fit in each trailer, based on
assumptions about the arrangement of
water heaters in the trailer. Finally, DOE
calculated the average cost for each unit
shipped based on an average cost of
$4,000 per trailer load. See chapter 5 of
the NOPR TSD for more details about
DOE’s shipping cost assumptions and
the shipping costs per unit for each
storage water heater product class.
products or manufacturing processes.
More details about the manufacturer
interviews are contained in chapter 12
of the NOPR TSD. The interview guides
DOE distributed to manufacturers are
contained in appendix 12–A of the
NOPR TSD.
g. Manufacturer Interviews
To account for the large variation in
the rated storage volumes of residential
storage water heaters and differences in
both usage patterns and first cost to
consumers of water heaters larger or
smaller than the representative capacity,
DOE scaled its MPCs and efficiency
levels at the representative capacities to
several discrete rated storage volumes at
capacities higher and lower than the
representative storage volume for each
storage water heater product class. DOE
developed the MPCs for water heaters at
each of the rated storage volumes shown
in Table IV.22. These storage volumes
were determined to be the most
prevalent storage volumes available on
the market during the market analysis
(see Chapter 3 of the TSD). The MPCs
developed for this analysis were used in
the downstream LCC analysis, where a
distribution of MPCs was used based on
the estimated market share of each rated
storage volume (see Section IV.E).
Throughout the rulemaking process,
DOE seeks feedback and insight from
interested parties to improve the
information used in its analyses. DOE
interviewed manufacturers as a part of
the NOPR manufacturer impact analysis
(see section IV.H.4). During the
interviews, DOE sought feedback on all
aspects of its analyses for residential
heating products. For the engineering
analysis, DOE discussed the analytical
assumptions and estimates, cost model,
and cost-efficiency curves with
manufacturers of water heaters, DHE,
and pool heaters. DOE considered all
the information manufacturers provided
when refining the cost model and
assumptions. DOE incorporated
equipment and manufacturing process
figures into the analysis as averages to
avoid disclosing sensitive information
about individual manufacturers’
5. Results
The results from the engineering
analysis were used in the LCC analysis
to determine consumer prices for
residential heating products at the
various potential standard levels. Using
the manufacturer markup, DOE
calculated the MSPs of the
representative water heaters, DHE, and
pool heater from the MPCs developed
using the cost model. Chapter 5 of the
NOPR TSD provides the full list of
MPCs and MSPs at each efficiency level
for each analyzed representative
product.
6. Scaling to Additional Rated Storage
Capacities for Water Heaters
TABLE IV.22—ADDITIONAL WATER HEATER STORAGE VOLUMES ANALYZED
Storage volumes
analyzed (gallons,
U.S.)
Water heater product class
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Gas-fired Storage ...................................................................................................................................................................
Electric Storage ......................................................................................................................................................................
Oil-fired Storage .....................................................................................................................................................................
To develop the MPCs for the analysis
of additional storage volumes, DOE
developed a cost model based on
teardowns of representative units from a
range of nominal capacities and
multiple manufacturers. Whenever
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possible, DOE maintained the same
product line that was used for the
teardown at the representative storage
volume to allow for a direct comparison
between models at the representative
storage volume and models at higher
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30, 50, 65, 75.
30, 40, 66, 80, 119.
50.
and lower storage volumes. The cost
model accounts for changes in the size
of water heater components that would
scale with tank volume (e.g., tank
dimensions, wrapper dimensions, wall
thicknesses, insulation thickness, anode
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rod(s), flue pipe(s)). Components that
typically do not change based on tank
volume (e.g., gas valves, thermostats,
controls) were assumed to remain
largely the same across the different
storage volume sizes, while accounting
for price differences due to changes in
insulation thickness. DOE estimated the
changes in material and labor costs that
occur at volume sizes higher and lower
than the representative capacity based
on observations made during teardowns
and professional experience. Performing
teardowns of models outside of the
representative capacity allowed DOE to
accurately model certain characteristics
(such as tank wall thickness and
wrapper thickness) that are not
identifiable in manufacturer literature.
While DOE was able to receive
feedback from manufacturers regarding
the manufacturing costs of storage water
heaters at representative storage
capacities, DOE was unable to solicit
manufacturing cost feedback from
manufacturers regarding the additional
water heaters shown above. However,
DOE was able to finely tune the
performance of the cost model to
accurately predict the weights of nonrepresentative units via the additional
teardowns. For example, DOE observed
that the tank wall thickness increases as
a function of tank diameter. Based on
the feedback received from
manufacturers for representative units
and the accuracy of the material
predictions for non-representative units,
DOE believes that its scaling is accurate.
In addition to comparing model output
to actual teardowns, model outputs
were also compared to published
catalog data.
The results of DOE’s analysis for the
additional storage volumes are
presented in chapter 5 of the NOPR TSD
(engineering analysis). Chapter 5 of the
NOPR TSD also contains additional
details about the calculation of MPCs for
storage volumes outside of the
representative capacity. DOE is seeking
comment its MPC estimates at the
additional storage volumes outside of
the representative storage volumes, as
well as on its approach to developing
these MPCs. (See issue number 12 under
Section VII.E ‘‘Issues on Which DOE
Seeks Comment’’).
7. Energy Efficiency Equations
As part of the engineering analysis for
residential water heaters, DOE reviewed
the energy efficiency equations that
define the existing Federal energy
conservation standards for gas-fired and
electric storage water heaters. The
energy efficiency equations allow DOE
to expand the analysis on the
representative rated storage volume to
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the full range of storage volumes
covered under the existing Federal
energy conservation standards.
DOE uses energy efficiency equations
to characterize the relationship between
rated storage volume and energy factor.
The energy efficiency equations allow
DOE to account for the increases in
standby losses as tank volume increases.
As the tank storage volume increases,
the tank surface area increases. The
larger surface area results in higher heat
transfer rates that result in higher jacket
losses. Other losses to consider are the
feed-through losses and flue losses (for
gas-fired water heaters). The current
energy efficiency equations show that
for each water heater class, the
minimum energy factor decreases as the
rated storage volume increases.
After reviewing market data and
product literature for gas-fired and
electric storage water heaters, DOE
presented two approaches for amending
the existing energy efficiency equations
for storage water heaters. One approach
was to maintain the same slope used in
the existing equations, but to
incrementally increase the intercepts.
This created energy efficiency equations
with the same slope to define EF across
the entire range of storage volumes for
each efficiency level. The advantage of
this approach would be to maintain the
same slopes established in NAECA and
used in the 2001 rulemaking, which
have historically characterized the water
heater market.
A second approach was to adjust the
slope of the energy efficiency equations
based on the review of the storage water
heater models currently on the market.
The advantage of this approach is the
acknowledge the changes in the product
efficiencies offered over time and
account for these changes. DOE
examined the efficiencies of models
with varying storage volumes, but with
the same or similar design features. DOE
varied the slope of the line to maximize
the number of models in the series that
meet the efficiency levels DOE is
considering in the full range of rated
storage volumes. DOE sought comments
on approaches to develop the energy
efficiency equations for all storage
volumes and all efficiency levels of gasfired and electric storage water heaters.
Specifically, DOE sought comment on
an alternative approach based on model
series that incorporate current market
data from AHRI’s Consumers’ Directory
to generate revised equation slopes that
minimize the number of models that
would become obsolete. DOE received
feedback from several interested parties,
as discussed immediately below.
ACEEE commented that the
alternative energy efficiency equations
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appear to relax the energy factor
requirements for smaller capacity water
heaters while making the energy factor
requirements more stringent for larger
capacity water heaters. (ACEEE, Public
Meeting Transcript, No. 34.4 at p. 100)
AHRI stated that there are more options
for saving energy at higher capacities.
AHRI further stated that additional
energy may be saved by using an
alternative energy efficiency equation
and that there may be two equations
that define the energy conservation
standard across the range of rated
volumes. (AHRI, Public Meeting
Transcript, No. 34.4 at pp. 101–102)
Rheem argued that size constraints must
be considered when determining
alternative energy efficiency equations
and efficiency levels for replacement
water heaters. Rheem stated that there
are certain doorways and attics where
installations will not be possible due to
size constraints. (Rheem, Public Meeting
Transcript, No. 34.4 at p. 104)
Rheem expressed concern that
changes to the energy efficiency
equations may result in the elimination
of certain capacities. However, Rheem
stated that the current slope is
inappropriate as it would set
unattainable levels for small and large
capacity water heaters. Rheem
commented that the proposed
alternative equations disproportionately
affect gas-fired storage water heaters,
especially large-storage-volume
products. In sum, Rheem recommended
that DOE should revisit the current
equations to determine whether energy
factors across the full range of rated
storage volumes are still appropriate.
(Rheem, No. 49 at p. 6)
EEI expressed support for DOE’s
decision to update the energy efficiency
equations for storage-type water heaters.
However, EEI cautioned DOE to avoid
eliminating certain storage volumes
from the market. Therefore, EEI
suggested that DOE develop a two-slope
approach for smaller and larger water
heaters to ensure competition in the
marketplace. (EEI, No. 40 at p. 4)
In response, DOE agrees that the
alternative slopes examined at each
efficiency level for the preliminary
analysis were not as stringent for the
lower storage volume models and were
more stringent for higher storage volume
models when compared to the slope
defining existing standards. DOE
presented such slopes because many
models at lower storage volumes have
already reached close to the maximum
possible efficiency with conventional
technologies, while there is more
potential for increased energy efficiency
for models with larger storage volumes.
However, DOE also notes that this
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increased stringency may discourage
manufacturers from continuing to
develop larger storage volume models.
To attempt to mitigate these issues, DOE
is proposing ‘‘two-slope’’ energy
efficiency equations to better define the
relationship between storage volume
and energy factor across the range of
covered storage volumes.
ACEEE stated its support for
modifying the energy efficiency
equations for electric and gas-fired
storage water heaters if the effect would
be to increase the EF for larger units
(i.e., those units with a higher rated
storage volume). For electric storage
water heaters, ACEEE supported
capping the EF requirement at 0.95,
even for the smaller rated storage types.
(ACEEE, No. 35 at p. 6) NEEA and NPCC
agreed with DOE’s intention to adjust
the slopes of the energy efficiency
equations for gas-fired and electric
storage water heaters. Specifically,
NEEA and NPCC stated their support for
the recommended approach by fitting
the energy efficiency equations to actual
product lines on the market. NEEA and
NPCC recommended a further lessening
of the slope than the examples shown in
the preliminary analysis to preserve at
least one model offered on the current
market over the range of storage
volumes. (NEEA and NPCC, No. 42 at
p. 6) BWC commented that the energy
efficiency equations for water heaters
should be changed, arguing that as
amended standards increase energy
efficiency, it becomes increasingly
difficult for units with larger gallon
capacities to comply. (BWC, No. 46 at
p. 1)
In contrast, A.O. Smith stated that the
existing energy efficiency equations
should not be changed. While A.O.
Smith acknowledged some of the points
DOE made in the preliminary analyses
regarding the existing energy efficiency
equations, A.O. Smith stated it would
take a much more detailed investigation
than DOE has used to validate the
points raised. (A.O. Smith, No. 37 at
p. 8)
While DOE acknowledges that A.O.
Smith does not support changing the
energy-efficiency equations for gas-fired
and electric storage water heaters, DOE
believes that the slopes of the energy
efficiency equations can be revised to
more accurately characterize the
relationship between storage volume
and energy factor for the current storage
water heater market.
For this NOPR, DOE reviewed AHRI’s
March 2009 Consumers’ Directory and
developed a database of products that
includes all gas-fired and electric
storage water heater models subject to
this rulemaking. DOE also reviewed
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manufacturers’ catalogs to gather
information on the design
characteristics of each water heater
model. The manufacturers’ catalogs
include information on efficiency
ratings, product series descriptions,
jacket insulation thicknesses, ignition
types, and drafting methods (i.e., natural
or power vented drafting). To further
investigate the relationship between EF
and rated storage volume, DOE
conducted testing according to the water
heater test procedure specified in 10
CFR 430, subpart B, appendix E (the
same test procedure manufacturers use
to certify products in AHRI’s
Consumers’ Directory) to verify the EF
values. DOE tested model series with
similar design characteristics and
volumetric designs to isolate how EF
changes with rated storage volume. DOE
performed this testing for a number of
model series at various efficiencies and
for a variety of manufacturers. DOE
chose models to test by selecting
product series from multiple major
manufacturers that span the range of
rated volumes within each product class
and that span the range of efficiency
levels. After completion of testing, DOE
conducted a teardown analysis of the
tested models and confirmed the
specific technologies that affect energy
efficiency and the volumetric
characteristics of the tank. DOE used the
results of this analysis to adjust the
energy efficiency equations.
Using the information gathered from
product catalogs, independent testing
results, and product teardowns, DOE
developed an alternative approach for
revising the energy efficiency equations
based on three constraints. DOE applied
the following constraining criteria to the
development process:
• For gas-fired water heaters, each
energy efficiency equation must include
units with the specified efficiency level
at 40-gallon rated storage volume.
• For electric storage water heaters,
each energy efficiency equation must
include units with the specified
efficiency level at 50-gallon rated
storage volume.
• The energy efficiency equations
cannot result in a standard that falls
below current standards over the entire
rated volume range.
DOE chose this approach because it
takes into account the models currently
on the market, considers the
technologies incorporated into those
models, and attempts to optimize the
number of models across the entire
rated volume range that would meet the
efficiency levels DOE is considering.
The approach also attempts to minimize
the number of models that would be
eliminated from the market by the
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efficiency levels DOE is considering
across the entire range of storage
volumes.
In examining the market data to
develop the energy efficiency equations,
DOE noted a trend of greater decline in
energy efficiency at higher rated storage
volumes than at lower storage volumes.
As a result, DOE developed energy
efficiency equations with varying slopes
at several of the efficiency levels
analyzed for the NOPR analysis. These
equations maintain one slope from the
minimum covered rated storage volume
up to a certain rated storage volume (i.e.,
60 gallons for gas-fired storage water
heaters and 80 gallons for electric
storage water heaters), and then
maintain a different slope over the
remaining range of covered storage
volumes. DOE selected 60-gallon and
80-gallon storage volumes as the point
where the change in slope of the energy
efficiency equations for gas-fired and
electric storage water heaters,
respectively, should occur, because the
market data suggested a natural break in
the available products at those points.
Models with gallon sizes above 60
gallons for gas-fired units and 80 gallons
for electric units typically experienced
reduced efficiencies more rapidly as a
function of increasing storage volume,
as compared to units with lower volume
sizes. The higher ends of the residential
storage capacities also have a lower
volume of shipments.
Based upon the above approach, for
gas-fired storage water heaters, DOE did
not change the slope of the energy
efficiency equation for storage volumes
above 60 gallons across efficiency levels
(i.e., DOE kept the same slope above 60
gallons at each efficiency level). Few
gas-fired storage water heaters exist with
storage volumes greater than 60 gallons,
and, therefore, the market data were
very limited. Due to the lack of data for
the efficiency at larger gas-fired water
heater storage volumes, DOE used the
slope defining the current standard for
residential gas-fired storage water
heaters, as listed in DOE’s regulations at
10 CFR 430.32(d). In other words, DOE
maintained the same slope for
Efficiency Level 1 through Efficiency
Level 5 for gas-fired storage water
heaters above 60 gallons.
For the max-tech efficiency levels
considered for gas-fired storage water
heaters and electric storage water
heaters, DOE also did not change the
slope of the energy efficiency equations.
Because there are no products currently
available on the market meeting the
max-tech efficiency levels, DOE could
not perform an analysis or come to any
definitive conclusion about the effect of
storage volume on energy factor at these
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efficiency levels. However, DOE does
recognize that with any storage water
heater, the standby losses will increase
with storage volume due to increased
tank surface area. Because there is no
data that DOE can use to make a
determination of an appropriate slope at
these levels, DOE maintained the
relationship between storage volume
and energy factor developed previously
for water heaters. Therefore, the energy
efficiency equations for the max-tech
levels exhibit the same slopes used for
the gas-fired storage water heater and
electric storage water heaters in the
current energy conservation standards at
10 CFR 430.32(d). Table IV.23 and Table
IV.24 show the energy efficiency
equations developed for the NOPR for
gas-fired and electric storage water
heaters, respectively.
TABLE IV.23—NOPR ENERGY EFFICIENCY EQUATIONS FOR GAS STORAGE WATER HEATERS
Efficiency level
20 to 60 gallons
Baseline Energy Efficiency Equation ..................................................
EL 1 Energy Efficiency Equation ........................................................
EL 2 Energy Efficiency Equation ........................................................
EL 3 Energy Efficiency Equation ........................................................
EL 4 Energy Efficiency Equation ........................................................
EL 5 Energy Efficiency Equation ........................................................
EL 6 Energy Efficiency Equation ........................................................
EF
EF
EF
EF
EF
EF
EF
=
=
=
=
=
=
=
¥0.00190(VR)
¥0.00150(VR)
¥0.00120(VR)
¥0.00100(VR)
¥0.00090(VR)
¥0.00078(VR)
¥0.00078(VR)
+
+
+
+
+
+
+
Over 60 and up to 100 gallons
0.670 ...........
0.675 ...........
0.675 ...........
0.680 ...........
0.690 ...........
0.700 ...........
0.8312 .........
EF
EF
EF
EF
EF
EF
EF
=
=
=
=
=
=
=
¥0.00190(VR)
¥0.00190(VR)
¥0.00190(VR)
¥0.00190(VR)
¥0.00190(VR)
¥0.00190(VR)
¥0.00078(VR)
+
+
+
+
+
+
+
0.670.
0.699.
0.717.
0.734.
0.750.
0.767.
0.8312.
TABLE IV.24—NOPR ENERGY EFFICIENCY EQUATIONS FOR ELECTRIC STORAGE WATER HEATERS
Efficiency level
20 to 80 gallons
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Baseline Energy Efficiency Equation ..................................................
EL 1 Energy Efficiency Equation ........................................................
EL 2 Energy Efficiency Equation ........................................................
EL 3 Energy Efficiency Equation ........................................................
EL 4 Energy Efficiency Equation ........................................................
EL 5 Energy Efficiency Equation ........................................................
EL 6 Energy Efficiency Equation ........................................................
EL 7 Energy Efficiency Equation ........................................................
DOE seeks comment on the energy
efficiency equations for gas-fired and
electric storage water heaters developed
for the NOPR. In particular, DOE seeks
comment on its approach to developing
the energy efficiency equations, the
appropriate slope of energy efficiency
equations at each efficiency level
analyzed, and the appropriate storage
volumes for changing the slope of the
line. DOE is also interested in
alternatives to the energy efficiency
equations that DOE should consider for
the final rule. (See Issue 7 under ‘‘Issues
on Which DOE Seeks Comment’’ in
section VII.E of this NOPR.)
There are very few models of oil-fired
storage water heaters on the market. The
lack of data to correlate storage volume
and energy factor for oil-fired water
heaters makes it difficult for DOE to
conclude that an alternative approach is
needed for the energy efficiency
equations. In the preliminary analysis,
DOE presented energy efficiency
equations for oil-fired storage water
heaters that were developed by
maintaining the same slope used in the
existing Federal requirements found in
10 CFR 430.32(d). DOE did not present
any alternative method to establishing
energy efficiency equations for oil-fired
storage water heaters.
In response, AHRI stated its support
for using the current energy efficiency
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EF
EF
EF
EF
EF
EF
EF
EF
=
=
=
=
=
=
=
=
¥0.00132(VR)
¥0.00113(VR)
¥0.00095(VR)
¥0.00080(VR)
¥0.00060(VR)
¥0.00030(VR)
¥0.00113(VR)
¥0.00113(VR)
+
+
+
+
+
+
+
+
0.97 .............
0.97 .............
0.967 ...........
0.966 ...........
0.965 ...........
0.960 ...........
2.057 ...........
2.257 ...........
equations for oil-fired storage water
heaters. (AHRI, No. 43 at p. 5)
Because DOE did not receive any
comments in opposition to using the
same slopes for oil-fired storage water
heaters that currently define the existing
Federal standards, DOE is continuing to
use the same methodology for the
NOPR.
AHRI also recommended that DOE
remove the volume adjustment term
from the energy efficiency equations for
gas-fired instantaneous water heaters
and specify a minimum EF applicable to
all sizes of residential instantaneous
water heaters. (AHRI, No. 43 at p. 5)
Additionally, A.O. Smith stated that
because gas-fired instantaneous water
heaters have no volume correction, an
EF level for all sizes would be
appropriate. (A.O. Smith, No. 37 at p. 7)
DOE acknowledges that nearly all are
rated at 0 gallons of storage volume.
Because the volume adjustment term is
multiplied by storage volume, this will
by default eliminate the volume
adjustment term from the energy
efficiency equation used for gas-fired
instantaneous water heaters with a rated
storage volume of 0 gallons. However,
by definition, gas-fired instantaneous
water heaters may have a rated storage
volume of up to 2 gallons. Therefore,
DOE is proposing to maintain the
volume adjustment factor for
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Over 80 and up to 120 gallons
EF
EF
EF
EF
EF
EF
EF
EF
=
=
=
=
=
=
=
=
¥0.00132(VR)
¥0.00149(VR)
¥0.00153(VR)
¥0.00155(VR)
¥0.00168(VR)
¥0.00190(VR)
¥0.00113(VR)
¥0.00113(VR)
+
+
+
+
+
+
+
+
0.97.
0.999.
1.013.
1.026.
1.051.
1.088.
2.057.
2.257.
consistency with the other energyefficiency equations.
See chapter 5 of the NOPR TSD for
additional information about the energy
efficiency equations for residential
water heaters.
D. Markups To Determine Product Price
By applying markups to the
manufacturer selling prices estimated in
the engineering analysis, DOE estimated
the amounts consumers would pay for
baseline and more-efficient products. At
each step in the distribution channel,
companies mark up the price of the
product to cover business costs and
profit margin. The appropriate markups
for determining the consumer product
price depend, therefore, on the type of
distribution channels through which
products move from manufacturer to
consumer.
Bock stated that DOE needs to
consider that manufacturers sell to their
representatives, who sell water heaters
to distributors. (Bock, No. 53 at p. 2)
DOE’s information indicates that
manufacturer representatives work on
commission to facilitate sales from
manufacturers to both distributors and
retailers, but they do not mark up the
products. The commission is part of the
manufacturers’ costs.
The distribution channel for water
heaters differs for replacement versus
new applications, resulting in different
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markups. For replacement applications,
manufacturers sell to either plumbing
distributors or large retail outlets
(typically large home-supply stores).
Products destined for replacement
applications follow one of two paths: (1)
A retail outlet sells a unit to the
consumer, who either installs it or hires
someone to install it; or (2) a plumbing
distributor sells a unit to a contractor,
who then sells it to a consumer and
installs it. Bock suggested modifying the
first distribution channel to include a
contractor-installer. (Bock, Public
Meeting Transcript, No. 34.4 at pp. 140–
141) DOE agrees that a contractorinstaller may be involved in the first
path, but because the consumer
purchases the product directly, the
contractor does not mark up the cost of
the unit. Thus, DOE did not include a
contractor-installer in the first
distribution path.
AHRI disagreed with the analytical
results that indicate higher markups for
new construction than for replacement
applications. (AHRI, No. 33 at p. 1)
DOE’s markup for new construction is
higher because it includes a markup for
builders. Because builders incur the cost
of a water heater or direct heating
equipment installed in a new home,
DOE finds it appropriate to include a
markup for this cost. To estimate a
builder markup, DOE calculated an
average markup that applies to all costs
builders incur (based on Census data).
NEEA and NPCC stated that DOE
should repeat the process used to
determine markups for the 2001 water
heater rulemaking so that costs
including markups align with the
marketplace. They also stated that
DOE’s method for validating calculated
markups is insufficient, although further
explanation was not provided. (NEEA
and NPCC, No. 42 at pp. 6–7)
The 2001 water heater rulemaking
used data on retail prices to estimate
markups. DOE did not use the same
markup process as in the current
rulemaking, however, because
commenters on the previous rulemaking
stated that DOE provided no
consistency checks to determine the
method’s validity, and it did not
account for the differences in price
associated with different technologies.
In addition, DOE has adopted a different
approach to estimate markups in all of
its rulemakings conducted in recent
years that DOE believes is appropriate
because it provides consistent estimates
based on publicly-available statistics.
DOE collected retail price data for water
heaters to provide a check on its
estimated markups. DOE’s average
calculated retail price for water heaters
is close to the average Internet retail
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price for typical electric and oil-fired
storage water heaters, 7 percent lower
for gas-fired instantaneous water
heaters, and 11 percent lower for gasfired storage water heaters. Given the
uncertainty regarding the
representativeness of the retail price
data that DOE collected, DOE considers
that its markup method provides
reasonably good agreement with prices
in the market.
E. Life-Cycle Cost and Payback Period
Analyses
DOE conducted LCC and PBP
analyses to evaluate the economic
impacts on individual conducted LCC
and PBP analyses to evaluate the
economic impacts on individual
consumers of potential amended energy
conservation standards for the three
types of residential heating products.
The LCC represents total consumer
expenses during the life of an appliance,
including purchase and installation
costs plus operating costs (expenses for
energy use, maintenance, and repair).
To compute LCCs for the three heating
products, DOE discounted future
operating costs to the time of purchase,
then summed those costs over the life of
the appliances. The PBP is calculated
using the change in purchase cost
(normally higher) that results from an
amended efficiency standard, divided
by the change in annual operating cost
(normally lower) that results from the
standard.
DOE measures the changes in LCC
and PBP associated with a given
efficiency level relative to an estimate of
base-case appliance efficiencies. The
base-case estimate reflects the market in
the absence of amended mandatory
energy conservation standards,
including the market for products that
exceed the current standards.
For each set of heating products, DOE
calculated the LCC and PBP for a
nationally representative set of housing
units, which were selected from EIA’s
Residential Energy Consumption Survey
(RECS). The preliminary analysis used
the 2001 RECS. The analysis for today’s
proposed rule uses the 2005 RECS. (See
https://www.eia.doe.gov/emeu/recs/.) For
each sampled household, DOE
determined the energy consumption and
energy price for the heating product. By
developing a representative sample of
households, the analysis captured the
variability in energy consumption and
energy prices associated with the use of
residential heating products. DOE
determined the LCCs and PBPs for each
sampled household using a heating
product’s unique energy consumption
and the household’s energy price, as
well as other variables. DOE calculated
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the LCC associated with the baseline
heating product in each household. To
calculate the LCC savings and PBP
associated with equipment that meets
higher efficiency standards, DOE’s
analysis replaced the baseline unit with
a range of more-efficient designs.
EEI stated that not all residential
water heaters are installed in homes,
and thus DOE should modify its
analysis to account for product usage
and energy pricing in commercial
establishments. (EEI, No. 40 at p. 5) DOE
is unaware of data that show the
percentage of residential water heater
shipments that go to the commercial
sector or how those products are used
in the commercial sector, and the
commenter did not provide such data.
Therefore, DOE did not undertake a
separate analysis for such installations.
Inputs to the calculation of total
installed cost include the cost of the
product—which includes manufacturer
costs, manufacturer markups, retailer or
distributor markups, and sales taxes—
and installation costs. Inputs to the
calculation of operating expenses
include annual energy consumption,
energy prices and price projections,
repair and maintenance costs, product
lifetimes, discount rates, and the year
that proposed standards take effect. DOE
created distributions of values for some
inputs to account for their uncertainty
and variability. Probabilities are
attached to each value. As described
above, DOE used samples of households
to characterize the variability in energy
consumption and energy prices for
heating products. For the inputs to
installed cost, DOE used probability
distributions to characterize sales taxes.
DOE also used distributions to
characterize the discount rate and
product lifetime that are inputs to
operating cost.
The computer model DOE uses to
calculate LCC and PBP, which
incorporates Crystal Ball (a
commercially available software
program), relies on a Monte Carlo
simulation to incorporate uncertainty
and variability into the analysis. The
Monte Carlo simulations randomly
sampled input values from the
probability distributions and household
samples. The model calculated the LCC
and PBP for products at each efficiency
level for 10,000 housing units per
simulation run.
Table IV.25 summarizes the approach
and data DOE used to derive inputs to
the LCC and PBP calculations. The table
provides the data and approach DOE
used for the preliminary TSD, as well as
the changes made for today’s NOPR.
The following subsections discuss the
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initial inputs and the changes DOE
made to them.
TABLE IV.25—SUMMARY OF INPUTS AND KEY ASSUMPTIONS IN THE LCC AND PBP ANALYSES*
Inputs
Preliminary TSD
Changes for the proposed rule
Installed Costs
Product Cost ............................................
Installation Cost .......................................
Derived by multiplying manufacturer cost by manufacturer, retailer and distributor markups and
sales tax, as appropriate.
Water Heaters: Based on data from RS Means
and other sources.
DHE: Based on data from RS Means and DOE’s
furnace installation model.
Pool Heaters: Based on data from RS Means .....
No change.
Applied additional cost for space constraints and
other installation situations.
No change.
No change.
Operating Costs
Annual Energy Use .................................
Energy Prices ..........................................
Energy Price Trends ................................
Repair and Maintenance Costs ...............
Water Heaters: Used hot water draw model to
calculate hot water use for each household in
the sample from RECS 2001. Calculated energy use using the water heater analysis model
(WHAM).
DHE: Based on sample and data from RECS
2001.
Pool Heaters: Based on sample and data from
RECS 2001.
Electricity: Based on EIA’s 2006 Form 861 data ..
Natural Gas: Based on EIA’s 2006 Natural Gas
Navigator.
Variability: Regional energy prices determined for
13 regions.
Forecasted using EIA’s AEO2008 ........................
Water Heaters: Based on RS Means and other
sources.
DHE: Based on RS Means and other sources .....
Pool Heaters: Based on RS Means and other
sources.
No change in approach; sample and data updated using RECS 2005.
No change in approach; sample and data updated using RECS 2005.
No change in approach; sample and data updated using RECS 2005.
Electricity: Updated using data from EIA’s 2007
Form 861 data and EIA’s Form 826.
Natural Gas: Updated using EIA’s 2007 Natural
Gas Navigator.
Variability: No change.
Forecasts updated using EIA’s AEO2009.
Updated various repair costs.
Updated various repair costs.
Updated various repair costs.
Present Value of Operating Cost Savings
Product Lifetime .......................................
Water Heaters: Based on range of lifetimes from
various sources. Variability and uncertainty:
characterized using Weibull probability distributions.
DHE: same as for water heaters ..........................
Pool Heaters: same as for water heaters .............
Discount Rates ........................................
Approach based on the cost to finance an appliance purchase. Primary data source was the
Federal Reserve Board’s SCF** for 1989,
1992, 1995, 1998, 2001, and 2004.
Water heaters: 2015 ..............................................
DHE and Pool Heaters: 2013
Compliance Date of New Standard .........
Revised average lifetimes for gas-fired and electric storage water heaters.
Set lifetime of oil-fired storage water heater equal
to that of gas-fired storage water heater.
No change.
Average lifetime increased from 6 years to 8
years
No change in approach; added data from 2007
SCF.**
No change.
* References for the data sources mentioned in this table are provided in the sections following the table or in chapter 8 of the NOPR TSD.
** Survey of Consumer Finances.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
1. Product Cost
2. Installation Cost
To calculate consumer product costs,
DOE multiplied the manufacturer
selling prices developed in the
engineering analysis by the supplychain markups described above (along
with sales taxes). DOE used different
markups for baseline products and
higher-efficiency products, because the
markups estimated for incremental costs
differ from those estimated for baseline
models.
The installation cost is the total cost
to the consumer to install the
equipment, excluding the marked-up
consumer product price. Installation
costs include labor, overhead, and any
miscellaneous materials and parts.
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a. Water Heaters
In its preliminary analysis, DOE
included several installation costs that
reflect the space constraints on water
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heaters having thicker insulation. DOE
assumed that major modifications for
replacement installations would occur
40 percent of the time for water heaters
with 3 inches or greater insulation. The
analysis included costs for
modifications such as removing door
jams or incorporated strategies such as
installing a smaller tank plus a
tempering valve. To estimate the
fraction of households that would
require various modifications, DOE used
the water heater location determined for
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each sample household. DOE
determined the location using
information from the 2005 RECS, which
reports whether the house has a
basement, whether the basement is
heated or unheated, and the presence or
absence of a garage, crawlspace, or attic.
DOE received several comments on
the space constraints for water heaters
with increased insulation thicknesses.
AHRI stated that the analysis does not
fully recognize the size constraints on
water heaters that have increased
insulation. (AHRI, No. 33 at p. 2) For
example, AHRI questioned DOE’s
assumption that space constraints do
not apply if the floor area of a house is
more than 1,000 square feet. (AHRI, No.
43 at p. 4) Rheem and AHRI stated that
DOE should consider the space
constraints of water heaters installed in
attics. (Rheem, No. 49 at p. 2; AHRI, No.
43 at p. 4) Rheem stated that space
constraints render larger products
economically and technically infeasible.
(Rheem, No. 49 at p. 1) EEI stated that
DOE should consider the effect of
adding insulation to electric storage
water heaters and the issue of space
constraints in replacement situations.
(EEI, No. 40 at p. 4) PG&E, San Diego
Gas and Electric (SDG&E), and SoCal
Gas stated that if the diameter of a water
heater is increased by 2 inches,
installation becomes unworkable in
highly constrained spaces. (PG&E,
SDG&E, and SoCal Gas, No. 38 at p. 3)
A.O. Smith stated that many closets
and cabinets do not have adequate
clearance to accommodate largerdiameter water heaters. It stated that
many electric storage water heaters
cannot accept larger-diameter tanks
without modifying the installation. A.O.
Smith added that in the South, many
water heater installations are in attics,
and larger water heaters may not fit
between the two ceiling joists in the
pull-down staircase to the attic. A.O.
Smith suggested that DOE’s analysis
should increase the number of
installations that would require
modification or the use of a small water
heater with a tempering valve. (A.O.
Smith, No. 37 at pp. 1–2)
In response to the above comments,
for the NOPR analysis, DOE further
investigated the issue of space
constraints for water heaters with
insulation thickness of 2 inches and
above. Based upon the results of this
inquiry, DOE expanded the percentage
of installations that may have space
constraints, including houses having a
floor area of more than 1,000 square
feet. For approximately 20 percent of
replacement installations, DOE applied
major modifications (removal of door
jamb at an average cost of $191) for
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water heater designs with 2-inch
insulation. For another 20 percent of
replacement installations, DOE assumed
that the household would install a
smaller water heater and use tempering
and check valves (at an average cost of
$142). DOE also added a cost for extra
labor needed to install water heaters in
attics, and for installing larger water
heaters (66 gallon and larger).
AHRI stated that the additional cost of
$22 for tempering and check valves
associated with installing an electric
water heater is significantly
understated. (AHRI, No. 43 at p. 4) In
clarification, DOE incorporated an
average cost of $142 for tempering and
check valves for homes where they
would be needed. The value of $22 is
an average over all homes, including
those where tempering and check valves
are not necessary.
AHRI stated that a survey conducted
by the SEGWHAI project in California
determined that the average installation
cost for a standard gas-fired storage
water heater approached $1,000, which
is higher than DOE’s estimated average.
(AHRI, Public Meeting Transcript, No.
34.4 at pp. 84–85) DOE used RS Means
and installation cost data to derive a
nationally-representative range of
installation costs, whereas the
SEGWHAI data pertain only to
California. Because of the need to set a
national standard, DOE has continued to
rely on RS Means as a recognized and
commonly used source for estimating
such costs.
AHRI also stated that DOE
underestimated the cost of condensing
gas-fired storage water heaters. AHRI
said that SEGWHAI estimated an
installed cost of $4,000, compared to
DOE’s estimate of $1,782. The
SEGWHAI estimate refers to a largecapacity commercial condensing unit
having an EF of 0.84. For a condensing
gas-fired storage water heater having an
EF of 0.82 (a more appropriate
comparison for the residential units at
issue here), SEGWHAI proposes a
$1,700 Tier 2 cost, which is comparable
to the estimated installed cost of the
0.77 EF unit considered in DOE’s
analysis.
NEEA and NPCC questioned why
DOE included the cost of installing an
electrical outlet in the cost of gas-fired
storage water heaters. (NEEA and NPCC,
No. 42 at p. 8) In response, DOE
understands that the baseline gas-fired
water heater requires no electricity. If
such a model is replaced with a higherefficiency unit, however, an electrical
outlet installation may be required.
The American Gas Association (AGA)
stated that the installation costs for gasfired storage water heaters having an EF
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65899
greater than 0.62 need to include the
cost of stainless steel vent connectors.
(AGA, No. 44 at p. 3) DOE agrees that
some models having an EF greater than
0.62 will require stainless steel vent
connectors, but only if the recovery
efficiency (RE) is 78 percent or higher.
For the NOPR analysis, DOE added the
cost of stainless steel vent connectors
for all natural draft gas-fired water
heaters that have an RE of 78 percent or
higher.
A.O. Smith stated that the installation
costs for electric storage water heaters at
all efficiency levels are overstated by a
factor of two. (A.O. Smith, No. 37 at p.
6) In response, DOE acknowledges that
the average installation costs for electric
storage water heaters presented in the
preliminary TSD were too high.
Consequently, for the NOPR analysis,
DOE updated the labor cost. Instead of
using national-average costs, DOE used
region-specific costs, which yield a
lower national-average cost for electric
water heaters. DOE also reduced the
labor time by one half hour. The result
is that the average installation cost for
electric storage water heaters is
approximately half as much as the cost
estimated in the preliminary analysis.
AGA stated that DOE’s cost estimate
for providing electrical supply to water
heaters that incorporate electronic
ignition is too low. AGA stated that DOE
should use the cost estimates in other
rulemakings for installations where
electrical service is needed. (AGA, No.
44 at pp. 3–4) DOE’s estimated cost for
adding electrical supply for water
heaters requiring electronic ignition,
which is based on RS Means, is similar
to the costs DOE used in the rulemaking
for cooking products (74 FR 16040
(April 8, 2009)) and other rulemakings
for installations that require electrical
service.
Rheem stated that the cost of
installing gas-fired, electric storage, and
low-boy electric water heaters in
manufactured housing units, where
water heaters are typically installed
under a counter, would be affected at
higher efficiency levels. (Rheem, No. 49
at p. 2) As discussed previously, DOE
considered and accounted for the cost of
accommodating space constraints that
may arise in some replacement
applications when higher-efficiency
units with thicker insulation are
installed. In the specific case of
manufactured homes, for the NOPR
DOE increased the fraction of
installations assumed to have space
constraints by two-fold.
Table IV.26 shows the average
installation costs used in the NOPR
analysis for selected efficiency levels
considered for gas-fired and electric
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storage water heaters. (Installation costs
for electric storage water heaters with
heat pump design are further discussed
below.) The costs vary with the location
of the water heater. For electric
resistance water heaters, the average
installation costs at different efficiency
levels are similar for basement and
garage locations, but they are higher for
water heaters of 0.95 EF for indoor and
attic locations. For gas-fired water
heaters, the average installation cost is
much higher for 0.67 EF and 0.80 EF
units because thereis a change from
metal Category I vents to plastic
Category IV vents.
TABLE IV.26—AVERAGE AND INCREMENTAL INSTALLATION COSTS FOR ELECTRIC AND GAS-FIRED STORAGE WATER
HEATERS
Electric
EF
0.90
0.91
0.93
0.95
Description
...................
and 0.92 ...
and 0.94 ...
...................
Gas-fired
Average installation cost
(2008$) *
Incremental installation cost
(2008$)
$222
241
259
282
........................
$19
36
60
1.5 in (Baseline)
2 and 2.25 in .....
2.5 and 3 in .......
4 in ....................
EF
0.59
0.62
0.63
0.67
0.80
Description
..................
..................
..................
..................
..................
Average installation cost
(2008$)*
Incremental installation cost
(2008$)
$576
595
621
808
828
........................
$19
46
233
252
Pilot, 1 in ...........
Pilot, 1.5 in ........
Pilot, 2 in ...........
Power vent, 2 in
Condensing, 2 in
* Average installation cost represents the weighted average cost for replacement and new construction applications.
DOE received several comments on
installation costs for heat pump water
heaters. In its preliminary analysis, DOE
applied a distribution of costs for heat
pump water heater installations in
enclosed spaces, including situations
where modifications would be required.
In its comments on the preliminary
analysis, GE stated that in general, heat
pump water heaters should be no more
difficult or expensive to install than
standard electric storage water heaters,
because they will require the same
electrical and plumbing connections. GE
noted that its heat pump water heater
occupies a footprint similar to that of a
standard unit. GE stated, however, that
it may be difficult to install a heat pump
water heater in a confined space that
lacks ventilation. (GE, No. 51 at p. 2)
A.O. Smith commented that the
requirements for providing adequate air
flow for a heat pump water heater may
be higher than DOE estimated. (A.O.
Smith, No. 37 at p. 1) NEEA and NPCC
stated that DOE should use a
distribution of costs to encompass heat
pump water heater installations that
require building modifications. (NEEA
and NPCC, No. 42 at p. 8)
DOE agrees that installation of heat
pump water heaters in enclosed spaces
may require modifications to allow for
adequate ventilation. Accordingly, for
half of indoor replacement installations,
DOE added a cost for installing a fullylouvered closet door to permit adequate
air flow for the operation of the unit. It
used a distribution of costs that averages
$344. In addition, DOE assumed that the
household facing space constraints
would install a smaller water heater and
use tempering and check valves in 20
percent of replacement installations.
DOE’s preliminary analysis
considered the fact that heat pump
water heaters draw heat from the space
in which they are located and release
cooled air. Thus, when such a water
heater is located in a conditioned space,
its use affects the load that the home’s
space heating and air conditioning
equipment must meet. DOE accounted
for the additional energy costs that
affected households would incur.
Southern commented that DOE had
not adequately considered the issues
Southern previously raised regarding
installing heat pump water heaters to
replace existing electric water heaters,
which included the need to provide
venting of cooled air released by such
units. The commenter also stated that
for new construction installations in
multifamily housing units, interior
locations are preferred for installing
mechanical systems. Southern
commented that a heat pump water
heater could be installed indoors, but it
would be costly to provide supply and
return vents to the exterior. (Southern,
No. 50 at pp. 2–3)
In the NOPR analysis, DOE continued
to assume that many households that
would be affected by indoor operation
of a heat pump water heater would not
want to incur the cost of a venting
system, and would instead operate their
heating and cooling systems to
compensate for the effects of the heat
pump water heater. However, DOE
agrees that some households would
prefer to install a venting system. DOE
estimated that those households that
would experience significant indoor
cooling due to operation of the heat
pump water heater in the heating
months (i.e., the heat pump cooling load
is greater than 10 percent of the space
heating load) would have a venting
system installed to exhaust and supply
air. Using calculations specific to each
household in the subsample for electric
water heaters, DOE estimated that 40
percent of replacement installations
would incur this cost, which averages
$460.
Table IV.27 shows the average
additional installation costs that DOE
applied for heat pump water heaters
(relative to the baseline electric storage
water heater), along with the fraction of
installations receiving each specific
cost.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
TABLE IV.27—ADDITIONAL INSTALLATION COSTS FOR HEAT PUMP WATER HEATERS
Share of
installations
impacted
(percent)
Installation cost description
Assignment to installations
Additional Labor ............................................................
Closet Door Redesign due to Space Constraints ........
All installations ..............................................................
50 of indoor and heated basement replacement installations.
20 of all replacement installations ................................
Tempering Valve Addition due to Space Constraints ..
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Average cost *
100
16
$69
344
16
142
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TABLE IV.27—ADDITIONAL INSTALLATION COSTS FOR HEAT PUMP WATER HEATERS—Continued
Share of
installations
impacted
(percent)
Installation cost description
Assignment to installations
Condensate Pump ........................................................
Venting Adder ** ...........................................................
25 of all replacement installations ................................
40 of replacement installations with significant cooling
load effects.
All installations ..............................................................
Larger Drain Pan ..........................................................
Average cost *
20
10
154
460
100
2
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
* Labor cost hours from 2008 RS Means; material cost from 2008 RS Means; condensate pump from retailer web sites; drain pan from 2001
TSD.
** All households experiencing significant cooling load effects in the heating season are either assigned the venting adder or the extra cost for
space heating is included in the energy use calculations.
In summary, for the NOPR analysis,
DOE used a distribution of installation
costs for heat pump water heaters
ranging from $213 to $1,918. The
estimated average installation cost for a
heat pump water heater (at 2.00 EF),
weighted over replacement and new
construction applications, is $446. This
compares to average costs of $222 for a
baseline (0.9 EF) electric storage water
heater and $282 for a 0.95 EF electric
storage water heater. For further details
on DOE’s derivation of installation costs
for electric storage water heaters, please
see chapter 8 of the NOPR TSD. DOE
requests comments on its analysis of
installation costs for water heaters; it is
particularly interested in comments on
its analysis of installation costs for heat
pump water heaters. This is identified
as issue 13 under ‘‘Issues on Which
DOE Seeks Comment’’ in section VII.E
of this NOPR.
Regarding installation of gas-fired
instantaneous water heaters, A.O. Smith
questioned whether DOE considered the
need for the pressure relief valve and
drain pans that manufacturers and
codes require. (A.O. Smith, No. 37 at p.
6) Noritz stated that gas-fired
instantaneous water heaters that achieve
an EF of 0.83 or higher require
condensate drains and some method of
treating the condensate so that it can be
disposed of, further adding to the
installation cost. (Noritz, No. 36 at pp.
1–2) For the NOPR analysis, DOE
included the cost and installation of a
drain pan and pressure relief valve, as
well as a filter for treating the
condensate for units with an EF of 0.83
or higher.
A.O. Smith questioned whether DOE
included the cost to replace a gas line
with a larger line when installing gasfired instantaneous water heaters in
replacement applications. (In some
cases the existing gas line is not
adequate to accommodate the higher gas
input required by the instantaneous
water heaters.) A.O. Smith also stated
that the analysis should include the
costs related to extreme installation
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situations for gas-fired instantaneous
water heaters, as DOE did for the costs
of adding tempering valves or modifying
door jams for electric storage water
heaters. (A.O. Smith, No. 37 at p. 6) In
response, DOE did not include the costs
of such measures for gas-fired
instantaneous water heaters, because in
those cases where these measures would
be required, the extremely high cost
would likely lead households to
purchase a storage water heater instead.
AHRI stated that DOE should
reconcile its cost estimates for installing
instantaneous water heaters with the
SEGWHAI estimate, which is at least
$200 to $300 more than DOE’s estimate.
(AHRI, Public Meeting Transcript, No.
34.4 at p. 168) As noted above, the
SEGWHAI data pertain only to
California, where labor costs are higher
than the national average. For the
NOPR, DOE used RS Means and
installation cost data to derive regionspecific installation costs.
b. Direct Heating Equipment
DOE used the approach in the 1993
TSD to calculate installation costs for
baseline direct heating equipment for its
preliminary analysis, as it believes that
the factors affecting DHE installation are
largely unchanged, and more recent data
are not available. For gas wall gravity,
floor, and room direct heating
equipment, DOE increased installation
costs for designs that require electricity.
DOE made this adjustment for the
replacement market only, because
wiring is considered part of the general
electrical work in new construction.
DOE did not receive comments on the
installation costs for direct heating
equipment, so it maintained the same
approach for the NOPR analysis. For
further details on DOE’s derivation of
installation costs for direct heating
equipment, please see chapter 8 of the
NOPR TSD.
c. Pool Heaters
DOE developed installation cost data
for the baseline pool heater in its
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preliminary analysis using RS Means
and information in a consultant’s report.
DOE incorporated additional
installation costs for designs involving
electronic ignition and/or condensing.
DOE did not receive comments on the
installation costs for pool heaters, so it
maintained this earlier approach for the
NOPR analysis. For further details on
DOE’s derivation of installation costs for
pool heaters, please see chapter 8 of the
NOPR TSD.
3. Annual Energy Consumption
DOE determined the annual energy
use in the field for the three types of
heating products based on data obtained
from RECS. DOE supplemented this
data as required for each heating
product, as discussed below.
a. Water Heaters
DOE calculated the annual energy
consumption of water heaters in the
sample households by considering the
primary factors that determine energy
use: (1) Hot water use per household; (2)
energy efficiency of the water heater;
and (3) operating conditions other than
hot water draws. DOE used a hot water
draw model to calculate hot water use
for each household in the sample. The
characteristics of each water heater’s
energy efficiency were obtained from
the engineering analysis. DOE
developed water heater operating
conditions (other than hot water draws)
from weather data and other relevant
sources. DOE used a simplified energy
equation, the water heater analysis
model (WHAM), to calculate the energy
use of water heaters. WHAM accounts
for a range of operating conditions and
energy efficiency characteristics. DOE’s
approach is explained in further detail
in chapter 7 of the NOPR TSD.
To estimate hot water use by each
sample household, DOE used a hot
water draw model that accounts for the
key factors that determine such use,
such as the number and ages of the
people who live in the household, the
way they consume hot water, the
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presence of hot-water-using appliances,
the tank size and thermostat set point of
the water heater, and the climate in
which the residence is situated. In
general, households with higher hot
water use have water heaters with larger
storage volume.
DOE received several comments on
hot water use. ACEEE stated that the hot
water draw model is insufficiently
supported by field data. (ACEEE, Public
Meeting Transcript, No. 34.4 at p. 178)
NEEA and NPCC stated that DOE should
provide more detail on the draw model
and explain how it has been validated
and calibrated. (NEEA and NPCC, No.
42 at p. 7) DOE acknowledges that
insufficient field data are currently
available to fully validate the draw
model. However, Electric Power
Research Institute (EPRI) developed the
draw model based on a nationally
representative sample of households. It
is DOE’s understanding that this widelyused model, which has been updated
several times to account for changes in
household hot water use, is the most
credible tool available for modeling
daily hot water use. The draw model is
described in detail in appendix 7–B of
this NOPR’s TSD, as well as in the
reports referenced in chapter 7 of the
TSD.
NEEA and NPCC stated that current
estimates of hot water use in the Pacific
Northwest are about 20 percent higher
than DOE’s estimate of national-average
daily use. (NEEA and NPCC, No. 42 at
p. 7) Household hot water use differs
among geographic regions for various
reasons. DOE’s analysis for Census
Division 9 (which includes the Pacific
Northwest) shows average hot water use
by electric water heaters (47.9 gal/day)
as being higher than the average
national value (41.9 gal/day). Therefore,
DOE believes that the estimates used in
its analysis are reasonable.
EEI stated that DOE should consider
the effects on hot water use of smaller
households and the lower hot water use
of new dishwashers and clothes
washers, which are installed in both
new and existing homes. (EEI, No. 40 at
p. 6) For the NOPR, DOE used the most
recent data available regarding
household characteristics (from the
2005 RECS). In addition, DOE modified
the hot water draw model to account for
the impact of the efficiency standards
that recently became effective for
dishwashers and clothes washers.
BWC commented that hot water usage
for gas-fired instantaneous water heaters
may be different than for storage water
heaters, although it has no evidence to
support this idea. (BWC, No. 46 at p. 1)
GE and Noritz stated that they are
unaware of any data that support the
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assumption that consumers use more
hot water with a gas-fired water heater.
(GE, No. 51 at p. 3; Noritz, No. 36 at p.
2) Because DOE found no usable data
showing greater or lesser hot water use
for instantaneous water heaters than for
storage water heaters, it estimated that
households use the same volume of hot
water with both types of water heaters.
Commenting on the calculation of
energy use, Bock stated that WHAM
does not accurately estimate energy
consumption. (Bock, No. 53 at p. 2) In
response, DOE notes that the WHAM
equation has been validated against
field data and that the comparison
shows that WHAM results correlate
well.
NEEA and NPCC stated that the
estimated energy use results could be
verified with sub-metered (i.e.,
measured) field data. (NEEA and NPCC,
No. 42 at p. 7) DOE found that the submetered field data for water heaters are
insufficient to represent the range of
national water heater energy use
patterns. Therefore, DOE did not
undertake such verification of its energy
use estimates.
AHRI and Bock stated that the
estimates of annual energy consumption
for gas- and oil-fired water heaters are
about 65 percent of test procedure usage
specifications, whereas for electric
water heaters it is 55 percent. AHRI
questioned why the analysis appears to
be using different field use assumptions
for electric water heaters. (AHRI, No. 33
at p. 2; Bock, No. 53 at p. 2) In response,
DOE’s analysis used 2005 RECS data to
estimate the energy consumption of
water heaters in use by U.S. households.
DOE’s analysis thereby incorporates
assumptions about operating conditions
that are appropriate for each water
heater type. For example, DOE
determined that the average annual
ambient temperature is higher for the
stock of electric water heaters than for
the stock of gas-fired water heaters. This
difference contributes to the lower
average energy use for electric water
heaters.
A.O. Smith stated that the analysis of
ambient air temperature effects does not
include water heaters installed in attics
in the South, and that the temperature
derivation formulas are not applicable
to attic installations, where solar gain
can bring temperatures to ambient plus
40 °F in summer. (A.O. Smith, No. 37
at pp. 5–6) DOE’s analysis included
water heaters installed in attics and
accounted for the range of temperatures
found in such locations.
The energy efficiency and
consumption of heat pump water
heaters depend on ambient temperature.
The equation DOE used to determine
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the energy consumption of heat pump
water heaters is similar to the WHAM
equation, but it modulates the recovery
efficiency by applying a performance
adjustment factor that is a function of
the average ambient temperature. GE
stated that because lower ambient
temperatures will affect the performance
of both heat pump and storage water
heaters, DOE should use universally
applied conditions to compare products.
(GE, No. 51 at p. 2) DOE’s energy
calculations for heat pump and storage
water heaters accounted for the effects
of lower ambient temperatures. Heat
pump water heaters are more affected by
air temperature because the air provides
the heat to warm the water.
As stated previously, DOE assumed
that many households that would be
affected by indoor operation of a heat
pump water heater would not want to
incur the cost of a venting system, and
would instead operate their space
heating or cooling system to compensate
for the effects of the heat pump water
heater. For each such home, DOE
estimated the impact on space heating
only during heating months (i.e., when
indoor temperature is at least 10 degrees
greater than the average outdoor
temperature), and the impact on air
conditioning only during cooling
months (i.e., when indoor temperature
is at least 5 degrees less than the average
outdoor temperature). For each affected
household in the electric water heater
sub-sample, DOE included such indirect
energy use in its calculation of the
energy consumption of a heat pump
water heater.
BWC stated that the assumed rated
capacity (Pon) of 500 watts and cooling
capacity of 3,500 Btu/h are not correct
for all heat pump water heaters. (BWC,
No. 46 at p. 2) For the preliminary
analysis, DOE based those values on
information available in AHRI’s 2007
Consumers’ Directory. For the NOPR,
DOE created a distribution of values for
Pon and cooling capacity that represent
a range of heat pump water heater
designs.
To calculate the energy use of gasfired instantaneous water heaters, DOE
used the same approach as for storage
water heaters, modified to account for
the absence of a tank. For the
preliminary analysis, DOE applied a
performance adjustment factor to
account for evidence that the rated
energy efficiency of instantaneous water
heaters overstates actual performance,
as reported in a study of instantaneous
water heater installations conducted for
the California Energy Commission
(CEC). See Davis Energy Group. Measure
Information Template: Tankless Gas
Water Heaters (May 18, 2006); https://
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www.energy.ca.gov/title24/
2008standards/prerulemaking/
documents/2006–05–18_workshop/
2006–05–11_GAS_WATER.PDF. The
adjustment factor effectively increases
the calculated energy use of a gas-fired
instantaneous water heater by 8.8
percent.
A.O. Smith noted its strong support
for incorporating results from the CEC
study to account for performance dropoff at small draw volumes. Because it
requires 5 to 20 seconds for a gas-fired
instantaneous water heater to heat up, 1
gallon of cold water can be wasted at the
beginning of every water draw. (A.O.
Smith, No. 37 at pp. 1, 5) ACEEE, PG&E,
SDG&E, SoCal Gas, and AGA also
support applying a performance
adjustment. (ACEEE, No. 35 at p. 7;
PG&E, SDG&E, and SoCal Gas, No. 38 at
p. 4; AGA, No. 44 at p. 3) BWC
expressed support for applying the 8.8percent adjustment factor to gas-fired
instantaneous water heaters, noting that
its testing indicates that this number
may be a little low. (BWC, No. 46 at p.
1) AHRI disagreed with applying an 8.8percent factor. AHRI stated that the CEC
study obtained its field data from one
two-person household, which does not
support a technically sound analysis.
(AHRI, No. 33 at p. 2) Bock, GE, Noritz,
and Rheem agreed. (Bock, No. 53 at p.
2; GE, No. 51 at p. 3; Noritz, No. 36 at
p. 2; Rheem, No. 49 at pp. 6–7)
For the NOPR analysis, the
performance adjustment factor DOE
developed to capture the field energy
use of gas-fired instantaneous water
heaters is a probability distribution. The
factor changes based on household hot
water consumption, rather than on a
fixed value that may represent only a
fraction of households. The 8.8-percent
adjustment factor DOE used for the
preliminary analysis became the upper
value in the distribution DOE used for
the NOPR. The rest of the range was
derived from a Gas Technology Institute
(GTI) study that calculated an energy
use reduction (adjustment) factor as a
function of the volume of water gasfired instantaneous water heaters use
daily.
Southern stated that the draws in the
hot water draw model should ideally be
shorter for instantaneous water heaters.
(Southern, Public Meeting Transcript,
No. 34.4 at p. 194) ACEEE stated that
PG&E and Consumers Union have
performed studies on alternative draw
patterns for gas-fired instantaneous
water heaters that are more reflective of
daily use. (ACEEE, Public Meeting
Transcript, No. 34.4 at pp. 195–196) In
response, DOE’s performance
adjustment factor accounts for a range of
draw patterns associated with gas-fired
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instantaneous water heaters.
Accordingly, DOE maintains its existing
approach.
b. Direct Heating Equipment
For the preliminary analysis of LCC
and PBP, DOE estimated energy
consumption of direct heating
equipment in functioning housing units.
To represent actual households likely to
purchase and use direct heating
equipment, DOE developed a household
sample from the 2001 RECS. DOE did
not receive any comments on its
approach for estimating energy
consumption of direct heating
equipment. Therefore, for the NOPR,
DOE used the same approach, but it
used a household sample drawn from
the 2005 RECS.
c. Pool Heaters
For the preliminary analysis of LCC
and PBP, DOE estimated energy
consumption of pool heaters at
functioning housing units. To represent
actual households likely to purchase
and use pool heaters, DOE used a
household sample from the 2001 RECS.
For the NOPR, DOE used a household
sample drawn from the 2005 RECS.
AHRI stated that DOE’s estimate of
the annual energy use of a typical
residential pool heater is overestimated
by a factor of two. It said that DOE’s
estimated annual energy use of 53.6
MBtu [one thousand British thermal
units] based on an energy use of 250
kBtu/h at 78 percent thermal efficiency
(a baseline unit) represents 214 hours of
operation annually. AHRI mentioned a
CEC study that determined that gas pool
heaters were used on average 104 hours
per year, and it commented that the LCC
should be recalculated based on that
value. (AHRI, No. 43 at p. 5)
In response, DOE notes that the CEC
study mentioned is based on a single
study conducted in the early 1990s. For
the NOPR, DOE did revise the range of
operating hours used its analysis,
although it relied on more recent data
than the referenced CEC study. Instead,
DOE calculated the pool heater
operating hours using the estimated
pool heater heating load for each sample
household from the 2005 RECS. The
average hours of operation in the NOPR
analysis is 149 per year, which results
in an annual energy use of 38 MBtu for
a 250 kBtu/hr baseline unit operating at
78 percent thermal efficiency.
d. Rebound Effect
A rebound effect refers to increased
energy consumption resulting from
actions that increase energy efficiency
and reduce consumer costs. For its
preliminary analysis, DOE searched the
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literature on the rebound effect related
to the three types of heating products,
and also considered how EIA’s NEMS
incorporates a rebound effect.
For water heaters, DOE reviewed a
summary of studies on the rebound
effect, which concluded that ‘‘technical
improvements for residential hot water
heating will be between 60 and 90
percent effective in reducing energy
consumption for this service’’ (implying
a rebound effect of 10 to 40 percent).
See L.A. Greening, D.L. Greene, C.
Difiglio, Energy Efficiency and
Consumption: The Rebound Effect,
Energy Policy, 28(6–7): pp. 389–401.
DOE found that NEMS does not
incorporate a rebound factor, however.
Balancing these findings from the
literature with the zero rebound effect
used in NEMS, DOE decided that a
rebound effect of 10 percent was
reasonable for water heaters.
A.O. Smith supported the use of a 10percent rebound effect for water heaters.
(A.O. Smith, No. 37 at p. 2) It added that
there is an additional rebound effect for
gas-fired instantaneous water heaters
because of the promotion of
‘‘unlimited’’ or ‘‘endless’’ hot water.
(A.O. Smith, No. 37 at p. 7) NEEA and
NPCC suggested that DOE ignore the
rebound effect except in the case of the
highest candidate standard levels, as
adoption of the lower efficiency levels
would not provide consumers with
noticeable savings in energy bills.
(NEEA and NPCC, No. 42 at p. 8) ACEEE
stated that it does not believe that the
peer-reviewed literature supports
assertions of large rebound effects, and
the more conservative approach is to
ignore them for these products. (ACEEE,
No. 35 at p. 7)
As stated above, the literature does
indicate the presence of a rebound effect
of 10 to 40 percent for water heaters.
Given that NEMS does not incorporate
a rebound effect for water heating, and
that the comments received on the
preliminary analysis support a rebound
effect of 10 percent or lower, DOE
believes that using a value at the lower
end of the range found in the literature
(i.e., 10 percent) is reasonable and has
incorporated such an effect in its
analyses for this NOPR.
4. Energy Prices
For the LCC and PBP, DOE derived
average energy prices for 13 geographic
areas consisting of the nine U.S. Census
divisions, with four large States (New
York, Florida, Texas, and California)
treated separately. For Census divisions
containing one of these large States,
DOE calculated the regional average
excluding the data for the large State.
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DOE estimated residential electricity
prices for each of the 13 geographic
areas based on data from EIA Form 861,
‘‘Annual Electric Power Industry
Database,’’ and EIA Form 826, ‘‘Monthly
Electric Utility Sales and Revenue
Data.’’ DOE calculated an average
annual regional residential electricity
price by: (1) Estimating an average
residential price for each utility (by
dividing the residential revenues by
residential sales); and (2) weighting
each utility by the number of residential
consumers served in that region (based
on EIA Form 861). DOE calculated an
average monthly regional electricity
price by first calculating monthly prices
for each State, and then calculating a
regional price by weighting each State
in a region by the number of consumers
in that State using EIA Form 826. For
the preliminary TSD, DOE used EIA
data from 2006. The NOPR analysis
used the data from 2007.
DOE estimated average residential
natural gas prices in each of the 13
geographic areas based on data from
EIA’s Natural Gas Navigator. See Energy
Information Administration, Natural
Gas Navigator, 2009; https://
tonto.eia.doe.gov/dnav/ng/ng_pri_sum_
dcu_nus_m.htm. DOE calculated an
average natural gas price by first
calculating the price for each State, and
then calculating a regional price by
weighting each State in a region by the
number of consumers in that State. This
method differs from the method DOE
used to calculate electricity prices,
because EIA does not provide utilitylevel data on gas consumption and
prices. For the preliminary TSD, DOE
used EIA data from 2006. For today’s
proposed rule, DOE used the data from
2007.
DOE estimated average residential
prices for liquefied petroleum gas (LPG)
in each of the 13 geographic areas based
on data from EIA’s State Energy
Consumption, Price, and Expenditures
Estimates. See Energy Information
Administration, 2007 State Energy
Consumption, Price, and Expenditure
Estimates (SEDS); https://
www.eia.doe.gov/emeu/states/
_seds.html. For the preliminary TSD,
DOE used data from 2005. For today’s
proposed rule, DOE used the data from
2006.
DOE estimated average residential
prices for oil in each of the 13
geographic areas based on data from
EIA’s Petroleum Navigator. See Energy
Information Administration, Petroleum
Navigator, December, 2009; https://
tonto.eia.doe.gov/dnav/pet/pet_cons_
821dsta_a_EPD0_VAR_Mgal_a.htm. For
the preliminary TSD, DOE used data
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from 2006. For today’s proposed rule,
DOE used the data from 2007.
To estimate the trends in energy
prices for the preliminary TSD, DOE
used the price forecasts in AEO2008. To
arrive at prices in future years, DOE
multiplied current average regional
prices by the forecast of annual average
price changes in AEO2008. Because
AEO2008 forecasts prices to 2030, DOE
followed past guidelines that EIA
provided to the Federal Emergency
Management Program. DOE used the
average rate of change from 2020 to
2030 to estimate the price trend for
electricity after 2030, and the average
rate of change from 2015 to 2030 to
estimate the price trend after 2030 for
natural gas, LPG, and oil. For today’s
proposed rule, DOE used the same
approach, but updated its energy price
forecasts using AEO2009. DOE intends
to update its energy price forecasts for
the final rule based on the latest
available AEO. In addition, the
spreadsheet tools that DOE used to
conduct the LCC and PBP analyses
allow users to select price forecasts from
either AEO’s high-growth scenario or
low-growth scenario to estimate the
sensitivity of the LCC and PBP to
different energy price forecasts.
Earthjustice stated that DOE must
quantify the effect of a CO2 emissions
cap on energy prices in the LCC
analysis. (Earthjustice, No. 47 at p. 4)
DOE believes that it would be
inappropriate to speculate on the form
of any Federal carbon control
legislation, and the ensuing impacts on
residential energy prices. Therefore,
DOE does not incorporate such impacts
into the energy price forecasts that DOE
used for the NOPR analysis.
5. Repair and Maintenance Costs
Repair costs are associated with
repairing or replacing components that
have failed in the appliance, whereas
maintenance costs are associated with
maintaining the operation of the
equipment. Determining the repair cost
involves determining the cost and the
service life of the components that are
likely to fail. Discussion of repair and
maintenance costs for the three types of
heating products is provided below,
along with a summary of public
comments on this topic. For more
information on DOE’s development of
repair and maintenance cost estimates,
see chapter 8 of the NOPR TSD.
a. Water Heaters
The repair cost for a water heater
reflects the cost for a service call when
the product fails. There are four design
options considered for the gas-fired
water heater analysis that may
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encounter repair cost during the lifetime
of the water heater: (1) Pilot ignition; (2)
electronic ignition; (3) power vent; and
(4) condensing design. The energy
efficiency levels that include power
vent or condensing design encounter
both power vent as well as electronic
ignition repair costs. For each of the
above four design options, DOE
estimated both an average cost and the
year in which the repair would, on
average, be most likely to occur.
AHRI stated that DOE’s analysis of
gas-fired water heaters ignored the
introduction of FVIR designs that
require maintenance. (AHRI, No. 43 at
pp. 1–2) For the NOPR, DOE added a
cost for maintaining the FVIR for all gasfired storage water heaters.
For the preliminary analysis, DOE
determined that there is virtually no
maintenance or repair associated with
conventional electric resistance water
heaters. For a heat pump water heater,
maintenance includes annual cleaning
of the air filter and a preventive
maintenance cost to check the
evaporator and refrigeration system.
Although the literature suggests that no
professional help is necessary for this
maintenance, DOE believes there are
instances in which such help is needed.
For some locations where the heat
pump water heater might be more
exposed to the outdoor environment,
such as garages and crawlspaces, DOE
applied a 5-year preventative
maintenance cost based on experience
with heat pump water heater outdoor
installations in Australia, which has
roughly comparable conditions as much
of the United States. See Rheem
Manufacturing Company (Australia),
Owners Guide and Installation
Instruction: Air Sourced Heat Pump
Water Heater, 2006; https://
www.rheem.com.au/images/pdf/
owners_heatpump_126524B_0610.pdf.
DOE estimated that 27 percent of these
exposed installations would require this
maintenance, based on a survey
conducted for central air conditioners,
which include heat exchangers that
operate similarly as the evaporator heat
exchanger in a heat pump water heater.
ACEEE recommended that DOE use
refrigerator maintenance costs for heat
pump water heaters because of
similarities in the components and
operation. (ACEEE, No. 35 at p. 6) A.O.
Smith stated that the cost for regular
and routine maintenance on heat pump
water heaters must be considered. It
added that it is inaccurate to compare a
heat pump water heater to a refrigerator
due to the much longer duty cycle on
a heat pump water heater, the slow
recovery time, the need for frequent
cleaning, and the scale build-up on the
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water side, which is not an issue with
refrigerators. (A.O. Smith, No. 37 at p.
8) GE stated that DOE ascribed
inappropriate maintenance costs to heat
pump water heaters, which require no
more attention than a standard room air
conditioner. (GE, No. 51 at p. 2)
In response, DOE notes that it based
its maintenance costs for heat pump
water heaters on experience in
Australia, so it is not necessary to use
another appliance as a proxy. DOE
acknowledges that many heat pump
water heaters may require little or no
maintenance. However, DOE believes
that because the field experience with
heat pump water heaters is limited, it is
reasonable to apply a maintenance cost
for some installations. As described
above, DOE applied a 5-year
preventative maintenance cost for 27
percent of the installations in garages
and crawlspaces.
Regarding repair of conventional
electric resistance water heaters, ACEEE
stated that data may be available on the
number of resistive elements that need
to be replaced. (ACEEE, Public Meeting
Transcript, No. 34.4 at p. 211) Based on
this comment, for the NOPR, DOE
added a cost for replacing resistive
elements at least once during the
lifetime for one-fourth of installations.
For heat pump water heaters, DOE
considered the cost of replacing the
compressor and the evaporator fan and
the year in which, on average, they
would be expected to fail. DOE used a
lifetime distribution for the compressor
and evaporator fan with an average
lifetime of 19 years. For the majority of
households, the compressor and
evaporator fan would likely not fail
during the water heater’s lifetime.
However, because there is some overlap
between the lifetime distribution used
for the compressor and evaporator fan
and the lifetime distribution used for
electric water heaters (see below), DOE
included a compressor and evaporator
fan repair cost in the appropriate year
for some households. DOE requests
comments on its analysis of repair and
maintenance costs for heat pump water
heaters. This is identified as issue 14
under ‘‘Issues on Which DOE Seeks
Comment’’ in section VII.E of this
NOPR.
Regarding repair costs of gas-fired
instantaneous water heaters, AGA stated
that DOE needs to account for
incremental design options, particularly
electronic ignition maintenance and
replacement. (AGA, No. 44 at p. 4) In its
preliminary analysis, DOE already
applied a distribution of costs for
electronic ignition repair based on RS
Means. It maintained the same approach
for the NOPR analysis.
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For the preliminary analysis, DOE
applied a maintenance cost for some
gas-fired instantaneous water heaters to
address the fouling of the heat
exchanger from hard water, periodic
sensor inspections, and filter changes.
A.O. Smith stated that $85 per year is
too low for annual maintenance (deliming) for gas-fired instantaneous water
heaters. (A.O. Smith, No. 37 at p. 7) In
response, for the NOPR, DOE used a
distribution of costs for maintenance of
gas-fired instantaneous water heaters,
not a single cost of $85, and also applied
no cost for some installations.
Noritz stated that the basis for
including de-liming costs for gas-fired
instantaneous water heaters is clauses in
the warranty, which is standard for all
water heaters, so de-liming costs should
not be included only for gas-fired
instantaneous water heaters. (Noritz,
No. 36 at p. 2) Noritz stated that the
necessity for de-liming varies, so it
would be best not to include the cost for
any class of water heater, but if it is
included for gas-fired instantaneous
water heaters, DOE should account for
the fact that it is not necessary for every
installation. (Noritz, No. 36 at pp. 2–3)
DOE agrees that de-liming is not
necessary for every installation, so in
the NOPR analysis, it assigned zero cost
to a fraction of households.
For the preliminary analysis, DOE
determined that maintenance for oilfired water heaters is most frequently
performed under annual maintenance
contracts, which typically include
repair of failed components. DOE
estimated the average cost of separate
maintenance/repair contracts only for
water heaters as $153 per year. This
mean value comes from a collection of
annual maintenance contract prices,
which were gathered from web sites that
represent oil-fired product suppliers in
the eastern U.S. The same maintenance
cost applies to all energy efficiency
levels. DOE did not receive any
comments on this topic, so it
maintained the same approach for the
NOPR analysis.
Bock stated that DOE did not include
the cost of annually flushing oil-fired
storage water heaters. (Bock, No. 53 at
p. 2) For the NOPR, DOE included a cost
for flushing the tanks of all storage
water heaters, including oil-fired storage
water heaters.
b. Direct Heating Equipment
For the preliminary analysis, DOE
determined that maintenance cost data
for gas-fired furnaces provide a
reasonable approximation of
maintenance costs for DHE because of
the similarity in design and operation.
DOE derived the costs from a field
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survey sponsored by several gas utilities
that estimated the average total service
charge (parts, labor, and other charges).
See Jakob, F. E., et al., Assessment of
Technology for Improving the Efficiency
of Residential Gas Furnaces and Boilers,
1994. Gas Research Institute. Chicago,
IL. Report No. GRI–94/0175. DOE used
a maintenance frequency of once every
5 years for all direct heating equipment.
DOE determined the repair costs for
DHE using an approach that reflects the
cost and the service life of the
components that are likely to fail. The
non-condensing designs DOE
considered that may encounter repair
costs during the lifetime of the product
include pilot ignition, electronic
ignition, circulating blower, and
induced draft. The repair cost of the
condensing design includes electronic
ignition, circulation blower, and
induced draft components. DOE did not
receive comments on maintenance and
repair costs for DHE, so it continued to
use the existing approach for its NOPR
analysis.
c. Pool Heaters
For the preliminary analysis, DOE
determined that most pool owners do
not perform any pool heater
maintenance except when the heater
does not come on. In such situations,
the maintenance work includes
checking controls, cleaning burners,
cleaning the heat exchanger, starting the
heater, and measuring water
temperature rise. DOE used an average
cost of $351. For units employing power
vent and condensing design options,
maintenance also includes measuring
combustion differential pressure. For
these units, DOE used an average cost of
$491 and estimated that the
maintenance occurs on average in the
fifth year of the pool heater lifetime.
Raypak stated that pool heaters need
maintenance more than every 5 years
due to outdoor installation. (Raypak,
Public Meeting Transcript, No. 34.4 at p.
215) DOE applied a distribution ranging
from 3 to 6 years for pool heater
maintenance. Thus, some applications
would receive maintenance more than
once every 5 years.
Pool heater design options that may
encounter repair cost during the lifetime
of the pool heater include pilot ignition,
electronic ignition, and power vents.
For each of these, DOE estimated the
average repair cost and when in the
product lifetime such repair would be
likely to occur. DOE continued to use
the above approach for the NOPR
analysis.
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6. Product Lifetime
For the preliminary analysis, DOE
used a variety of sources to establish
minimum, average, and maximum
values for the lifetime of each of the
three types of heating products. For
each product class, DOE characterized
the product lifetime using a Weibull
probability distribution that ranged from
minimum to maximum lifetime
estimates. See chapter 8 of the NOPR
TSD for further details on the sources
DOE used to develop product lifetimes.
For the preliminary TSD, DOE chose
average lifetimes for gas-fired and
electric storage water heaters based on
the values in the middle of each range:
12 years for gas units and 14 years for
electric units. In the NOPR analysis,
DOE found that applying the above
values to historic shipments resulted in
estimates of the stock of gas-fired and
electric storage water heaters that did
not match the data on the stock reported
in the Census Bureau’s 2007 American
Housing Survey (AHS), which covers all
housing units in the United States. The
estimated stock is too small for gas-fired
water heaters and too large for electric
water heaters. Using an average lifetime
of 13 years for both gas-fired and
electric storage water heaters produces
stock estimates for 2007 that are close to
the stock numbers from the AHS.
Furthermore, several sources report a
lifetime of 13 years. (See chapter 8 of
the NOPR TSD.) Therefore, DOE used an
average lifetime of 13 years for both gasfired and electric storage water heaters
in its NOPR analysis.
DOE evaluated whether electric heat
pump water heaters have a different
lifetime from the baseline products. An
accelerated durability test of heat pump
water heaters conducted by Oak Ridge
National Laboratory suggests that these
units have similar lifetime as standard
electric resistance storage water heaters.
Therefore, DOE used the same lifetime
for all efficiency levels considered for
this product class.
For gas-fired instantaneous water
heaters, DOE used a distribution with 20
years as the average lifetime for these
units in its preliminary analysis. A.O.
Smith stated that a 20-year lifetime for
gas-fired instantaneous water heaters is
too long, and there is not adequate data
to backup this claim. (A.O. Smith, No.
37 at p. 2) BWC stated that DOE’s
average lifetime for gas-fired
instantaneous water heaters is derived
from manufacturer literature and it
suggested that DOE instead use an
independent source for this information.
(BWC, No. 46 at p. 2) DOE is not aware
of and the commenters did not provide
any other source of data on the lifetime
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of gas-fired instantaneous water heaters,
so it used the same distribution as in the
preliminary analysis.
For oil-fired storage water heaters,
DOE used 9 years as the average
lifetime. Bock stated that oil-fired
storage water heaters should have the
same lifetime as gas-fired storage water
heaters because they are identical in
material, construction, volume, and
storage temperature. (Bock, No. 53 at p.
2) For the NOPR analysis, DOE used the
same lifetime for oil-fired storage water
heaters as for gas-fired storage water
heaters (i.e., 13 years).
For direct heating equipment, DOE
used the average, minimum, and
maximum lifetime values from its 1993
TSD for direct heating equipment
because it did not find more recent
representative data. The average lifetime
DOE used for each of the product
classes was 15 years. DOE did not
receive any comments on DHE lifetime,
so it continued to use the above values
for the NOPR.
For pool heaters, DOE used 8 years as
an average lifetime based on the
available data. DOE did not receive any
comments on pool heater lifetime, so it
continued to use the above value for the
NOPR.
7. Discount Rates
To establish discount rates for the
heating products in the preliminary
analysis, DOE derived estimates of the
finance cost of purchasing these
appliances. Because the purchase of
equipment for new homes entails
different costs for consumers than the
purchase of replacement equipment,
DOE used different discount rates for
new construction and replacement. See
chapter 8 of this NOPR’s TSD for further
details on the development of discount
rates for heating products.
DOE estimated discount rates for
appliance purchases in new housing
using the effective real mortgage rate for
homebuyers, which accounts for
deducting mortgage interest for income
tax purposes, and an adjustment for
inflation. DOE developed a distribution
of mortgage interest rates using data
from the Federal Reserve Board’s
‘‘Survey of Consumer Finances’’ (SCF)
for 1989, 1992, 1995, 1998, 2001, and
2004. For today’s NOPR, DOE added
data from the 2007 SCF. Because the
mortgage rates carried by households in
these years were established over a
range of time, DOE believes they are
representative of rates that may apply
when amended standards take effect.
The effective real interest rates on
mortgages across the six surveys
averaged 3.0 percent.
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DOE’s approach for deriving discount
rates for replacement purchases
involved identifying all possible debt or
asset classes that might be used to
purchase replacement products,
including household assets that might
be affected indirectly. DOE used data
from the surveys mentioned above to
estimate the average percentages of the
various debt and equity classes in the
average U.S. household portfolios. DOE
used SCF data and other sources to
develop distributions of interest or
return rates associated with each type of
equity and debt. For today’s NOPR, DOE
added data from the 2007 SCF. The
average rate across all types of
household debt and equity, weighted by
the shares of each class, is 4.8 percent.
8. Compliance Date of the Amended
Standards
In the context of EPCA, the
compliance date is the future date when
parties subject to the requirements of a
new standard must begin to comply. As
described in DOE’s semi-annual
implementation report for energy
conservation standards activities
submitted to Congress pursuant to
section 141 of EPACT 2005, a final rule
for the three types of heating products
that are the subject of this rulemaking is
scheduled to be completed by March
2010. Compliance with amended energy
efficiency standards for direct heating
equipment and pool heaters is required
three years after the final rule is
published in the Federal Register (in
2013); compliance with amended
standards for water heaters is required
five years after the final rule is
published (in 2015). DOE calculated the
LCC for the three types of heating
products as if consumers would
purchase new products in the year
compliance with the standard is
required.
Earthjustice stated that DOE assumes
a 5-year lead time to be consistent with
the requirements in 42 U.S.C.
6295(e)(4)(B), which requires that DOE
‘‘publish a final rule no later than
January 1, 2000 to determine whether
standards in effect * * * should be
amended,’’ and that ‘‘any such
amendment shall apply to products
manufactured on or after January 1,
2005.’’ The commenter stated that this
assumption is contrary to the structure
and purpose of the statute. It also
declared that there is no statutory
language to deal with the current
situation, which involves determining a
compliance date for a standard that DOE
was required to adopt nearly 10 years
ago. Earthjustice stated that the required
publication date and compliance dates
have passed, and that it is unreasonable
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consumers purchase under the base case
(i.e., the case without new energy
efficiency standards). DOE refers to this
distribution as a base-case efficiency
distribution. Using the projected
distribution of product efficiencies for
each heating product, DOE randomly
assigned a specific product efficiency to
each sample household. If a household
was assigned a product efficiency
greater than or equal to the efficiency of
the standard level under consideration,
the LCC calculation shows that this
household is not affected by that
standard level. Each of the three types
of heating products is addressed below,
including relevant public comments and
DOE’s response. For further information
on DOE’s estimation of base-case market
shares, see chapter 8 of the NOPR TSD.
to apply the 5-year lead time specified
in 42 U.S.C. 6295(e)(4)(B). (Earthjustice,
No. 47 at p. 5) ASAP stated that DOE’s
compliance date of 2015 is arbitrary
because the law states that compliance
with the standard is required by 2005.
ASAP stated that DOE is obligated to
use time as a variable and look at a
range of implementation dates for all of
the standard levels to determine the
standard that would best meet the
statutory criteria. ASAP suggested that
DOE analyze a range of compliance
dates from 18 months to 8 years after
publication of the final rule. (ASAP,
Public Meeting Transcript, No. 34.4 at
pp. 57–58) AHRI stated that DOE is
obligated to allow five years between
the final rule and the compliance date
for the requirements for water heater
products. (AHRI, Public Meeting
Transcript, No. 34.4 at pp. 60–61)
In response, DOE notes that the
language in 42 U.S.C. 6295(e)(4)
specifically states that amended
standards, if any, shall apply to
products manufactured on or after the
36-month period beginning on the date
such a final rule is published for the
first iteration of rulemaking and on or
after the 60-month period beginning on
the date such a final rule is published
for the second iteration of rulemaking.
(42 U.S.C. 6295(e)(4)(A)–(B)) The
language of 42 U.S.C. 6295(e)(4)(B)
anticipates that a standard will be in
place for covered water heaters that are
manufactured precisely five years after
publication of the final rule and
prospectively thereafter. DOE believes
that the time differential, as specified in
EPCA, between the publication of the
final rule and the compliance deadline
reflects Congress’s judgment as to what
constitutes adequate lead time.
a. Water Heaters
In its preliminary analysis, DOE
estimated the base-case market shares of
various energy efficiency levels for
water heaters in the effective year. DOE
began with data on shipments for 2002–
2006 from AHRI, supplemented with
data on the number of water heater
models at different energy efficiency
levels reported in AHRI directories and
the Federal Trade Commission
directory. (See chapter 8 of the NOPR
TSD for citations for these data sources.)
For gas-fired and electric storage water
heaters, DOE then estimated the future
market impact of the ENERGY STAR
program. Effective in 2010, the
minimum efficiency for the ENERGY
STAR designation will be 0.67 EF for
non-condensing gas-fired storage water
heaters, 0.80 EF for condensing gas-fired
storage water heaters, and 2.0 EF for
heat pump water heaters. To estimate
the base-case market shares of these
products, DOE considered the market
penetration goals set by the ENERGY
STAR program.
For gas-fired instantaneous water
heaters, DOE estimated that the basecase market shares in 2015 would be
equivalent to current shares. In the case
of this product, the majority of the
9. Product Energy Efficiency in the Base
Case
To accurately estimate the percentage
of consumers who would be affected by
a particular standard level, DOE’s
analysis considered the projected
distribution of product efficiencies that
65907
market (approximately 85 percent of
shipments) is already at the ENERGY
STAR level, so there is limited room for
the shares of ENERGY STAR products to
increase in the near future. For oil-fired
storage water heaters, DOE also
estimated that the market shares in 2015
would be equivalent to current shares,
as there has been little change in the
past decade.
Southern and EEI stated that the 5percent market share DOE projected for
heat pump water heaters under the base
case seems too high. (Southern, Public
Meeting Transcript, No. 34.4 at p. 186;
EEI, No. 40 at p. 5) GE stated that based
on the expansion of the market for frontloading clothes washers, which was a
new higher-efficiency product in the
U.S. market with higher first cost but
much lower operating costs, the
predicted 5-percent market share for
heat pump water heaters is not
unreasonable. (GE, Public Meeting
Transcript, No. 34.4 at pp. 188–189) In
response, DOE notes that, consistent
with manufacturer predictions, heat
pump water heaters entered the mass
market in 2009. Given the high level of
interest in promoting ENERGY STARqualified appliances, DOE believes that
its projection was reasonable, and it
used the same market share for the
NOPR analysis.
For oil-fired storage water heaters,
Bock stated that the market shares for
Efficiency Level 5 and 6 are much
higher than indicated in the preliminary
TSD. (Bock, No. 34.4 at pp. 187–188)
For the NOPR, DOE updated its basecase efficiency distribution to reflect
data from the March 2009 AHRI
directory of certified products, which
resulted in a higher market share at
levels 5 and 6.
DOE’s projected base-case energy
efficiency market shares are shown in
Table IV.28. These market shares
represent the products that households
would purchase in 2015 in the absence
of revised energy conservation
standards.
TABLE IV.28—WATER HEATERS: BASE-CASE ENERGY EFFICIENCY MARKET SHARES
Gas storage
Market
share (%)
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EF
0.59
0.62
0.63
0.64
0.65
0.67
0.80
........................
........................
........................
........................
........................
........................
........................
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87.2
3.0
0.9
1.2
1.4
5.3
1.0
20:45 Dec 10, 2009
Market
share (%)
EF
0.90 .......................
0.91 .......................
0.92 .......................
0.93 .......................
0.94 .......................
0.95 .......................
2.0 .........................
2.2 .........................
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8.7
19.5
2.5
2.5
4.0
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EF
0.53
0.54
0.56
0.58
0.60
0.62
0.66
0.68
Gas-fired instantaneous
Market
share (%)
.......................
.......................
.......................
.......................
.......................
.......................
.......................
.......................
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0.0
0.0
0.0
11.1
16.7
40.0
10.0
EF
0.62
0.69
0.78
0.80
0.82
0.84
0.85
0.92
11DEP2
.......................
.......................
.......................
.......................
.......................
.......................
.......................
.......................
Market
share (%)
0.3
1.8
1.0
12.2
62.9
2.8
3.8
9.5
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Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
TABLE IV.28—WATER HEATERS: BASE-CASE ENERGY EFFICIENCY MARKET SHARES—Continued
Gas storage
Electric storage
Market
share (%)
EF
Oil storage
Market
share (%)
EF
EF
Gas-fired instantaneous
Market
share (%)
EF
0.95 .......................
100
100
b. DHE
Little is known about the efficiency
distribution of direct heating equipment
that consumers in the United States
currently purchase. For the preliminary
analysis, DOE estimated the market
shares of different energy efficiency
levels within each product class in the
base case using data in the March 2007
GAMA directory. DOE did not receive
any comments on its estimation of basecase market shares for DHE. It employed
the same approach for its NOPR
analysis, but used more recent GAMA
data on the number of models at
different energy efficiency levels. See
Gas Appliance Manufacturers
Association, Consumer’s Directory of
Certified Efficiency Ratings for Heating
and Water Heating Equipment (March
2008); https://www.gamanet.org/gama/
inforesources.nsf/vAllDocs/
Product+Directories?OpenDocument.
c. Pool Heaters
No shipments data are available on
the distribution of gas-fired pool heaters
by energy efficiency level. For the
preliminary TSD, DOE estimated the
market shares of different energy
efficiency levels in the base-case by
using data from the FTC on the number
of gas-fired pool heater models at
different energy efficiency levels as a
proxy for shipments. DOE did not
receive any comments on its estimation
of base-case market shares for pool
heaters. It employed the same approach
for the NOPR analysis, but used more
recent FTC data on the numbers of
models at various energy efficiency
levels.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
10. Inputs to Payback Period Analysis
The payback period is the amount of
time it takes the consumer to recover the
additional installed cost of moreefficient products, compared to baseline
products, through energy cost savings.
The simple payback period does not
account for changes in operating
expense over time or the time value of
money. Payback periods are expressed
in years. Payback periods that exceed
the life of the product mean that the
increased total installed cost is not
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100
recovered in reduced operating
expenses.
The inputs to the PBP calculation are
the total installed cost of the equipment
to the customer for each efficiency level
and the annual (first-year) operating
expenditures for each efficiency level.
The PBP calculation uses the same
inputs as the LCC analysis, except that
energy price trends and discount rates
are not needed.
NEEA and NPCC stated that that they
are concerned about how the payback
period was calculated for efficiency
level 3 for gas-fired instantaneous water
heaters (0.80 EF) because of the lengthy
payback period. (NEEA & NPCC, No. 42
at p. 2) In response, DOE notes that
almost the entire market is at CSL 3 or
higher. Therefore, the PBP that DOE
calculated applies only to the very few
households that would be affected by a
standard at this level. There is a
significant cost differential in going
from CSL 1 and 2 to CSL 3, which leads
to very high PBPs for the affected
households.
11. Rebuttable-Presumption Payback
Period
The PBP analysis helps to determine
whether the 3-year rebuttable
presumption of economic justification
applies—that is, whether the purchaser
will recover the higher installed cost of
more-efficient equipment through
lowered operating costs within 3 years.
(42 U.S.C. 6295(o)(2)(B)(iii)) For each
efficiency level it considered, DOE
determined the value of the first year’s
energy savings by calculating the
quantity of those savings in accordance
with DOE’s test procedure, and
multiplying that amount by the average
energy price forecast for the year in
which a new standard is expected to
take effect. Section V.B.1.c of this notice
and chapter 8 of the NOPR TSD present
the rebuttable presumption PBP results.
Earthjustice stated the DOE must
justify any refusal to adopt standard
levels at least as strong as those that
satisfy the rebuttable presumption
payback period. (Earthjustice, No. 47 at
p. 3) The LCC and PBP analyses
generate values that calculate the
payback period for consumers of
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Market
share (%)
5.7
100
potential energy conservation standards;
these include, but are not limited to, the
3-year payback period contemplated
under the rebuttable presumption test
discussed above. However, DOE
routinely conducts an 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) and 42 U.S.C.
6316(e)(1)). 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.
F. National Impact Analysis—National
Energy Savings and Net Present Value
Analysis
The national impact analysis assesses
the national energy savings and the net
present national impact analysis
assesses the national energy savings and
the net present value of total product
costs and savings expected to result
from standards at specific efficiency
levels. DOE used the NIA spreadsheet to
calculate energy savings and NPV, using
the annual energy consumption and
total installed cost data from the LCC
analysis. DOE forecasted the energy
savings, energy cost savings, product
costs, and NPV for each product class
from 2013 (or 2015) through 2043 (or
2045). The forecasts provided annual
and cumulative values for the above
output parameters. In addition, DOE
used its NIA spreadsheet to analyze
scenarios that used inputs from the
AEO2009 Low Economic Growth and
High Economic Growth cases. These
cases have higher and lower energy
price trends compared to the Reference
case, as well as higher and lower
housing starts, which result in higher
and lower appliance shipments to new
homes.
Earthjustice stated that DOE needs to
consider the impact of increased
employment and reduced emissions in
its national impact analysis.
(Earthjustice, No. 47 at p. 1) NRDC
stated that DOE failed to include the
benefits of avoided carbon emissions in
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Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
the NIA. (NRDC, No. 48 at p. 5) In
response, DOE accounts for the impacts
on employment in the employment
impact analysis (section IV.I), and it
quantifies avoided carbon emissions in
the environmental assessment (section
IV.K).The NIA primarily considers the
national energy savings and the NPV
from a national perspective of total
appliance consumer costs and savings
expected to result from standards, and
it also evaluates the benefits to the
economy of reduced energy prices due
to standards. Even though employment
and reduced emissions are separately
addressed outside the NIA, DOE
thoroughly considers these issues when
conducting its analyses in the context of
standard setting.
65909
Table IV.29 summarizes the approach
and data DOE used to derive the inputs
to the NES and NPV analyses for the
preliminary analysis and the changes to
the analyses for the proposed rule. A
discussion of these inputs and changes
follows. See chapter 10 of the NOPR
TSD for further details.
TABLE IV.29—APPROACH AND DATA USED FOR NATIONAL ENERGY SAVINGS AND CONSUMER NET PRESENT VALUE
ANALYSES
Inputs
Preliminary TSD
Shipments ................................................
Compliance Date of Standard .................
Annual shipments from shipments model .............
Water Heaters: 2015. DHE and Pool Heaters:
2013.
Efficiency market shares estimated for compliance year. SWEF * remains constant except for
gas and electric water heaters, for which
SWEF increases slightly over forecast period.
‘‘Roll-up’’ scenario used for determining SWEF in
2013 (or 2015) for each standards case.
SWEF remains constant except for gas and
electric water heaters, for which SWEF increases slightly over forecast period.
Annual weighted-average values as a function of
SWEF.
Water heaters: 10%. DHE: 15%. Pool Heaters:
10%.
Annual weighted-average values as a function of
SWEF.
Annual weighted-average values as a function of
the annual energy consumption per unit and
energy (and water) prices.
Annual values are a function of efficiency level ...
See IV.F.1.a through IV.F.1.d.
No change.
AEO2008 forecasts (to 2030) and extrapolation
to 2043 (and 2045).
Varies yearly and is generated by DOE/EIA’s
NEMS.
Three and seven percent real ...............................
Future expenses are discounted to 2007 .............
Updated using AEO2009 forecasts.
Base-Case Forecasted Efficiencies .........
Standards-Case Forecasted Efficiencies
Annual Energy Consumption per Unit .....
Rebound Effect ........................................
Total Installed Cost per Unit ....................
Energy Cost per Unit ...............................
Repair Cost and Maintenance Cost per
Unit.
Escalation of Energy Prices ....................
Energy Site-to-Source Conversion Factor
Discount Rate ..........................................
Present Year ............................................
Changes for the proposed rule
No change in approach; updated efficiency market shares estimated for compliance year.
No change in approach; updated efficiency market shares estimated for compliance year.
No change.
No change.
No change.
No change.
No change.
No change.
No change.
Future expenses are discounted to 2010, when
the final rule will be published.
* Shipments-Weighted Energy Factor.
1. Shipments
The shipments portion of the NIA
spreadsheet is a model that uses
historical data as a basis for projecting
future shipments of the appliance
products that are the subject of this
rulemaking. In projecting shipments for
water heaters and pool heaters, DOE
accounted for two market segments: (1)
New construction and (2) replacement
of failed equipment. Data were
unavailable to develop separate
forecasts of direct heating equipment
shipments for replacement and new
home installations, so the forecast was
based on the time series of historical
total shipments developed for each
product class.
Table IV.30 summarizes the approach
and data DOE used to derive the inputs
to the shipments analysis for the
preliminary analysis, and the changes
DOE made for today’s proposed rule. A
discussion of these inputs and changes
follows. For details on the shipments
analysis, see chapter 9 of the NOPR
TSD.
TABLE IV.30—APPROACH AND DATA USED FOR THE SHIPMENTS ANALYSIS
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Inputs
Preliminary analysis
Changes for the proposed rule
Historical Shipments ................................
Water Heaters: Data provided by AHRI ................
DHE: Data provided by AHRI and DOE estimates
New Construction Shipments ..................
Pool Heaters: Data from 1993 TSD and DOE estimates.
For water heaters and pool heaters, determined
by multiplying housing forecasts by forecasted
saturation of products in new housing.
Water Heaters: Used updated data from AHRI.
DHE: Used data from manufacturers and HPBA *
for hearth products.
Pool Heaters: Used inputs from manufacturers.
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No change in approach. New housing forecast
updated with AEO2009 projections.
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Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
TABLE IV.30—APPROACH AND DATA USED FOR THE SHIPMENTS ANALYSIS—Continued
Inputs
Preliminary analysis
Replacements ..........................................
First-Time Owners ...................................
Changes for the proposed rule
Housing forecasts based on AEO2008 projections.
New housing product saturations based on AHS
for water heaters, consultant data for pool
heaters.
For water heaters and pool heaters, determined No change for water heaters. For pool heaters,
by tracking total product stock by vintage and
included estimated non-replacement of some
establishing the failure of the stock using retirepool heaters.
ment functions from the LCC and PBP analysis.
Included for pool heaters ...................................... No change.
* Hearth, Patio & Barbecue Association.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
To determine new construction
shipments, DOE used forecasts of
housing starts coupled with estimates of
product market saturation in new
housing. For the preliminary analysis,
DOE used actual data for 2007 for new
housing completions and mobile home
placements and adopted the projections
from AEO2008 for 2008 to 2030. DOE
updated its new housing projections for
today’s proposed rule using AEO2009.
DOE estimated replacements using
historical shipments data and product
retirement functions that it developed
from product lifetimes.
AHRI stated that shipments for all of
the products dropped considerably in
2008, and this drop will change the
forecast since today’s new house
installation is tomorrow’s replacement
installation. (AHRI, No. 33 at p. 2) In
response, DOE’s NOPR analysis used
actual shipments data for 2008, so any
such changes are captured in DOE’s
analysis.
a. Water Heaters
For the preliminary analysis, DOE
used information on choice of water
heater products in recently-built
housing to estimate shipments to the
new construction market. DOE assumed
the market shares of water heaters using
a particular fuel follow the average
pattern in new homes for 2000 to 2006
throughout the forecast period. The
shipments model assumes that when a
unit using a particular fuel is retired, it
generally is replaced with a unit that
uses the same fuel. Section IV.F.1.d
discusses the potential effects of energy
conservation standards on choice of
water heater product in the new
construction and replacement markets.
For its shipments forecast for gas-fired
storage water heaters and electric
storage water heaters, DOE assumed that
the current market shares of smallvolume and large-volume products
would remain the same throughout the
forecast period.
Within the category of gas-fired water
heaters, DOE disaggregated the shares of
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gas storage water heaters and gas-fired
instantaneous water heaters based on
projections of total shipments of gasfired instantaneous water heaters.
Because there is much uncertainty about
the future growth of gas-fired
instantaneous water heaters, DOE
modeled three scenarios for their market
penetration. The scenarios are based on
experience with gas-fired instantaneous
water heaters in Australia, where the
proportion of instantaneous water
heaters in total gas-fired storage water
heater shipments has grown
considerably in the past decade. (See
Syneca Consulting, Cost-Benefit
Analysis: Proposal to Introduce a
Minimum Energy Performance Standard
for Gas Water Heaters, 2007, Australian
Greenhouse Office: Equipment Energy
Efficiency Gas Committee.) Residential
water heating services and technology
in Australia are roughly comparable to
those in the United States. Storage water
heaters have somewhat lower volume
capacities in Australia, but end-use hot
water demand also may be lower. Prices
of gas-fired instantaneous water heaters
in Australia are roughly comparable to
prices of gas-fired storage water heaters
(excluding installation costs). In the
United States, gas-fired instantaneous
water heaters currently cost about twice
as much as typical 40-gallon gas storage
water heaters. Although the price
differential in the United States likely
will decrease, the specifics of the United
States market probably will not
duplicate the market in Australia.
Nonetheless, DOE believes that the
market evolution in Australia provides
the most similar model for scenarios for
the United States.
AHRI stated that the Australian water
heater market has significant differences
from the U.S. market because in
Australia: (1) Gas water heaters are not
the prevalent residential option; (2)
many gas water heaters are installed
outside; and (3) prices of gas storage
water heaters and gas-fired
instantaneous water heaters are
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practically equal. (AHRI, No. 43 at p. 2)
Rheem stated that in Australia, most
water heaters are installed outdoors,
which makes a difference in terms of the
venting and total installation cost.
(Rheem, Public Meeting Transcript, No.
34.4 at p. 241) A.O. Smith commented
that the scenario for low market
penetration of gas-fired instantaneous
water heaters may be reasonable, but the
other two scenarios over-predict the
market penetration. (A.O. Smith, No. 37
at p. 7) Noritz stated that Australia is the
only market it has identified that could
provide any insight into the adoption of
gas-fired instantaneous water heaters in
the United States. (Noritz, No. 36 at
p. 3)
In response, DOE acknowledges the
uncertainty associated with basing
forecasted market penetration of gasfired instantaneous water heaters on the
Australian experience, but it agrees with
Noritz (the largest manufacturer of these
products) that there is no other market
that could provide a model for
forecasting U.S. market penetration. In
making use of the Australian
experience, DOE took into account some
of the differences between the two
markets that would tend to cause
shipments growth to be lower in the
U.S. For further details on the
shipments forecast for gas-fired
instantaneous water heaters, see chapter
9 of the NOPR TSD.
b. Direct Heating Equipment
To estimate historical shipments of
direct heating equipment for the
preliminary analysis, DOE used two sets
of data from AHRI and information from
the 1993 TSD. Data were unavailable to
develop separate forecasts of direct
heating equipment shipments for
replacement and new home
installations, so DOE based the forecast
on the time series of historical total
shipments developed for each product
class. To forecast shipments of gas room
DHE, shipments of room heaters were
held constant at the average level from
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2002 to 2005, and gas fireplace
shipments (referred to as hearth
products DHE in this NOPR) assigned to
gas room DHE were held constant at the
average from 2002 to 2004. Forecasted
floor furnaces shipments follow the
downward trend from 2000 to 2007.
Total combined shipments of gas wall
gravity and gas wall fan DHE were held
constant at the average volume from
2002 to 2006. The upward trend seen
from 2002 to 2006 was extrapolated into
the future for gas wall fan DHE. DOE
derived future shipments of gas wall
gravity DHE based on the combined
shipments of gas wall gravity and gas
wall fan DHE and the forecast
shipments for the latter. Shipments of
gas fireplaces assigned to gas wall fan
DHE were kept constant at the average
from 2002 to 2004.
Commenting on DOE’s forecast, HPBA
stated that gas fireplace shipments will
likely decrease as opposed to staying
level. (HPBA, Public Meeting
Transcript, No. 34.4 at p. 258) Apart
from a decrease due to the 2008–2009
economic recession, DOE is not aware of
reasons why gas fireplace (hearth
products) shipments would be expected
to decrease, given that the number of
U.S. households will continue to
increase. However, based on its review
of market information, DOE modified its
forecast of gas hearth products
shipments. The forecast used for the
NOPR accounts for the sharp decline in
shipments in 2007–2008, but assumes
that shipments in the future will
approximately follow the trend seen in
1998–2007.
In addition, DOE modified its forecast
of gas wall gravity and gas wall fan DHE
to better reflect current information.
Instead of having different trends for
each of these product classes, as in the
preliminary analysis, DOE assumed that
shipments of each class would stay
constant at the 2008 level during the
forecast period.
c. Pool Heaters
To forecast pool heater shipments for
new construction for the preliminary
analysis, DOE multiplied the annual
housing starts forecasted for singlefamily and multi-family housing by the
estimated saturation of gas-fired pool
heaters in recently built new housing.
For replacement pool heaters, DOE used
a survival function based on its
distribution of product lifetimes to
determine when a unit fails. DOE also
introduced a market segment
representing purchases by existing
households that had not owned a pool
heater. These first-time owners include
existing households that have a pool
and those that install one.
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In the preliminary analysis, DOE’s
projected that pool heater shipments
would grow significantly from 0.28
million in 2006 to over 0.7 million by
2040. Raypak stated that the slope of the
shipments forecast for pool heaters
should be consistent with the past 10
years of data, which show that the slope
is either constant or decreasing due to
economic reasons. It also stated that
pool heater new construction shipments
are declining because of lot size issues
and other restrictions. (Raypak, No. 34.4
at p. 247) EEI stated that projected pool
heater shipments are overstated and that
DOE should obtain more recent
numbers to develop more realistic
projections for shipments. (EEI, No. 40
at pp. 5–6) In response, DOE revised the
NOPR analysis to account for those
households that are not likely to replace
their pool heater when it fails due to
cost. As a result, the shipments
projection shows only modest growth
over the analysis period.
d. Impacts of Standards on Shipments
In some of its energy conservation
standard rulemakings, DOE has used
elasticities to estimate the response of
appliance demand (shipments) to
changes in the installed cost and
operating costs associated with moreefficient appliances. Typically, higher
installed costs of more-efficient
appliances are projected to cause some
consumers to forego purchase of a new
product.
In the case of water heaters, however,
DOE believes that this approach would
not be appropriate because the
consumer (or home builder) decision is
usually not whether to purchase the
product or not, but rather what type of
water heater to buy. A water heater is
generally not a discretionary purchase.
However, to the extent that energy
conservation standards result in an
increase in the price of a specific type
of water heater compared to a
competing product, some consumers (or
home builders in the case of shipments
for new construction) may purchase the
competing product. The consumer or
builder decision is not solely based on
economic factors, as the availability of
natural gas plays a key role. Evaluation
of this decision requires an assessment
of the specific factors that influence it
in the context of the two main markets
for water heaters, replacements and new
homes.
In the preliminary analysis, DOE
determined that the greatest potential
for product switching would exist in the
case of a standard that effectively
required an electric heat pump water
heater. This type of product often has a
substantially higher installed cost than
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a typical electric resistance storage
water heater and is relatively new to
consumers and builders. Because the
product choice decision partially
depends on the relative costs of
competing products, DOE considered
the following potential combinations of
electric and gas-fired storage water
heaters that could result from standards:
(1) Electric heat pump water heater and
a gas-fired storage water heater using
natural draft; (2) electric heat pump
water heater and a gas-fired storage
water heater using a power vent; and (3)
electric heat pump water heater and a
gas-fired storage water heater using
condensing technology. DOE used data
from the 2001 RECS to estimate the
percentage of households expected to
purchase an electric water heater in the
base case that could switch to a gas-fired
water heater because they had the
necessary infrastructure. To estimate
how many households that could switch
to gas-fired water heaters would do so,
DOE considered the difference in
installed cost between the gas-fired
storage water heater and an electric heat
pump water heater in each of the
combinations listed above.
DOE did not quantify the potential for
switching to gas water heating in the
case of a standard that requires 0.95 EF
for electric water heaters, as the
installed cost is only moderately higher
than the baseline electric water heater
(0.90 EF), and DOE judged that this
would not be sufficient to prompt
consumers to consider switching to gas
water heating.
ACEEE stated that because builders
make the choices that lock in
subsequent energy source decisions at
the time of construction, converting to
a different energy source for water
heating is too costly. However, it added
that a few consumers in existing houses
would choose gas conversion over
installing a heat pump water heater.
(ACEEE, No. 35 at pp. 6–7) NEEA and
NPCC commented that most water
heater replacements are on an
emergency basis and that there is no
convincing argument to include fuel
switching in the analysis. (NEEA and
NPCC, No. 42 at p. 9)
DOE agrees with the comment from
ACEEE but it also notes that not all
water heater replacements are on an
emergency basis. DOE believes that the
cost differential estimated in its analysis
suggests that a small fraction of
consumers would be likely to switch.
For the NOPR, DOE used a similar
approach as for the preliminary analysis
using data from the 2005 RECS.
Southern stated that many consumers
would switch to a gas-fired storage
water heater instead of installing a heat
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pump water heater even if the installed
cost is more, especially if the heat pump
water heater would need to be installed
in an enclosed interior location.
(Southern, No. 50 at p. 4) DOE’s
approach took detailed account of those
situations in which consumers with a
failed electric storage water heater
would find it less expensive to switch
to a gas-fired storage water heater
instead of installing a heat pump water
heater. In determining which
households would switch to a gas-fired
storage water heater, the analysis
considered the installed costs that
consumers might incur if they replaced
an electric storage water heater located
indoors with a heat pump water heater.
(Refer to the discussion of installation
costs for heat pump water heaters in
section IV.E.2.a.) Given that an interior
location may not easily allow the
venting required with installing a gasfired storage water heater, DOE does not
believe consumers would switch to a
gas-fired storage water heater instead of
installing a heat pump water heater if
the installed cost of the gas-fired
product is higher.
In the NOPR analysis, the fraction of
households using an electric storage
water heater estimated to switch to a
gas-fired storage water heater instead of
installing a heat pump water heater
ranges from zero with a standard level
for gas-fired storage water heaters that
requires condensing technology, to 9
percent with a standard level for gasfired storage water heaters that requires
power vent technology.
In the preliminary analysis, DOE
concluded that builders who planned to
install an electric storage water heater
would not switch to gas-fired storage
water heaters in the event of a standard
that effectively requires heat pump
technology. A.O. Smith stated that
builders would be unlikely to switch
from a heat pump water heater to a gasfired storage water heater due to the cost
of adding gas to the house, and if gas
were already supplied to the house, a
heat pump water heater would not have
been installed. (A.O. Smith, No. 37 at p.
8) DOE agrees that availability of natural
gas is the key determining factor for
builders. Accordingly, DOE’s analysis
for the NOPR shows negligible
switching in new homes.
EEI stated that there may be a switch
from electric storage to electric
instantaneous water heaters if DOE
adopts a standard level that would
require use of heat pump technology for
electric storage water heaters. (EEI, No.
40 at p. 5) DOE acknowledges that some
households facing extreme structural
modifications to accommodate a heat
pump water heater may purchase an
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electric instantaneous water heater
instead. However, because such
switching requires expensive electrical
modification to the home’s electrical
circuits to accommodate the higher
electrical demand of instantaneous
water heaters, DOE believes it is an
unlikely choice for most households
with electric water heating.
With respect to the new construction
market, in the preliminary analysis,
DOE concluded that builders who
planned to install an electric storage
water heater would not switch to gasfired storage water heaters in the event
of a standard that effectively requires
heat pump technology. A.O. Smith
commented that builders would be
unlikely to switch from a heat pump
water heater to a gas-fired storage water
heater due to the cost of adding gas to
the house, and if gas had been already
supplied to the house, a heat pump
water heater would not have been
installed. (A.O. Smith, No. 37 at p. 8)
DOE agrees that availability of natural
gas is the key factor determining water
heater choice for home builders.
Accordingly, DOE’s analysis for the
NOPR shows negligible switching in
new homes.
Regarding potential switching from
gas-fired water heaters to electric water
heaters, DOE determined that the cost of
replacing an existing gas-fired storage
water heater with an electric one is
substantial due to the complexity of the
installation. Because it takes longer for
an electric storage water heater to
recover heated capacity, a larger electric
tank may be necessary to replace a gas
unit. In new construction, if natural gas
is available, builders generally will
install a gas-fired water heater. Given
the above considerations, in both new
construction and the replacement
market, a large increase in the price of
a gas storage water heater compared to
an electric storage water heater likely
would be necessary to motivate
consumers to replace a gas water heater
with an electric unit, or to motivate
builders to install an electric water
heater instead of a gas unit. Because
DOE does not envision such a price
differential resulting from this
rulemaking, it concluded that amended
standards would not induce switching
from a gas storage water heater to an
electric storage water heater.
In its preliminary analysis, DOE did
not quantify the potential for switching
away from oil-fired water heaters. Bock
and EEI stated that DOE should consider
fuel and equipment switching impacts
of standards on oil-fired equipment.
(Bock, No. 53 at p. 1; EEI, No. 40 at pp.
4–5) In response, DOE believes that the
price of the oil-fired storage water heater
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is a minor factor in the fuel choice
decision for households with such a
water heater. In most cases, a household
with an oil-fired storage water heater
needing replacement would switch to a
gas-fired water heater if gas is available
because of the greater convenience and
lower cost of gas water heating.
Therefore, DOE believes that the
moderately higher equipment price that
might result from the proposed standard
level (5 percent) would have a negligible
impact on fuel switching for oil-fired
storage water heaters, and DOE did not
include such switching in its NOPR
analysis.
In its preliminary analysis, DOE did
not quantify the potential for switching
away from gas-fired instantaneous water
heaters due to lack of quantitative
information about the factors that shape
the purchase decision for this product.
However, given that the vast majority of
the market (85 percent) is already at the
proposed standard level (0.82 EF), there
is little reason to expect any switching
to storage water heaters as a result of the
proposed standard.
For DHE and pool heaters, DOE did
not find any data it could use to
estimate the extent of switching away
from the gas-fired products subject to
this rulemaking if energy conservation
standards were to result in a significant
increase in installed costs. DOE did not
receive any comments on its approach
for these products, and it maintained
the same approach for the NOPR
analysis.
In summary, DOE projects that no fuel
switching would occur for gas-fired
storage, oil-fired storage, and gas-fired
instantaneous water heaters. For electric
storage water heaters, DOE estimated
that a standard that effectively requires
heat pump water heaters would result in
a decline in shipments ranging from
zero to 9 percent, depending on the
standard level for gas-fired storage water
heaters.
DOE requests comments on its
analysis of fuel switching that may
result from the proposed standards on
water heaters and the other heating
products. In particular, DOE requests
comments on (1) its general approach,
which does not involve price
elasticities; (2) its analysis of switching
to gas-fired storage water heaters in the
case of a standard that effectively
requires an electric heat pump water
heater; (3) its conclusion that the
proposed standards would not induce
switching from a gas storage water
heater to an electric storage water
heater; and (4) its conclusion that the
proposed standards would not induce
switching for gas-fired instantaneous
water heaters, DHE, and pool heaters.
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This is identified as issue 15 under
‘‘Issues on Which DOE Seeks Comment’’
in section VII.E of this NOPR.
2. Other Inputs
The following is a discussion of the
other inputs to the NIA and any
revisions DOE made to those inputs for
today’s proposed rule.
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a. Base-Case Forecasted Efficiencies
A key input to DOE’s estimates of
NES and NPV is the energy efficiencies
that DOE forecasts over time for the base
case (without new standards) and each
of the standards cases. The forecasted
efficiencies represent the annual
shipment-weighted energy efficiency of
the products under consideration over
the forecast period.
For the preliminary analysis, DOE
used the SWEFs for 2013 or 2015 as a
starting point to forecast the base-case
energy efficiency distribution for each
product class. To represent the
distribution of product energy
efficiencies in those years, DOE used the
same market shares as in the base case
for the LCC analysis. For gas storage
water heaters and electric storage water
heaters, DOE estimated the distribution
of product energy efficiencies in 2015
by accounting for the estimated market
impact of the newly established
ENERGY STAR efficiency levels for
water heaters (see section IV.9.a). The
projected trend to 2015 represents an
average annual increase in energy
efficiency of 0.27 percent for gas-fired
storage water heaters and 0.55 percent
for electric storage water heaters. DOE
applied the above values to estimate the
increase in average energy efficiency
until the end of the forecast period.
DOE found no quantifiable
indications of change in energy
efficiencies over time for oil-fired and
gas-fired instantaneous water heaters,
direct heating equipment, or pool
heaters, and it did not receive any
comments on this topic. Therefore, for
these products, DOE estimated that
energy efficiencies remain constant at
the 2015 or 2013 level until the end of
the forecast period.
For today’s proposed rule, DOE
maintained the approach described
above.
b. Standards-Case Forecasted
Efficiencies
For its determination of standardscase forecasted efficiencies, DOE used a
‘‘roll-up’’ scenario in the preliminary
analysis and the NOPR to establish the
SWEF for the year that standards would
become effective and subsequent years.
In this approach, product energy
efficiencies in the base case that do not
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meet the standards level under
consideration would roll up to meet the
new standard level. The market share of
energy efficiencies that exceed the
standard level under consideration
would be the same in the standards case
as in the base case. Changes over the
forecast period match those in the base
case. For today’s proposed rule, DOE
maintained this approach.
c. Annual Energy Consumption
The inputs for determining NES are
annual energy consumption per unit,
shipments, equipment stock, national
annual energy consumption, and site-tosource conversion factors. Because the
annual energy consumption per unit
depends directly on efficiency, DOE
used the SWEFs associated with the
base case and each standards case, in
combination with the annual energy use
data, to estimate the shipment-weighted
average annual per-unit energy
consumption under the base case and
standards cases. The national energy
consumption is the product of the
annual energy consumption per unit
and the number of units of each vintage.
This calculation accounts for differences
in unit energy consumption from year to
year. For today’s proposed rule, DOE
maintained this approach.
d. Site-to-Source Energy Conversion
To estimate the national energy
savings expected from appliance
standards, DOE uses a multiplicative
factor to convert site energy
consumption (at the home or
commercial building) into primary or
source energy consumption (the energy
required to deliver the site energy).
These conversion factors account for the
energy used at power plants to generate
electricity and losses in transmission
and distribution, as well as for natural
gas losses from pipeline leakage and
energy used for pumping. For
electricity, the conversion factors vary
over time due to projected changes in
generation sources (i.e., the power plant
types projected to provide electricity to
the country). The factors that DOE
developed are marginal values, which
represent the response of the system to
an incremental decrease in consumption
associated with appliance standards.
In the preliminary analysis, DOE used
annual site-to-source conversion factors
based on the version of NEMS that
corresponds to AEO2008. For today’s
NOPR, DOE updated its conversion
factors based on AEO2009. The AEO
does not provide energy forecasts
beyond 2030; DOE used conversion
factors that remain constant at the 2030
values throughout the remainder of the
forecast period.
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In response to a request from the
DOE’s Office of Energy Efficiency and
Renewable Energy (EERE), the National
Research Council (NRC) appointed a
committee on ‘‘Point-of-Use and FullFuel-Cycle Measurement Approaches to
Energy Efficiency Standards’’ to conduct
a study called for in section 1802 of
EPACT 2005. The fundamental task
before the committee was to evaluate
the methodology used for setting energy
efficiency standards and to comment on
whether site (point-of-use) or source
(full-fuel-cycle) measures of energy
efficiency better support rulemaking to
achieve energy conservation goals. The
NRC committee defined site (point-ofuse) energy consumption as reflecting
the use of electricity, natural gas,
propane, and/or fuel oil by an appliance
at the site where the appliance is
operated. Full-fuel-cycle energy
consumption was defined as including,
in addition to site energy use, the
following: Energy consumed in the
extraction, processing, and transport of
primary fuels such as coal, oil, and
natural gas; energy losses in thermal
combustion in power generation plants;
and energy losses in transmission and
distribution to homes and commercial
buildings. (See The National
Academies, Board on Energy and
Environmental Systems, Letter to Dr.
John Mizroch, Acting Assistant
Secretary, U.S. DOE, Office of EERE
from James W. Dally, Chair, Committee
on Point-of-Use and Full-Fuel-Cycle
Measurement Approaches to Energy
Efficiency Standards, May 15, 2009.)
In evaluating the merits of using
point-of-use and full-fuel-cycle
measures, the NRC committee noted
that DOE uses what the committee
referred to as ‘‘extended site’’ energy
consumption to assess the impact of
energy use on the economy, energy
security, and environmental quality.
The extended site measure of energy
consumption includes the generation,
transmission, and distribution but,
unlike the full-fuel-cycle measure, does
not include the energy consumed in
extracting, processing, and transporting
primary fuels. A majority of members on
the NRC committee concluded that
extended site energy consumption
understates the total energy consumed
to make an appliance operational at the
site. As a result, the NRC committee’s
primary general recommendation is for
DOE to consider moving over time to
use of a full-fuel-cycle measure of
energy consumption for assessment of
national and environmental impacts,
especially levels of greenhouse gas
emissions, and to providing more
comprehensive information to the
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public through labels and other means,
such as an enhanced Web site. For those
appliances that use multiple fuels (e.g.,
water heaters), the NRC committee
believes that measuring full-fuel-cycle
energy consumption would provide a
more complete picture of energy used,
thereby allowing comparison across
many different appliances as well as an
improved assessment of impacts. The
NRC committee also acknowledged the
complexities inherent in developing a
full-fuel-cycle measure of energy use
and stated that a majority of the
committee recommended a gradual
transition to that expanded measure and
eventual replacement of the currently
used extended site measure.
DOE acknowledges that its site-tosource conversion factors do not capture
all of the energy consumed in
extracting, processing, and transporting
primary fuels. DOE also agrees with the
NRC committee’s conclusion that
developing site-to-source conversion
factors that capture the energy
associated with the extraction,
processing, and transportation of
primary fuels is inherently complex and
difficult. However, DOE has performed
some preliminary evaluation of a fullfuel-cycle measure of energy use.
Based on two studies completed by
the National Renewable Energy
Laboratory (NREL) in 1999 and 2000,
DOE estimated the ratio of the energy
used upstream to the energy content of
the coal or natural gas delivered to
power plants. For coal, the NREL
analysis considered typical mining
practices and mine-to-plant
transportation distances, and used data
for the State of Illinois. Based on data
in this report, the estimated
multiplicative factor for coal is 1.08 (i.e.,
it takes approximately 1.08 units of coal
energy equivalent to provide 1 unit of
coal to a power plant). A similar
analysis of the energy consumed in
upstream processes needed to produce
and deliver natural gas to a power plant
yielded a multiplicative factor of 1.19.
(For further information on the NREL
studies, please see: Spath, Pamela L.,
Margaret K. Mann, and Dawn Kerr, Life
Cycle Assessment of Coal-fired Power
Production, NREL/TP–570–25119, June
1999; and Spath, Pamela L. and
Margaret K. Mann, Life Cycle
Assessment of a Natural Gas CombinedCycle Power Generation System, NREL/
TP–570–27715, September 2000.)
While the above factors are indicative
of the magnitude of the impacts of using
full-fuel-cycle measures of energy use,
there are two aspects of the problem that
warrant further study. The first is the
refinement of the estimates of the
multiplicative factors, particularly to
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incorporate regional variation. The
second is development of forecasts of
the multiplicative factors over the time
frames used in the rulemaking analyses,
typically ten to fifty years. The second
issue, of forecasting how the efficiency
factors for various fuels may change
over time, has the potential to be quite
significant. The existing NEMS forecast
of power plant electricity generation by
fuel type can be used to estimate the
impact of a changing mix of fuels.
However, currently NEMS provides no
information on potential changes to the
relative ease with which the different
fuels can be extracted and processed.
DOE intends to further evaluate the
viability of using full-fuel-cycle
measures of energy consumption for
assessment of national and
environmental impacts of appliance
standards.
e. Total Installed Costs and Operating
Costs
The total annual installed cost
increase is equal to the annual
difference in the per-unit total installed
cost between the base case and
standards cases multiplied by the
shipments forecasted in the standards
case.
The annual operating cost savings per
unit reflect differences in energy, repair,
and maintenance costs between the base
case and the various standard levels
DOE considered. DOE forecasted energy
prices for the preliminary analysis are
based on AEO2008. DOE updated the
energy prices for today’s proposed rule
using forecasts from AEO2009.
f. Discount Rates
DOE multiplies monetary values in
future years by the discount factor to
determine the present value. For the
preliminary analysis and today’s NOPR,
DOE estimated the NPV of appliance
consumer benefits using both a 3percent 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
(OMB Circular A–4 (Sept. 17, 2003),
section E, ‘‘Identifying and Measuring
Benefits and Costs’’). NRDC stated that
a discount rate below 3 percent is
warranted for societal benefits. (NRDC,
No. 48 at p. 5) OMB Circular A–4 states
that when regulation primarily and
directly affects private consumption, a
lower discount rate is appropriate. ‘‘The
alternative most often used is sometimes
called the social rate of time preference
* * * the rate at which ‘society’
discounts future consumption flows to
their present value.’’ (p. 33) It suggests
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that the real rate of return on long-term
government debt may provide a fair
approximation of the social rate of time
preference, and states that over the last
30 years, this rate has averaged around
3 percent in real terms on a pre-tax
basis. It concludes that ‘‘for regulatory
analysis, [agencies] should provide
estimates of net benefits using both 3
percent and 7 percent.’’ (p. 34) DOE
finds that the guidance from OMB is
reasonable, so it is continuing to use a
3-percent and a 7-percent discount rate
for estimating net benefits.
3. Other Inputs
a. Effects of Standards on Energy Prices
In the preliminary analysis, DOE
analyzed the potential impact on natural
gas prices resulting from amended
standards on water heaters and the
associated benefits for all natural gas
consumers in all sectors of the economy.
(DOE did not include natural gas
savings from amended standards on
DHE and pool heaters in this analysis
because they are not large enough to
have a noticeable impact.) DOE used
NEMS–BT to account for the natural gas
savings associated with two scenarios of
possible standards, including max-tech
efficiency levels. Like other widely used
energy-economic models, NEMS
incorporates parameters to estimate the
changes in energy prices that would
result from an increase or decrease in
energy demand. The response of price to
a decrease in demand is termed the
‘‘inverse price elasticity.’’ The overall
inverse price elasticity observed in
NEMS changes over the forecast period
based on the model’s dynamics of
natural gas supply and demand. DOE
calculated the nominal savings in total
natural gas expenditures in each year by
multiplying the estimated annual
change in the average end-user natural
gas price by the annual total U.S.
natural gas consumption associated
with each scenario. DOE then calculated
the NPV of the savings in natural gas
expenditures for 2015 to 2045 using 3and 7-percent discount rates for each
scenario.
For the NOPR, DOE used the same
approach to estimate the benefits of
reduced natural gas prices as in the
preliminary TSD. However, it analyzed
the potential impact on natural gas
prices, and the associated benefits for
natural gas consumers, resulting from
the proposed water heater standards
(TSL 4), as well as the other TSLs
considered.
NRDC stated that DOE must consider
the benefit of reduced natural gas and
electricity prices and include it in the
NIA. (NRDC, No. 48 at p. 5) ACEEE
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stated that DOE must incorporate the
impacts of gas and electricity
consumption reductions resulting from
the standards on energy prices in the
primary economic analysis, rather than
simply note side studies that DOE did
not incorporate into the decisionmaking process. (ACEEE, No. 35 at p. 8)
DOE reports the results of its analysis
of the benefits of reduced natural gas
prices associated with standards in
chapter 10 of the NOPR TSD, National
Impacts Analysis. As discussed therein,
when gas prices drop in response to a
lower output of existing natural gas
production capacity, consumers benefit
but producers suffer. In economic terms,
the situation represents a benefits
transfer to consumers (whose
expenditures fall) from producers
(whose revenue falls equally). When
prices decrease because extraction costs
decline, however, consumers and
producers both benefit, and the change
in natural gas prices represents a net
gain to society. Consumers benefit from
the lower prices, and producers, whose
revenues and costs both fall, are no
worse off. Because there is uncertainty
about the extent to which the calculated
impacts from reduced natural gas prices
are a benefits transfer, DOE tentatively
concluded that it should not give a
heavy weight to this factor in its
consideration of the economic
justification of standards on heating
products.
DOE investigated the possibility of
estimating the impact of specific
standard levels on electricity prices in
its rulemaking for general service
fluorescent lamps and incandescent
reflector lamps. (See U.S. Department of
Energy—Office of Energy Efficiency and
Renewable Energy: Energy Conservation
Standards for General Service
Fluorescent Lamps and Incandescent
Reflector Lamps; Proposed Rule, 74 FR
16920, 16978–979 (April 13, 2009).) It
found that whereas natural gas markets
exhibit a fairly simple chain of agents
from producers to consumers, the
electric power industry is a complex
mix of fuel suppliers, producers, and
distributors. While the distribution of
electricity is regulated everywhere, its
institutional structure varies, and
upstream components are more
complicated, because the cost of
generation differs across the country.
For these and other reasons, accurate
modeling of the response of electricity
prices to a decrease in residential-sector
demand due to standards is
problematic. Thus, DOE does not plan
to estimate the value of potentially
reduced electricity costs for all
consumers associated with revised
standards for heating products.
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G. Consumer Subgroup Analysis
In analyzing the potential impact of
new or amended standards on
individual and commercial consumers,
DOE evaluates the impact on
identifiable subgroups of consumers
that may be disproportionately affected
by a national standard level. DOE used
RECS data to analyze the potential effect
of energy conservation standards on the
considered consumer subgroups for
selected heating products, as explained
below. For gas-fired and electric storage
water heaters, and gas wall fan and gas
wall gravity DHE, DOE estimated
consumer subgroup impacts for lowincome households and senior-only
households. In addition, for gas-fired
and electric storage water heaters, DOE
estimated consumer subgroup impacts
for households in multi-family housing
and households in manufactured homes
as well.
DOE did not evaluate consumer
subgroup impacts for gas-fired
instantaneous water heaters and oilfired storage water heaters. Gas-fired
instantaneous water heaters were
excluded from the consumer subgroup
analysis due to insufficient data, and
oil-fired storage water heaters were
excluded due to low product shipments.
For direct heating equipment, gas floor
DHE and gas room DHE were excluded
due to the low and decreasing levels of
product shipments. For gas hearth DHE,
DOE examined the senior-only
subgroup, but did not evaluate the lowincome subgroup because the saturation
of this product is very small among lowincome households due to the high
product cost. DOE did not evaluate
consumer subgroup impacts for pool
heaters because the sample size of the
subgroups is too small for meaningful
analysis. More details on the consumer
subgroup analysis and results can be
found in chapter 11 of the NOPR TSD.
H. Manufacturer Impact Analysis
1. Overview
In determining whether an amended
energy conservation standard for the
three types of heating products subject
to this rulemaking is economically
justified, the Secretary is required to
consider ‘‘the economic impact of the
standard on the manufacturers and on
the consumers of the products subject to
such standard.’’ (42 U.S.C.
6295(o)(2)(B)(i)(I)) The statute also calls
for an assessment of the impact of any
lessening of competition as determined
by the Attorney General that is likely to
result from the adoption of a standard.
(42 U.S.C. 6295(o)(2)(B)(i)(V)) DOE
conducted the MIA to estimate the
financial impact of amended energy
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conservation standards on
manufacturers of residential water
heaters, DHE, and pool heaters, and to
assess the impacts of such standards on
employment and manufacturing
capacity.
The MIA has both quantitative and
qualitative aspects. The quantitative
part of the MIA relies on the
Government Regulatory Impact Model
(GRIM), an industry cash-flow model
customized for the three heating
products covered in this rulemaking.
The GRIM inputs characterize each
industry’s cost structure, shipments,
and revenues. This includes information
from many of the analyses described
above, such as MPCs and MSPs from the
engineering analysis and shipment
forecasts from the NIA. The key GRIM
output is the Industry Net Present Value
(INPV), which estimates the value of
each industry on the basis of cash flows,
expenditures, and investment
requirements as a function of TSLs.
Different sets of assumptions (scenarios)
will produce different results. The
qualitative part of the MIA addresses
factors such as product characteristics,
characteristics of particular firms, and
market trends. The qualitative
discussion also includes an assessment
of the impacts of standards on
manufacturer subgroups. The complete
MIA is discussed in chapter 12 of the
NOPR TSD.
DOE conducted the MIA for the three
types of heating products in three
phases. Phase 1 (Industry Profile)
characterized each industry using data
on market shares, sales volumes and
trends, pricing, employment, and
financial structure. Phase 2 (Industry
Cash Flow) focused on each industry as
a whole. In this phase, DOE used each
GRIM to prepare an industry cash-flow
analysis. Using publicly-available
information developed in Phase 1, DOE
adapted each GRIM’s generic structure
to perform an analysis of the impacts on
residential water heater, directing
heating equipment, and pool heater
manufacturers due to amended energy
conservation standards. In Phase 3
(Subgroup Impact Analysis), DOE
conducted interviews with a
representative cross-section of
manufacturers that produce the majority
of residential water heater, DHE, and
pool heater sales. During these
interviews, DOE discussed engineering,
manufacturing, procurement, and
financial topics specific to each
company, and obtained each
manufacturer’s view of the industry as
a whole. The interviews also provided
valuable information that DOE used to
evaluate the impacts of amended energy
conservation standard on manufacturer
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cash flows, manufacturing capacity, and
employment levels. Each of these
phases is discussed in further detail
below.
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a. Phase 1: Industry Profile
In Phase 1 of the MIA, DOE prepared
a profile of each of the three heating
product industries based on the market
and technology assessment prepared for
this rulemaking. Before initiating the
detailed impact studies, DOE collected
information on the present and past
structure and market characteristics of
each industry. This information
included market share data, product
shipments, manufacturer markups, and
the cost structure for various
manufacturers. The industry profile
includes: (1) Further detail on the
overall market and product
characteristics; (2) estimated
manufacturer market shares; (3)
financial parameters such as net plant,
property, and equipment, SG&A
expenses, cost of goods sold, etc.; and
(4) trends in the number of firms,
market, and product characteristics for
the three heating product industries.
The industry profile included a topdown cost analysis of residential water
heater, DHE, and pool heater
manufacturers that DOE used to derive
preliminary financial inputs for the
GRIMs (e.g., revenues, depreciation,
SG&A, and research and development
(R&D) expenses). DOE also used public
sources of information to further
calibrate its initial characterization of
each industry, including Security and
Exchange Commission 10–K filings
(available at https://www.sec.gov),
Standard & Poor’s stock reports
(available at https://
www2.standardandpoors.com), and
corporate annual reports. DOE
supplemented this public information
with data released by privately held
companies.
b. Phase 2: Industry Cash-Flow Analysis
Phase 2 focused on the financial
impacts of potential amended energy
conservation standards on industries as
a whole. More-stringent 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. To quantify
these impacts in Phase 2 of the MIA,
DOE used the GRIMs to perform three
cash-flow analyses: one for the
residential water heater industry
(separated into the impacts on gas-fired
and electric storage, oil-fired storage,
and gas-fired instantaneous water
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heaters), one for DHE (separated into the
impacts on traditional DHE and gas
hearth DHE), and one for gas-fired pool
heaters. In performing these analyses,
DOE used the financial values derived
during Phase 1 and the shipment
scenarios used in the NIA.
c. Phase 3: Subgroup Impact Analysis
Using average cost assumptions to
develop an industry-cash-flow estimate
does not adequately assess differential
impacts of amended energy
conservation standards among
manufacturer subgroups. 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 used the
results of the industry characterization
analysis in Phase 1 to group
manufacturers that exhibit similar
characteristics. The interviews provided
valuable information on manufacturer
subgroups. During the manufacturer
interviews, DOE discussed financial
topics specific to each manufacturer and
obtained each manufacturer’s view of
the industry as a whole.
As stated above, DOE reports the MIA
impacts by grouping the impacts of
certain product classes together. DOE
presents the industry impacts by the
major product types (gas-fired and
electric storage water heaters, oil-fired
storage water heaters, gas-fired
instantaneous water heaters, traditional
DHE, gas hearth DHE, and gas-fired pool
heaters). These product groupings
represent separate markets that are
served by the same manufacturers and
are typically produced in the same
factories. Once segmented into major
product types by industry, DOE was
only able to identify one subgroup—
small manufacturers.
For its small business manufacturer
subgroup analysis, DOE uses the small
business size standards published by
the Small Business Administration
(SBA) to determine whether a company
is 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,’’ a
residential water heater, DHE, or pool
heater manufacturer and its affiliates
may employ a maximum of 500
employees. The 500-employee threshold
includes all employees in a business’s
parent company and any other
subsidiaries. Based upon this
classification, DOE identified five
residential water heater manufacturers,
12 DHE manufacturers, and one small
gas-fired pool heater manufacturer that
qualify as small businesses per the
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applicable SBA definition. The small
business subgroup is discussed in
chapter 12 of the TSD and in section
VI.B of today’s notice.
2. GRIM Analysis
DOE uses the GRIM to quantify the
changes in cash flow that result in a
higher or lower industry value. The
GRIM analysis uses a standard, annualcash-flow analysis that incorporates
MPCs, MSPs, shipments, and industry
financial information as inputs, and
models changes in costs, distribution of
shipments, product and capital
conversion costs, and manufacturer
markups that would result from
amended energy conservation
standards. The GRIM spreadsheet uses
the inputs to arrive at a series of annual
cash flows, beginning with the base year
of the analysis, 2010, and continuing
over the analysis period. DOE used the
same base year (2010) as the NIA, which
is the same year as the announcement
of the final rule. DOE used the same
analysis period in the MIA as in the
NIA. For all rulemakings, DOE
considers a 30-year analysis period after
the anticipated compliance date of the
final rule, which under EPCA means the
date after which regulated parties must
comply with the requirements of the
amended standard. The compliance date
of the rulemaking is estimated to be
March of 2013 for DHE and pool heaters
and March of 2015 for residential water
heaters. The analysis period runs from
the beginning of 2013 to 2043 for DHE
and pool heaters and from the beginning
of 2015 to 2045 for residential water
heaters.
DOE uses the GRIM to calculate cash
flows using standard accounting
principles and to compare changes in
INPV between the base case and various
TSLs (the standards cases). The
difference in INPV between the base
case and the standards case represents
the financial impact of the potential
amended energy conservation standard
on manufacturers. DOE collected this
information from a number of sources,
including publicly-available data and
manufacturer interviews.
DOE created a separate GRIM for each
of the three types of heating products.
For today’s notice, DOE is structuring
separate TSLs for the three heating
products. DOE also treats certain
product classes within the three heating
products separately. For example, DOE
created specialized interview guides for
different groups of product classes.
These interview guides included one for
storage water heaters (gas-fired storage,
electric storage, and oil-fired storage
water heaters), one for gas-fired
instantaneous water heaters, one for
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traditional DHE (gas wall fan, gas wall
gravity, gas floor, and gas room DHE),
one for gas hearth DHE, and one for gasfired pool heaters. DOE grouped product
classes made by the same manufacturers
and in the same production facilities
together. This allowed DOE to better
understand the impacts on
manufacturers of these product classes.
For example, the TSLs DOE
considered for residential water heater
packages selected efficiency levels of
gas-fired storage, electric storage, oilfired storage, and gas-fired
instantaneous water heaters. The TSLs
DOE considered for DHE packages
selected efficiency levels for gas wall
fan, gas wall gravity, gas floor, gas room,
and gas hearth units. Each of the TSLs
DOE considered for pool heaters consist
of a single efficiency level for gas-fired
pool heaters. DOE describes the TSLs in
section V.A of today’s notice. Because
the combinations of TSLs can make it
more difficult to discuss the required
efficiencies for each product class, DOE
presents the MIA results in section
V.B.2 of today’s notice and chapter 12
of the NOPR TSD by groups of
manufacturers that make the covered
products. DOE presents the MIA results
for gas-fired storage and electric storage
water heaters together because
manufacturers typically produce both
types of water heaters in the same
facilities. The MIA results for oil-fired
storage and gas-fired instantaneous
water heaters are presented separately.
The MIA results for DHE are separated
into traditional DHE (gas wall fan, gas
wall gravity, gas floor, and gas room
DHE) and gas hearth DHE. The MIA
results for gas-fired pool heaters are also
presented separately.
a. GRIM Key Inputs
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i. Manufacturer Product Costs
In the MIA, DOE used the MPCs for
the three types of heating products at
each efficiency level calculated in the
engineering analysis, as described in
section IV.C and further detailed in
chapter 5 of the NOPR TSD. Changes in
MPCs can affect revenues and gross
margins. For instance, manufacturing a
higher-efficiency product is typically
more expensive due to the use of more
complex components and higher-cost
raw materials. For gas-fired storage
water heaters, DOE used a weighted
average MPC using both standard burner
and ultra-low-NOX burner costefficiency curves from the engineering
analysis to account for shipments of
ultra-low-NOX water heaters.
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ii. Base-Case Shipments Forecast
The GRIM estimates manufacturer
revenues based on total unit shipment
forecasts and the distribution of these
values by efficiency level. Changes in
the efficiency mix at each standard level
affect manufacturer finances. For this
analysis, the GRIM uses the NIA
shipments forecasts from 2008 and
continuing until the end of the analysis
period for each heating product (2045
for residential water heaters and 2043
for DHE and pool heaters). In the
shipments analysis, DOE also estimated
the distribution of efficiencies in the
base case for all product classes. See
section IV.F.1 for additional details.
iii. Product and Capital Conversion
Costs
Amended energy conservation
standards will cause manufacturers to
incur one-time conversion costs to bring
their production facilities and product
designs into compliance. For the MIA,
DOE classified these one-time
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 costs
focused on making product designs
comply with the amended energy
conservation standard. Capital
conversion costs are one-time
investments in property, plant, and
equipment to adapt or change existing
production facilities so that new
product designs can be fabricated and
assembled.
DOE assessed the product conversion
costs manufacturers would be required
to make at each TSL. For residential gasfired storage water heaters, electric
storage water heaters, and gas-fired pool
heaters, DOE based most of its estimates
of the product conversion costs on
information obtained from manufacturer
interviews. DOE estimated average
industry product conversion costs by
weighting the estimates from
manufacturers by market share, then
extrapolating the interviewed
manufacturers’ product conversion costs
for each product class to account for the
market share of companies that were not
interviewed. DOE verified the accuracy
of these product conversion costs by
comparing them to its own estimate of
the product development, testing,
certification, and retraining effort
required by each manufacturer at each
TSL. DOE also compared the product
conversion costs to the total cost of
other recent product development
efforts manufacturers have incurred
(such as the cost to redesign burners to
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comply with ultra-low-NOX
requirements). For gas-fired and electric
storage water heaters at TSL 5, DOE
used the industry-wide product
conversion costs for the standard-size
volumes at TSL 4. DOE assumed the
additional product conversion costs for
the large gallon sizes at TSL 5 scaled
with the total industry-wide product
conversion costs. At TSL 5 for gas-fired
and electric storage water heaters, DOE
multiplied its estimate for the entire
industry to exclusively offer heat pump
products at TSL 6 and condensing
products at TSL 7 by the percentage of
total electric storage and gas-fired
storage water heater models that exceed
a 55 gallon rated volume (27 percent
and 11 percent, respectively).
For oil-fired storage water heaters,
gas-fired instantaneous water heaters,
and all DHE product classes, DOE did
not receive sufficient manufacturer data
to serve as the basis for its industrywide product conversion estimates. For
these products, DOE calculated its
estimates by reviewing product
literature and publically-available
information about the efficiency of the
existing product lines. DOE used this
information to estimate the number of
product lines that manufacturers would
need to modify or develop at each TSL.
DOE also estimated a per-product-line
development cost at each efficiency
level and assumed these costs
represented the product conversion
costs for a manufacturer that has to
upgrade product lines to meet that TSL.
DOE also assumed that that the product
development costs increase as the
design changes become more complex
and if manufacturers do not currently
offer products that meet or exceed the
required efficiency. DOE calculated the
product conversion costs by multiplying
its per-line product conversion cost
estimate by the number of product lines
that manufacturers would need to
modify or develop at each TSL. For
traditional DHE and gas-fired water
heaters, DOE assumed that
manufacturers would convert all
existing product lines that did not meet
the efficiencies required at that TSL.
However, for gas hearth DHE DOE
assumed that manufacturers would only
convert up to 50-percent of their
existing product lines that did not meet
the required efficiencies. DOE’s
estimates of the product conversion
costs for all of the heating products
addressed in this rulemaking can be
found in section V.B.2 of today’s notice
and in chapter 12 of the NOPR TSD.
DOE also evaluated the level of
capital conversion costs manufacturers
would incur to comply with potential
amended energy conservation
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standards. During interviews, DOE
asked manufacturers to estimate the
required capital conversion costs to
expand the production of higherefficiency products or quantify the
required tooling and plant changes if
product lines meeting the required
efficiency level do not exist. For
residential gas-fired storage water
heaters, electric storage water heaters,
and gas-fired pool heaters, DOE based
its capital conversion costs for most
TSLs on these interviews. DOE verified
the accuracy of these capital conversion
costs by comparing them to a separate
bottoms-up estimate of the number of
sub-assembly and assembly lines for
each manufacturer and the required
tooling changes to each line at each
TSL, considering the costs of recent line
upgrades. As a final verification, DOE
examined what level of capital
investments would be required to
maintain the historical value for net
plant, property, and equipment as a
ratio of total revenue. For gas-fired and
electric storage water heaters at TSL 5,
DOE used the industry-wide capital
conversion costs for the standard-size
volumes at TSL 4. At TSL 5 DOE also
used a separate estimate to calculate the
additional capital conversion costs that
would be required to manufacture gasfired condensing water heaters and
electric heat pump water heaters for
rated storage volumes above 55 gallons.
For oil-fired storage water heaters, gasfired instantaneous water heaters, and
DHE, DOE used a bottoms-up approach
to estimate the cost of additional
production equipment and changes to
existing production lines that the
industry would require at each TSL.
DOE used feedback from manufacturer
interviews about the tooling
requirements at each efficiency level
and product catalogs to estimate the
total capital conversion costs for each
product category at each TSL.
DOE did not consider the provisions
in the American Recovery and
Reinvestment Act of 2009, Public Law
111–5, in its estimates of the capital
conversion costs for all products. The
industrial development bonds and
advanced energy project tax credit
programs in that Act have not been fully
distributed, and there is insufficient
information available to do a thorough
analysis of their potential impacts. It is
also unclear if manufacturers of
residential water heaters, DHE, or pool
heaters would qualify for these
provisions. DOE is not aware of any
manufacturers of products covered by
this rulemaking being awarded funds
from these programs (see https://
www.energy.gov/recovery/ for a list of
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awardees). Therefore, DOE did not
include the bonds or tax credit in its
analysis for this NOPR of potential
impacts on the three heating product
industries. DOE’s estimates of the
capital conversion costs for all three
types of heating products can be found
in section V.B.2 of today’s notice and in
chapter 12 of the NOPR TSD.
b. GRIM Scenarios
i. Residential Water Heater StandardsCase Shipments Forecasts
The GRIM used several residential
water heater shipments developed in
the NIA. The NIA incorporated different
scenarios that account for fuel
switching, penetration rates of gas-fired
instantaneous water heaters, growth
rates of ENERGY STAR products, and
economic growth rates. To account for
the likely impacts on the water heater
industry of amended energy
conservation standards, DOE used the
main NIA shipment scenario. The main
NIA water heater scenario accounted for
fuel switching. In this scenario, DOE
considered the potential for current
users of electric storage water heaters to
instead purchase a gas-fired storage
water heater replacement if amended
energy conservation standard for
electric storage water heaters were set at
levels that would effectively require the
use of heat pumps. The main NIA
scenario used the Reference case gasfired instantaneous water heater market
share scenario. Finally, the main NIA
scenario used the Reference case
economic growth scenario and the
moderate rate of efficiency growth
scenarios. In all standards-case
shipment scenarios, DOE considered
that shipments at efficiencies below the
projected minimum standard levels
would roll up to those efficiency levels
in response to amended energy
conservation standards. See section
IV.F.1 of this NOPR and chapter 10 for
more information on the residential
water heater standards-case shipment
scenarios.
ii. Direct Heating Equipment and Pool
Heater Shipment Scenarios
For the DHE and pool heater
shipments, DOE used the NIA
shipments in the base case and the
standards case. DOE also considered
that shipments at efficiencies below the
projected minimum standard levels in
the base case would roll up to those
efficiency levels in response to amended
energy conservation standards. See
section IV.F.1 of this NOPR and chapter
10 of the NOPR TSD for additional
details about the shipment scenarios.
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iii. Markup Scenarios
In the GRIM, DOE used the MSPs
estimated in the engineering analysis for
each product class and efficiency level.
The MSPs include direct manufacturing
production costs (i.e., labor, material,
and overhead estimated in DOE’s
MPCs), all non-production costs (i.e.,
SG&A, R&D, shipping, and interest),
along with profit.
DOE used several standards-case
markup scenarios to represent the
uncertainty about the potential impacts
on prices and profitability following the
implementation of amended energy
conservation standards. For the three
types of heating products, DOE analyzed
two markup scenarios: (1) a preservation
of return on invested capital scenario,
and (2) a preservation of operating profit
scenario.
Return on invested capital is defined
as net operating profit after taxes
divided by the total invested capital
(fixed assets and working capital, or net
plant, property, and equipment plus
working capital). In the preservation of
return on invested capital scenario, the
manufacturer markups are set so that
the return on invested capital the year
after the compliance date of the
amended energy conservation standards
is the same as in the base case. This
scenario models the situation in which
manufacturers maintain a similar level
of profitability from the investments
required by amended energy
conservation standards as they do from
their current business operations. After
standards, manufacturers have higher
net operating profits but also greater
working capital and investment
requirements. Because manufacturers
earn additional operating profit from the
investments required by the amended
energy conservation standards, this
scenario represents the high bound to
profitability following standards.
During interviews, multiple
manufacturers stated that the higher
production costs could severely harm
profitability. Because of the highly
competitive market, several
manufacturers suggested that the
additional costs required at higher
efficiencies could not be fully passed
through to customers. In the
preservation of operating profit markup
scenario, manufacturer markups are
lowered so that only the total operating
profit in absolute dollars is maintained
as before the amended energy
conservation standard. DOE
implemented this scenario in GRIM by
lowering the manufacturer markups at
each TSL to yield approximately the
same earnings before interest and taxes
in the standards case in the year after
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the compliance date of the amended
standards, as in the base case. This
scenario represents the lower bound of
industry profitability following
amended energy conservation standards
because higher production costs and the
investments required to comply with
the amended energy conservation
standard do not yield additional
operating profit.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
3. Discussion of Comments
During the February 2009 public
meeting, interested parties commented
on the assumptions and results of the
preliminary analysis. In oral and written
comments, interested parties discussed
the effects of the current economic
downturn on manufacturers, the high
costs required to educate installers and
service contractors, and potential
employment impacts due to amended
energy conservation standards. DOE
addresses these comments below. DOE
also received comments on the
cumulative burden of ultra-low-NOX
requirements, which are addressed in
sections IV.C and V.B.2.f.
a. Responses to General Comments
AHRI stated that DOE must take into
account the impacts of the current
economic conditions on the
manufacturing industry in the
manufacturer impact analysis. (AHRI,
Public Meeting Transcript, No. 34.4 at
p. 19)
In the MIA, DOE models the impacts
of amended energy conservation
standards on manufacturers of
residential water heaters, DHE, and pool
heaters from the base year to the end of
the analysis period (i.e., 2010–2045 for
residential water heaters and 2010–2043
for DHE and pool heaters). DOE notes
the compliance dates for all three
heating products (i.e., 2015 for
residential water heaters and 2013 for
DHE and pool heaters). Using
information that only reflects these
three industries during the current
economic downturn would not be
representative of the three heating
products over the entire analysis period.
DOE used the most current information
that is publicly available in many of its
estimates and analyses, inputs that take
the current economic downturn into
consideration. For example, as
described in section IV.C.4.b, DOE uses
5-year averages for metal material prices
and up-to-date prices for other raw
materials and purchased components in
its engineering analysis cost models. For
today’s notice, DOE also updated many
of its LCC and NIA assumptions to
better reflect the most recent
information (e.g., AEO2009) and in
response to comments from interested
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parties (sections IV.E and IV.F). For the
MIA, DOE uses financial parameters like
standard R&D to model the cash-flow
impacts on the water heater, DHE, and
pool heater industries. To calculate the
estimates of the financial parameters
used in the GRIMs, DOE examined 6
years of SEC 10–K data. While DOE
updated some of these GRIM estimates
based on interviews with
manufacturers, these changes were
made to better reflect the parameters
that are representative of each industry
over the long-term and are not
specifically attributable to current
economic conditions.
b. Water Heater Comments
BWC and AHRI stated that the
economic downturn has limited the
funding available for R&D and the
tooling necessary to develop and
manufacture more-efficient products.
(BWC, No. 46 at p. 3; AHRI, No. 33 at
p. 1) Noritz America Corporation also
stated that the economy has greatly
affected manufacturers’ bottom line and
ability to support R&D. (Noritz, No. 36
at p. 3)
For today’s notice, DOE includes the
capital and product conversion costs
that would be required to meet the
entire industry demand at each TSL.
While DOE agrees that the current
economic downturn may affect the
funding for R&D and capital
expenditures in the near term, DOE
notes that the compliance date for the
residential water heater standard is
2015. In the GRIM, DOE allocates its
estimates of the product conversion and
capital conversion costs in between the
announcement of the final rule adopting
energy conservation standard (estimated
to be March 2010) and the compliance
date requiring compliance with the
energy conservation standards for water
heaters. DOE also assumes that more of
the capital conversion and product
conversion costs will occur closer to the
compliance date than the
announcement date. Because most of
the product conversion and capital
conversion costs are allocated several
years in the future, it is expected that
the economic conditions at that time
will be different than they are currently.
BWC argued that as new technologies
are developed, manufacturers must
incur additional costs to educate
installers and service contractors. (BWC,
No. 46 at p. 3)
DOE agrees with BWC that a higher
energy conservation standard could
require manufacturers to incur costs to
educate installers and service
contractors, especially if the products
have to change dramatically to
accommodate amended energy
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conservation standards. During
interviews, manufacturers indicated that
significant resources are required to
educate installers and service
contractors when a new product is
introduced. The resources required are
even greater when the new product
involves a new technology or a new
mode of operation. For example, an
energy conservation standard that
eliminates atmospheric gas-fired storage
water heaters would have such an
impact on manufacturers. Product
conversion costs are one-time
investments which encompass research,
development, testing, and marketing,
focused on making product designs
comply with the amended energy
conservation standard. Hence, DOE
includes an estimate of the cost to
manufacturers to educate installers and
service contractors in the product
conversion costs at each TSL.
Bock asserted that the ENERGY STAR
program will affect consumer
purchasing patterns. Bock commented
that ENERGY STAR, which ignored oilfired storage water heaters, caused a loss
of market share, a reduction in
shipments, and a decrease in
employment for oil-fired storage water
heater manufacturers. (Bock, No. 53 at
p. 3)
DOE agrees that a reduction in oilfired storage water heater shipments
could affect employment at oil-fired
manufacturers’ plants. However, DOE
does not believe that the proposed
energy conservation standard will cause
a reduction in oil-fired storage water
heater shipments. For example, today’s
proposed energy conservation standards
increase the installed price of electric
storage water heaters, gas storage water
heaters, and instantaneous gas-fired
water heaters by roughly $132, $101,
and $588, respectively over the current
baseline products. The installed cost of
an oil-fired storage water heater
increases by only $61. DOE does not
believe that these minimum price
increases for consumers would distort
the market such that consumers would
elect to replace oil-fired storage water
heaters with another type of water
heater. DOE addresses the direct
employment impacts due to standards
in section V.B.2.d.
4. Manufacturer Interviews
DOE interviewed manufacturers
representing over 95 percent of
residential storage water heater sales,
about 50 percent of gas-fired
instantaneous water heater sales,
approximately 99 percent of traditional
DHE sales (gas wall fan, gas wall gravity,
gas floor, and gas room DHE), over 50
percent of gas hearth DHE sales, and
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about 75 percent of pool heater sales.
These interviews were beyond those
DOE conducted as part of the
engineering analysis. DOE used these
interviews to tailor each GRIM to
incorporate unique financial
characteristics for each industry. DOE
contacted companies from its database
of manufacturers, which provided a
representative sample of each industry.
All interviews provided information
that DOE used to evaluate the impacts
of potential amended energy
conservation standards on manufacturer
cash flows, manufacturing capacities,
and employment levels.
Before each telephone interview or
site visit, DOE provided company
representatives with an interview guide
that included the topics for which DOE
sought input. The MIA interview topics
included: (1) Key issues to this
rulemaking; (2) a company overview
and organizational characteristics; (3)
manufacturer production costs and
selling prices; (4) manufacturer markups
and profitability; (5) shipment
projections and market shares; (6)
product mix; (7) financial parameters;
(8) conversion costs; (9) cumulative
regulatory burden; (10) direct
employment impact assessment; (11)
exports, foreign competition, and
outsourcing; (12) consolidation; and (13)
impacts on small business. The MIA
interview guide for storage water heaters
contained three additional sections: (1)
Ultra-low-NOX water heaters; (2) unit
shipping methods and associated costs;
and (3) alternative energy efficiency
equations. Appendix 12A of the NOPR
TSD contains the five interview guides
DOE used to conduct the MIA
interviews.
In the manufacturer interviews, DOE
asked manufacturers to describe their
major concerns about this rulemaking.
The following sections describe the
most significant key issues identified by
manufacturers. DOE also includes
additional concerns in chapter 12 of the
TSD. DOE’s responses are provided
where relevant in today’s notice.
a. Storage Water Heater Key Issues
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
i. Fuel Switching
Gas-fired storage, electric storage, and
oil-fired storage water heater
manufacturers are concerned that this
energy conservation standard
rulemaking could cause fuel switching.
While most storage water heater
manufacturers also sell gas-fired
instantaneous water heaters, storage
manufacturers are concerned that a
more aggressive standard on gas-fired
and electric storage units could lower
the first cost differential of gas-fired
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instantaneous water heaters and
increase their market penetration.
Increased penetration of gas-fired
instantaneous water heaters would
lower the shipments of storage water
heaters, resulting in lower profitability
and fewer shipments for manufacturers
that focus on storage water heaters,
especially if they lose market share to
companies that exclusively manufacture
instantaneous water heaters.
ii. Ultra-Low-NOX Requirements
Manufacturers that make gas-fired
storage water heaters are concerned
about the large product development
costs to meet the ultra-low-NOX
requirements in some regions of the
Southwest. In particular, manufacturers
are concerned that higher energy factors,
lower NOX emissions, and compliance
with existing safety regulations are often
at odds. Manufacturers also stated that
the higher cost of the ultra-low-NOX gas
storage water heaters would hurt
consumers in those regions and could
cause them to switch to less expensive
electric storage units.
iii. Profitability
Manufacturers stated that amended
energy conservations standards could
affect profitability. At any TSL,
manufacturers will be forced to
discontinue a certain percentage of their
existing products and make potentially
significant product and plant
modifications. If manufacturers earn a
lower markup for more-efficient
products after the amended energy
conservation standard, their profit
margin would decrease. Energy
conservation standards could also harm
profitability by eliminating up-sell
opportunities to more-efficient units
that earn a greater absolute profit.
Finally, while manufacturers generally
agree with DOE’s estimate of
manufacturer production costs, many
noted that their actual product offerings
are more segmented into multiple
models made at various production
locations. Multiple product offerings
could make it more difficult to reach the
price points DOE calculates. If
production costs were higher, markups
would be lower than the manufacturer
markup DOE assumes and profitability
would decrease.
iv. Appropriateness of Heat Pump Water
Heaters
Heat pump water heaters are
effectively required for all rated storage
volumes at TSL 6 and TSL 7 and for a
portion of the market at TSL 5 for
electric storage water heaters to meet the
specified efficiency level. Most electric
storage water heater manufacturers
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disagreed with DOE’s decision to
include heat pump water heaters in the
electric storage water heater product
class. In addition, all electric storage
water heater manufacturers agreed that
this technology is only appropriate for
the ENERGY STAR level, not a
minimum required efficiency. While
many manufacturers intend to or
currently are designing heat pump water
heaters in response to the ENERGY
STAR requirements, manufacturers
believe that setting a minimum standard
during the design phase is not
appropriate and could cause many
serious and negative consequences.
Manufacturers listed many reasons
why this technology is not ready to be
applied across the millions of electric
storage water heaters needed to satisfy
demand. A significant problem is that
heat pump water heaters could not be
installed in a large portion of existing
homes (e.g., 30 to 40 percent of homes),
without incurring tremendous costs for
affected consumers to modify their
existing structures. The technology also
has not been fully developed and has
not yet been proven reliable for largescale manufacturing. Some
manufacturers are concerned that any
problems that arise with applying the
technology across millions of electric
storage water heaters that could not be
proven by the compliance date of the
rule would cause significant harm to
their industry due to the antibacksliding provision in EPCA.
Manufacturers stated that other
problems could arise with the
production of heat pump water heaters
if the standard were set at TSL 6 or TSL
7. For example, there is almost no
existing capacity to manufacture these
water heaters, especially on the scale
that an energy conservation standard
would require. Requiring over 4 million
annual shipments in 2015 could lead to
acquisition problems because
component suppliers are not prepared
for such a jump in demand. In
particular, acquiring sufficient
compressors, thermal expansion valves,
and other purchased parts to meet
market demand could be a challenge.
Manufacturers also added that setting
the energy conservation standard at a
level effectively requiring the use of
heat pump technology would cause
many negative impacts in the industry,
even if the technology were proven by
the compliance date specified in the
final rule. Because of the increased labor
required, manufacturers would have to
consider shifting a considerable portion
of production overseas to obtain viable
production costs, as was true for the
residential air-conditioning industry.
Domestic employment in the industry
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would be affected because only part of
the production would likely remain in
the United States after the compliance
date of the amended energy
conservation standard.
Manufacturers also stated that they
would incur significant conversion costs
if the standard level effectively
mandates heat pump water heaters, for
the reasons explained below. Every
main assembly line and feeder line
would need modifications to integrate
the new assembly into existing
production facilities. Finally,
manufacturers would face a significant
challenge to retrain their service
technicians and installers for a
completely new technology. Because the
technology has not been fully
developed, the skills needed to service
and install heat pump water heaters are
unknown. However, manufacturers
indicated that a combination of
plumbing and HVAC skills would be
required that do not exist today.
v. Capital Conversion Costs for Oil-Fired
Storage Water Heaters
Oil-fired storage water heater
manufacturers indicated that capital
conversion costs for oil-fired storage
water heaters at higher efficiency levels,
while perhaps not appearing
prohibitively large on a nominal basis,
are extremely significant relative to the
volume of oil-fired water heater
shipments. At any level above TSL 1, at
least one manufacturer with substantial
market share indicated that there is a
real risk that these capital and product
conversion costs could cause it to exit
the market.
b. Gas-Fired Instantaneous Water Heater
Key Issues
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
i. Potential Market Distortion
Manufacturers stated that amended
energy conservation standard could
greatly affect the market penetration of
gas-fired instantaneous water heaters. If
the prices were greatly increased
relative to storage water heaters, market
penetration could be slowed. In
addition, a drastic increase in the
required efficiency (at TSL 7) could
disrupt current arrangements with
overseas suppliers or parent companies
and limit product availability in the
United States.
ii. Ultra-Low-NOX Requirements
Manufacturers of gas-fired
instantaneous water heaters expressed
great concern about the conflicting
requirements of higher energy factor
requirements and pending ultra-lowNOX requirements. At most efficiency
levels, manufacturers commented that
there is a tradeoff in burner design
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between higher efficiency and lower
NOX emissions. Manufacturers
indicated that they have not found a
solution and are very concerned about
concurrently meeting the ultra-low-NOX
requirements and amended energy
conservation standards.
c. Direct Heating Equipment Key Issues
(Gas Wall Fan, Gas Wall Gravity, Gas
Floor, and Gas Room Direct Heating
Equipment)
i. Consumer Impacts
Manufacturers remarked that energy
conservation standards could hurt
consumers, arguing that many of
existing installations cannot be replaced
with more-efficient units because of
space considerations. Customers that
choose these units would either have to
pay for structural modifications or
switch to a different heat source. Some
manufacturers also noted that
improvements in efficiency for the most
common type of traditional DHE (gas
wall gravity DHE) have long paybacks at
any TSL.
All manufacturers stated that gas wall
gravity and gas room DHE provide a
unique utility by operating in the event
of a power failure. Manufacturers stated
that consumers would be hurt if these
products required line power, because it
would leave many without a backup
source of heat.
ii. Significant Capital and Product
Development Costs
Manufacturers stated that any product
conversion or capital conversion cost
would be difficult to justify because of
the very low shipment volumes of each
product line. Manufacturers remarked
that any required investments could
force them to reduce their product
offerings at best and permanently exit
the market at worst. Due to the large
number of product offerings that would
need to be recertified and/or redesigned,
some manufacturers argued that 3 years
would not be enough lead time. Finally,
because shipment volumes are so low,
any investment would significantly add
to the final cost of the product,
assuming that manufacturers could pass
part of the increased cost on to
consumers.
Manufacturers are also concerned that
higher production costs could drive
more consumers to purchase a central
system rather than replace their failed
direct heating system. If shipments
declined at all, manufacturers stated
they would be less able to justify the
required investment to upgrade
products and product lines, which
would hurt their industry further. All
manufacturers said that potential energy
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65921
conservation standards are a real threat
to their business and could cause them
to exit the market completely.
d. Direct Heating Equipment Key Issues
(Gas Hearth Direct Heating Equipment)
i. Loss of Aesthetic Appeal for
Decorative Products
According to manufacturers, all gas
hearth products have an aesthetic
function in addition to a heating
function. In fact, manufacturers stated
that the primary function of most gas
hearth products covered by this
rulemaking is the ambiance and
aesthetic appeal provided by the flame.
Gas hearth DHE are used mostly to zone
heat when occupants are in close
proximity or to supplement a central
heating system, but are used as a
primary heating source only in very rare
cases.
Because gas hearth DHE are mostly
decorative items in residences,
manufacturers believe that energy
conservation standards could have a
different impact on their industry than
the water heater industry, for example.
Gas hearth manufacturers stated that the
utility of the other strictly heating
products covered by today’s rule has
little to do with the appearance of the
products and would not be impacted at
any standard level. For example, the
consumer utility from water heaters
would not be impacted by amended
energy conservation standards as long as
hot water is still delivered. However,
the relevant manufacturers were greatly
concerned that potential energy
conversation standards for gas hearth
DHE could harm their industry and
consumers in qualitative ways, in
addition to the direct impacts on
industry value. Their customers’ needs
are related to the size, shape, and
appearance of the flame, and for these
customers, efficiency is not usually a
concern, given such products’ low usage
patterns. Manufacturers stated that they
earn premiums for aesthetic features
such as better-looking flames and more
attractive masonry, rather than higher
efficiency. Multiple manufacturers
stated that the yellow flames that
consumers look for in a log set depend
on a rich gas-to-air mixture, which
inherently limits the achievable energy
efficiency. Hence, at higher efficiency
levels, it becomes more difficult to
improve efficiency and maintain a
desirable flame color, an impact that is
hard to measure and which could have
a significant detrimental effect on the
industry.
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ii. Product Switching and Profitability
Because the aesthetic appeal of the
unit and the flame are critical features,
manufacturers believed that overlystringent energy conservation standards
could cause customers to switch to noncovered hearth products, such as woodburning stoves or strictly decorative
units, if the energy conservation
standards greatly raised prices. Finally,
manufacturers stated that a significant
portion of gas hearth products are
purchased by builders. Because the
appearance of the units and the flame
are more critical features than
efficiency, manufacturers believed that
higher costs could cause more builders
to purchase strictly decorative products
that are not covered by this rulemaking.
Besides higher prices potentially
causing a switching to non-covered
products, manufacturers were also
concerned that higher standards had the
potential to lower overall demand for
gas hearth products. At higher costs,
manufacturers believe that customers
would no longer purchase inserts for
existing homes or that builders would
make gas hearth products in new homes
an option rather than a standard feature.
Manufacturers also believe that a
shrinking market would reduce profits.
e. Pool Heater Key Issues
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
i. Impacts on Consumers
Manufacturers stated that an amended
energy conservation standards set above
an efficiency level achievable using
atmospheric technology (TSL 3 through
TSL 6) could hurt consumers.
According to manufacturers, customers
would not recoup the initial higher
costs with lower utility bills at these
TSLs. Because most residential pool
heaters are a luxury item with low usage
patterns, most customers do not
purchase units at TSL 4 and above.
Thus, manufacturers stated that moreefficient residential pool heaters are
only appropriate in commercial settings
(e.g., hotels, gyms) because the higher
usage allows such customers to recoup
the higher initial costs.
ii. Future Shipment Trends
Manufacturers commented that pool
heater shipments follow new housing
starts. Because the new housing market
is down, manufacturers have lowered
their projections for future pool heater
sales as well. Manufacturers also do not
expect future shipments to return to
historical levels, as recent new housing
starts have increasingly been on smaller
lots that do not have the room to
accommodate swimming pools.
Manufacturers are concerned that
amended energy conservation standards
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could further decrease future sales.
Because pool heaters are not a necessity,
the higher initial cost could dissuade
some consumers from replacing a failed
unit or adding a heater to a new pool or
spa. Manufacturers are also concerned
that a higher price point for gas-fired
pool heaters could hurt future
shipments by making alternatives like
solar or heat pump pool heaters
comparatively cheaper. Manufacturers
stated that this trend is already a
concern because a few States and
utilities have offered subsidies for solar
water heaters.
iii. Future NOX Emission Requirements
According to manufacturers,
residential gas-fired pool heaters are
currently exempt from ultra-low NOX
requirements in the Southwest air
quality management districts. However,
most manufacturers voiced a concern
over potential future requirements. If air
quality management districts set more
restrictive NOX requirements in the
future, some manufacturers may be
required to incur a costly redesign of
their burner systems.
I. Employment Impact Analysis
Employment impacts consist of direct
and indirect impacts. Direct
employment impacts are any changes in
the number of employees of
manufacturers of the appliance products
that are the subject of this rulemaking,
their suppliers, and related service
firms. Indirect employment impacts are
changes in employment in the larger
economy that occur due to the shift in
expenditures and capital investment
caused by the purchase and operation of
more-efficient appliances. The MIA
addresses the direct employment
impacts that concern manufacturers of
the three heating products.
Indirect employment impacts from
standards consist of the net jobs created
or eliminated in the national economy,
other than in the manufacturing sector
being regulated, due to: (1) Reduced
spending by end users on energy
(electricity, gas—including liquefied
petroleum gas—and oil); (2) reduced
spending on new energy supply by the
utility industry; (3) increased spending
on new products to which the new
standards apply; and (4) the effects of
those three factors throughout the
economy. DOE expects the net monetary
savings from standards to be redirected
to other forms of economic activity.
DOE also expects these shifts in
spending and economic activity to affect
the demand for labor in the short term,
as explained below.
One method for assessing the possible
effects on the demand for labor of such
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shifts in economic activity is to compare
sectoral employment statistics
developed by the Labor Department’s
Bureau of Labor Statistics (BLS). (Data
on industry employment, hours, labor
compensation, value of production, and
the implicit price deflator for output for
these industries are available upon
request by calling the Division of
Industry Productivity Studies (202–691–
5618) or by sending a request by e-mail
to dipsweb@bls.gov. See https://
www.bls.gov/news.release/
prin1.nr0.htm.) The 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. 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. 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.
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 manufacturing sectors).
In developing the preliminary
analysis and today’s NOPR, DOE
estimated indirect national employment
impacts using an input/output model of
the U.S. economy called Impact of
Sector Energy Technologies (ImSET).
ImSET is a spreadsheet model of the
U.S. economy that focuses on 188
sectors most relevant to industrial,
commercial, and residential building
energy use. (See J. M. Roop, M. J. Scott,
and R. W. Schultz, ImSET: Impact of
Sector Energy Technologies, PNNL–
15273, Pacific Northwest National
Laboratory, 2005). ImSET is a specialpurpose version of the ‘‘U.S. Benchmark
National Input-Output’’ (I–O) model
designed to estimate the national
employment and income effects of
energy-saving technologies. The ImSET
software includes a computer-based I–O
model with structural coefficients to
characterize economic flows among the
188 sectors. ImSET’s national economic
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I–O structure is based on a 1997 U.S.
benchmark table (See Lawson, Ann M.,
et al., ‘‘Benchmark Input-Output
Accounts of the U.S. Economy, 1997,’’
Survey of Current Business, Dec. 2002,
pp. 19–117.) Chapter 13 of the NOPR
TSD presents further details on the
employment impact analysis.
J. Utility Impact Analysis
The utility impact analysis included
an analysis of the potential effects of
amended energy conservation standards
for the three types of heating products
on the electric and gas utility industries.
For this analysis, DOE used NEMS–BT
to generate forecasts of electricity and
natural gas consumption, electricity
generation by plant type, and electric
generating capacity by plant type. DOE
conducts the utility impact analysis as
a scenario that departs from the latest
AEO Reference case. In other words, the
energy savings impacts from amended
energy conservation standards are
modeled using NEMS–BT to generate
forecasts that deviate from the AEO
Reference case. Chapter 13 of the NOPR
TSD presents details on the utility
impact analysis.
NEEA and NPCC urged DOE to
consider the impact of gas-fired
instantaneous water heaters on local gas
distribution companies’ ability to meet
hot water demand during peak periods,
and the possibility that they may have
to invest in shoring up system peak
capacity, adding significant upward
pressure on rates. (NEEA and NPCC, No.
42 at p. 9) DOE acknowledges that
growing use of gas-fired instantaneous
water heaters could contribute to peak
demand problems, and that higherefficiency gas-fired instantaneous water
heaters could ameliorate the problem.
However, DOE currently does not have
adequate data to reliably quantify the
potential impacts.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
K. Environmental Analysis
DOE has prepared a draft
environmental assessment (EA)
pursuant to the National Environmental
Policy Act and the requirements of 42
U.S.C. 6295(o)(2)(B)(i)(VI) and 6316(a)
to determine the environmental impacts
of the proposed standards. DOE
estimated the impacts on power sector
emissions of CO2, NOX, and Hg using
the NEMS–BT model. Because the onsite operation of non-electric heating
products requires use of fossil fuels and
results in emissions of CO2, NOX and
sulfur dioxide (SO2), DOE also
accounted for the reduction in these
emissions due to standards at the sites
where these appliances are used.
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1. Impacts of Standards on Emissions
In the EA, NEMS–BT is run similarly
to the AEO NEMS, except that heating
product energy use is reduced by the
amount of energy saved (by fuel type)
due to each TSL. The inputs of national
energy savings come from the NIA
spreadsheet model; the output is the
forecasted physical emissions at each
TSL. The net benefit of the standard is
the difference between emissions
estimated by NEMS–BT at each TSL and
the AEO Reference Case.
NEMS–BT tracks CO2 emissions using
a detailed module that provides results
with broad coverage of all sectors and
inclusion of interactive effects. For the
preliminary TSD, DOE used AEO2008.
For today’s NOPR, DOE used the
AEO2009 NEMS (stimulus version). For
the final rule, DOE intends to revise the
emissions analysis using the most
current AEO.
DOE has preliminarily determined
that SO2 emissions from affected
Electric Generating Units (EGUs) are
subject to nationwide and regional
emissions cap and trading programs that
create uncertainty about the standards’
impact on SO2 emissions. Title IV of the
Clean Air Act sets an annual emissions
cap on SO2 for all affected EGUs. SO2
emissions from 28 eastern States and the
District of Columbia (D.C.) are also
limited under the Clean Air Interstate
Rule (CAIR, published in the Federal
Register on May 12, 2005. 70 FR 25162
(May 12, 2005), which creates an
allowance-based trading program that
will gradually replace the Title IV
program in those States and DC. (The
recent legal history surrounding CAIR is
discussed below.) The attainment of the
emissions caps is flexible among EGUs
and is enforced through the use of
emissions allowances and tradable
permits. Energy conservation standards
could lead EGUs to trade allowances
and increase SO2 emissions that offset
some or all SO2 emissions reductions
attributable to the standard. DOE is not
certain that there will be reduced
overall SO2 emissions from the
standards. The NEMS–BT modeling
system that DOE used to forecast
emissions reductions currently indicates
that no physical reductions in power
sector emissions would occur for SO2.
The above considerations prevent DOE
from estimating SO2 reductions from
standards at this time.
Even though DOE is not certain that
there will be reduced overall emissions
from the standard, there may be an
economic benefit from reduced demand
for SO2 emission allowances. Electricity
savings decrease the generation of SO2
emissions from power production,
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which can lessen the need to purchase
SO2 emissions allowance credits, and
thereby decrease the costs of complying
with regulatory caps on emissions.
Much like SO2, NOX emissions from
28 eastern States and the District of
Columbia (DC) are limited under the
CAIR. Although CAIR has been
remanded to EPA by the D.C. Circuit, it
will remain in effect until it is replaced
by a rule consistent with the Court’s
July 11, 2008, opinion in North Carolina
v. EPA. 531 F.3d 896 (D.C. Cir. 2008);
see also North Carolina v. EPA, 550 F.3d
1176 (D.C. Cir. 2008). Because all States
covered by CAIR opted to reduce NOX
emissions through participation in capand-trade programs for electric
generating units, emissions from these
sources are capped across the CAIR
region.
In the 28 eastern States and DC where
CAIR is in effect, DOE’s forecasts
indicate that no NOX emissions
reductions will occur because of the
permanent cap. Energy conservation
standards have the potential to produce
environmentally-related economic
impact in the form of lower prices for
emissions allowance credits, if they
were large enough. However, DOE has
preliminarily concluded that the
proposed standard would not have such
an effect because the estimated
reduction in NOX emissions or the
corresponding allowance credits in
States covered by the CAIR cap would
be too small to affect allowance prices
for NOX under the CAIR.
The proposed standard would reduce
NOX emissions in those 22 States not
affected by the CAIR. As a result, DOE
used the NEMS–BT to forecast emission
reductions from the standards that are
considered in today’s NOPR.
Similar to emissions of SO2 and NOX,
future emissions of Hg would have been
subject to emissions caps. The Clean Air
Mercury Rule (CAMR) would have
permanently capped emissions of
mercury for new and existing coal-fired
plants in all States beginning in 2010
(70 FR 28606). However, the CAMR was
vacated by the D.C. Circuit in its
decision in New Jersey v. Environmental
Protection Agency. 517 F 3d 574 (D.C.
Cir. 2008) Thus, DOE was able to use
the NEMS–BT model to estimate the
changes in Hg emissions resulting from
the proposed rule.
EEI stated that DOE’s analysis of
emissions from electric power
generation should account for the rise in
renewable portfolio standards and the
possibility of an upcoming CO2 cap and
trade program, both of which would
reduce the amount of emissions
produced per kWh electricity generated.
(EEI, No. 40 at p. 6) DOE’s projections
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of CO2 emissions from electric power
generation are based on the AEO2009
version of NEMS. The emissions
projections reflect market factors and
policies that affect utility choice of
power plants for electricity generation,
including existing renewable portfolio
standards. Because of the speculative
nature of forecasting future regulations,
DOE does not include the impact of
possible future regulations in its
forecasts.
EEI stated that if DOE examines
changes in power plant emissions, then
it should also examine changes in the
emissions associated with oil extraction
(domestic and overseas), crude oil
transportation (sea and land-based),
natural gas flaring, oil refining, refined
oil delivery, natural gas production,
natural gas delivery, natural gas delivery
system methane leaks, propane
production and delivery, and emissions
associated with the extraction and
importation of liquefied natural gas.
(EEI, No. 40 at p. 6)
Emissions occur at each stage of the
extraction, conversion, and delivery of
the energy supply chain. Nonetheless,
emissions are dominated by power plant
emissions in the case of electric
appliances and in-house emissions in
the case of natural gas and oil-fired
appliances, so DOE focuses on those
points.
The operation of non-electric heating
products requires use of fossil fuels and
results in emissions of CO2, NOX and
SO2 at the sites where these appliances
are used. NEMS–BT provides no means
for estimating such emissions. DOE
calculated the effect of the proposed
standards on the above site emissions
based on emissions factors derived from
the literature.
2. Valuation of CO2 Emissions
Reductions
DOE received comments on the
desirability of valuing the CO2
emissions reductions that result from
standards. NRDC stated that DOE must
account for the value of avoided carbon
emissions. (NRDC, No. 48 at p. 4) NEEA
and NPCC stated that it would be
inappropriate to assign a value of zero
to avoided carbon emissions. (NEEA
and NPCC, No. 42 at p. 10) Earthjustice
stated that DOE must consider wellestablished literature on the value of
CO2 emissions to consider reduced
emissions in States that will remain
outside CO2 reduction regimes.
(Earthjustice, No. 47 at p. 4)
For today’s NOPR, DOE is relying on
a new set of values recently developed
by an interagency process that
conducted a thorough review of existing
estimates of the social cost of carbon
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(SCC). The SCC is intended to be a
monetary measure of the incremental
damage resulting from greenhouse gas
(GHG) emissions, including, but not
limited to, net agricultural productivity
loss, human health effects, property
damages from sea level rise, and
changes in ecosystem services. Any
effort to quantify and to monetize the
harms associated with climate change
will raise serious questions of science,
economics, and ethics. But with full
regard for the limits of both
quantification and monetization, the
SCC can be used to provide estimates of
the social benefits of reductions in GHG
emissions.
For at least three reasons, any single
estimate of the SCC will be contestable.
First, scientific and economic
knowledge about the impacts of climate
change continues to grow. With new
and better information about relevant
questions, including the cost, burdens,
and possibility of adaptation, current
estimates will inevitably change over
time. Second, some of the likely and
potential damages from climate
change—for example, the value society
places on adverse impacts on
endangered species—are not included
in all of the existing economic analyses.
These omissions may turn out to be
significant in the sense that they may
mean that the best current estimates are
too low. Third, controversial ethical
judgments, including those involving
the treatment of future generations, play
a role in judgments about the SCC (see
in particular the discussion of the
discount rate, below).
To date, regulations have used a range
of values for the SCC. For example, a
regulation proposed by the U.S.
Department of Transportation (DOT) in
2008 assumed a value of $7 per ton CO2
(2006$) for 2011 emission reductions
(with a range of $0–14 for sensitivity
analysis). Regulation finalized by DOE
used a range of $0–$20 (2007$). Both of
these ranges were designed to reflect the
value of damages to the United States
resulting from carbon emissions, or the
‘‘domestic’’ SCC. In the final Model
Year 2011 Corporate Average Fuel
Economy rule, DOT used both a
domestic SCC value of $2/t CO2 and a
global SCC value of $33/t CO2 (with
sensitivity analysis at $80/tCO2),
increasing at 2.4 percent per year
thereafter.
In recent months, a variety of agencies
have worked to develop an objective
methodology for selecting a range of
interim SCC estimates to use in
regulatory analyses until improved SCC
estimates are developed. The following
summary reflects the initial results of
these efforts and proposes ranges and
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values for interim social costs of carbon
used in this rule. It should be
emphasized that the analysis described
below is preliminary. These complex
issues are of course undergoing a
process of continuing review. Relevant
agencies will be evaluating and seeking
comment on all of the scientific,
economic, and ethical issues before
establishing final estimates for use in
future rulemakings.
The interim judgments resulting from
the recent interagency review process
can be summarized as follows: (a) DOE
and other Federal agencies should
consider the global benefits associated
with the reductions of CO2 emissions
resulting from efficiency standards and
other similar rulemakings, rather
continuing the previous focus on
domestic benefits; (b) these global
benefits should be based on SCC
estimates (in 2007$) of $55, $33, $19,
$10, and $5 per ton of CO2 equivalent
emitted (or avoided) in 2007 (in
calculating the benefits reported in this
NOPR, DOE has escalated the 2007$
values to 2008$ for consistency with
other dollar values presented in this
notice, resulting in SCC estimates (in
2008$) of approximately $5, $10, $20,
$34, and $56); (c) the SCC value of
emissions that occur (or are avoided) in
future years should be escalated using
an annual growth rate of 3 percent from
the current values); and (d) domestic
benefits are estimated to be
approximately 6 percent of the global
values. These interim judgments are
based on the following considerations.
1. Global and domestic estimates of
SCC. Because of the distinctive nature of
the climate change problem, estimates
of both global and domestic SCC values
should be considered, but the global
measure should be ‘‘primary.’’ This
approach represents a departure from
past practices, which relied, for the
most part, on measures of only domestic
impacts. As a matter of law, both global
and domestic values are permissible; the
relevant statutory provisions are
ambiguous and allow the agency to
choose either measure. (It is true that
Federal statutes are presumed not to
have extraterritorial effect, in part to
ensure that the laws of the United States
respect the interests of foreign
sovereigns. But use of a global measure
for the SCC does not give extraterritorial
effect to Federal law and hence does not
intrude on such interests.)
It is true that under OMB guidance,
analysis from the domestic perspective
is required, while analysis from the
international perspective is optional.
The domestic decisions of one nation
are not typically based on a judgment
about the effects of those decisions on
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other nations. But the climate change
problem is highly unusual in the sense
that it involves (a) a global public good
in which (b) the emissions of one nation
may inflict significant damages on other
nations and (c) the United States is
actively engaged in promoting an
international agreement to reduce
worldwide emissions.
In these circumstances, the global
measure is preferred. Use of a global
measure reflects the reality of the
problem and is expected to contribute to
the continuing efforts of the United
States to ensure that emission
reductions occur in many nations.
Domestic SCC values are also
presented. The development of a
domestic SCC is greatly complicated by
the relatively few region- or countryspecific estimates of the SCC in the
literature. One potential estimate comes
from the DICE (Dynamic Integrated
Climate Economy, William Nordhaus)
model. In an unpublished paper,
Nordhaus (2007) produced
disaggregated SCC estimates using a
regional version of the DICE model. He
reported a U.S. estimate of $1/tCO2
(2007 value, 2007$), which is roughly
11 percent of the global value.
An alternative source of estimates
comes from a recent EPA modeling
effort using the FUND (Climate
Framework for Uncertainty, Negotiation
and Distribution, Center for Integrated
Study of the Human Dimensions of
Global Change) model. The resulting
estimates suggest that the ratio of
domestic to global benefits varies with
key parameter assumptions. With a 3
percent discount rate, for example, the
US benefit is about 6 percent of the
global benefit for the ‘‘central’’ (mean)
FUND results, while, for the
corresponding ‘‘high’’ estimates
associated with a higher climate
sensitivity and lower global economic
growth, the US benefit is less than 4
percent of the global benefit. With a 2
percent discount rate, the U.S. share is
about 2 to 5 percent of the global
estimate.
Based on this available evidence, a
domestic SCC value equal to 6 percent
of the global damages is used in this
rulemaking. This figure is in the middle
of the range of available estimates from
the literature. It is recognized that the 6
percent figure is approximate and
highly speculative and alternative
approaches will be explored before
establishing final values for future
rulemakings.
2. Filtering existing analyses. There
are numerous SCC estimates in the
existing literature, and it is legitimate to
make use of those estimates to produce
a figure for current use. A reasonable
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starting point is provided by the metaanalysis in Richard Tol, ‘‘The Social
Cost of Carbon: Trends, Outliers, and
Catastrophes, Economics: The OpenAccess, Open-Assessment E–Journal,’’
Vol. 2, 2008–25. https://www.economicsejournal.org/economics/journalarticles/
2008-25 (2008). With that starting point,
it is proposed to ‘‘filter’’ existing SCC
estimates by using those that (1) are
derived from peer-reviewed studies; (2)
do not weight the monetized damages to
one country more than those in other
countries; (3) use a ‘‘business as usual’’
climate scenario; and (4) are based on
the most recent published version of
each of the three major integrated
assessment models (IAMs): FUND, DICE
and PAGE (Policy Analysis of the
Greenhouse Effect).
Proposal (1) is based on the view that
those studies that have been subject to
peer review are more likely to be
reliable than those that have not been.
Proposal (2) is based on a principle of
neutrality and simplicity; it does not
treat the citizens of one nation
differently on the basis of speculative or
controversial considerations. Proposal
(3) stems from the judgment that as a
general rule, the proper way to assess a
policy decision is by comparing the
implementation of the policy against a
counterfactual state where the policy is
not implemented. A departure from this
approach would be to consider a more
dynamic setting in which other
countries might implement policies to
reduce GHG emissions at an unknown
future date, and the United States could
choose to implement such a policy now
or in the future.
Proposal (4) is based on three
complementary judgments. First, the
FUND, PAGE, and DICE models now
stand as the most comprehensive and
reliable efforts to measure the damages
from climate change. Second, the latest
versions of the three IAMs are likely to
reflect the most recent evidence and
learning, and hence they are presumed
to be superior to those that preceded
them. It is acknowledged that earlier
versions may contain information that is
missing from the latest versions. Third,
any effort to choose among them, or to
reject one in favor of the others, would
be difficult to defend at this time. In the
absence of a clear reason to choose
among them, it is reasonable to base the
SCC on all of them.
The agency is keenly aware that the
current IAMs fail to include all relevant
information about the likely impacts
from greenhouse gas emissions. For
example, ecosystem impacts, including
species loss, do not appear to be
included in at least two of the models.
Some human health impacts, including
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increases in food-borne illnesses and in
the quantity and toxicity of airborne
allergens, also appear to be excluded. In
addition, there has been considerable
recent discussion of the risk of
catastrophe and of how best to account
for worst-case scenarios. It is not clear
whether the three IAMs take adequate
account of these potential effects.
3. Use a model-weighted average of
the estimates at each discount rate. At
this time, there appears to be no
scientifically valid reason to prefer any
of the three major IAMs (FUND, PAGE,
and DICE). Consequently, the estimates
are based on an equal weighting of
estimates from each of the models.
Among estimates that remain after
applying the filter, the average of all
estimates within a model is derived.
The estimated SCC is then calculated as
the average of the three model-specific
averages. This approach ensures that the
interim estimate is not biased towards
specific models or more prolific authors.
4. Apply a 3 percent annual growth
rate to the chosen SCC values. SCC is
assumed to increase over time, because
future emissions are expected to
produce larger incremental damages as
physical and economic systems become
more stressed as the magnitude of
climate change increases. Indeed, an
implied growth rate in the SCC is
produced by most studies that estimate
economic damages caused by increased
GHG emissions in future years. But
neither the rate itself nor the
information necessary to derive its
implied value is commonly reported. In
light of the limited amount of debate
thus far about the appropriate growth
rate of the SCC, applying a rate of 3
percent per year seems appropriate at
this stage. This value is consistent with
the range recommended by IPCC (2007)
and close to the latest published
estimate (Hope, 2008).
For climate change, one of the most
complex issues involves the appropriate
discount rate. OMB’s current guidance
offers a detailed discussion of the
relevant issues and calls for discount
rates of 3 percent and 7 percent. It also
permits a sensitivity analysis with low
rates for intergenerational problems. (‘‘If
your rule will have important
intergenerational benefits or costs you
might consider a further sensitivity
analysis using a lower but positive
discount rate in addition to calculating
net benefits using discount rates of 3
and 7 percent.’’) The SCC is being
developed within the general context of
the current guidance.
The choice of a discount rate,
especially over long periods of time,
raises highly contested and exceedingly
difficult questions of science,
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economics, philosophy, and law. See,
e.g., William Nordhaus, ‘‘The Challenge
of Global Warming (2008); Nicholas
Stern, The Economics of Climate
Change’’ (2007); ‘‘Discounting and
Intergenerational Equity’’ (Paul Portney
and John Weyant, eds., 1999). Under
imaginable assumptions, decisions
based on cost-benefit analysis with high
discount rates might harm future
generations—at least if investments are
not made for the benefit of those
generations. See Robert Lind, ‘‘Analysis
for Intergenerational Discounting,’’ id. at
173, 176–177. At the same time, use of
low discount rates for particular projects
might itself harm future generations, by
ensuring that resources are not used in
a way that would greatly benefit them.
In the context of climate change,
questions of intergenerational equity are
especially important.
Reasonable arguments support the use
of a 3 percent discount rate. First, that
rate is among the two figures suggested
by OMB guidance, and hence it fits with
existing National policy. Second, it is
standard to base the discount rate on the
compensation that people receive for
delaying consumption, and the 3
percent rate is close to the risk-free rate
of return, proxied by the return on long
term inflation-adjusted U.S. Treasury
Bonds. (In the context of climate
change, it is possible to object to this
standard method for deriving the
discount rate.) Although these rates are
currently closer to 2.5 percent, the use
of 3 percent provides an adjustment for
the liquidity premium that is reflected
in these bonds’ returns.
At the same time, other arguments
support use of a 5 percent discount rate.
First, that rate can also be justified by
reference to the level of compensation
for delaying consumption, because it fits
with market behavior with respect to
individuals’ willingness to trade off
consumption across periods as
measured by the estimated post-tax
average real returns to private
investment (e.g., the S&P 500). In the
climate setting, the 5 percent discount
rate may be preferable to the riskless
rate because it is based on risky
investments and the return to projects to
mitigate climate change is also risky. In
contrast, the 3 percent riskless rate may
be a more appropriate discount rate for
projects where the return is known with
a high degree of confidence (e.g.,
highway guardrails).
Second, 5 percent, and not 3 percent,
is roughly consistent with estimates
implied by reasonable inputs to the
theoretically derived Ramsey equation,
which specifies the optimal time path
for consumption. That equation
specifies the optimal discount rate as
the sum of two components. The first
reflects the fact that consumption in the
future is likely to be higher than
consumption today (even accounting for
climate impacts), so diminishing
marginal utility implies that the same
monetary damage will cause a smaller
reduction of utility in the future.
Standard estimates of this term from the
economics literature are in the range of
3 to 5 percent. The second component
reflects the possibility that a lower
weight should be placed on utility in
the future, to account for social
impatience or extinction risk, which is
specified by a pure rate of time
preference (PRTP). A conventional
estimate of the PRTP is 2 percent. (Some
observers believe that a principle of
intergenerational equity suggests that
the PRTP should be close to zero.) It
follows that discount rate of 5 percent
is within the range of values which are
able to be derived from the Ramsey
equation, albeit at the low end of the
range of estimates usually associated
with Ramsey discounting.
It is recognized that the arguments
above—for use of market behavior and
the Ramsey equation—face objections in
the context of climate change, and of
course there are alternative approaches.
In light of climate change, it is possible
that consumption in the future will not
be higher than consumption today, and
if so, the Ramsey equation will suggest
a lower figure. Some people have
suggested that a very low discount rate,
below 3 percent, is justified in light of
the ethical considerations calling for a
principle of intergenerational neutrality.
See Nicholas Stern, ‘‘The Economics of
Climate Change’’ (2007); for contrary
views, see William Nordhaus, A
Question of Balance (2008); Martin
Weitzman, ‘‘Review of the Stern Review
on the Economics of Climate Change.’’
Journal of Economic Literature, 45(3):
703–724 (2007). Additionally, some
analyses attempt to deal with
uncertainty with respect to interest rates
over time; a possible approach enabling
the consideration of such uncertainties
is discussed below. Richard Newell and
William Pizer, ‘‘Discounting the Distant
Future: How Much Do Uncertain Rates
Increase Valuations?’’ J. Environ. Econ.
Manage. 46 (2003) 52–71.
The application of the methodology
outlined above yields estimates of the
SCC that are reported in Table IV.31.
These estimates are reported separately
using 3 percent and 5 percent discount
rates. The cells are empty in rows 10
and 11 because these studies did not
report estimates of the SCC at a 3
percent discount rate. The modelweighted means are reported in the final
or summary row; they are $33 per tCO2
at a 3% discount rate and $5 per tCO2
with a 5% discount rate.
TABLE IV.31—GLOBAL SOCIAL COST OF CARBON ESTIMATES ($/TCO2 IN 2007 IN 2007$), BASED ON 3% AND 5%
DISCOUNT RATES *
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Model
1
2
3
4
5
6
7
8
......
......
......
......
......
......
......
......
9 ......
10 ....
11 ....
Study
Climate scenario
3%
...........
...........
...........
...........
...........
...........
...........
...........
Anthoff et al. 2009 .......................................
Anthoff et al. 2009 .......................................
Anthoff et al. 2009 .......................................
Link and Tol 2004 ........................................
Link and Tol 2004 ........................................
Guo et al. 2006 ............................................
Guo et al. 2006 ............................................
Guo et al. 2006 ............................................
PAGE ...........
PAGE ...........
DICE ............
Wahba & Hope 2006 ...................................
Hope 2006 ...................................................
Nordhaus 2008 ............................................
FUND default ...............................................
SRES A1b ....................................................
SRES A2 ......................................................
No THC ........................................................
THC continues .............................................
Constant PRTP ............................................
Gollier discount 1 .........................................
Gollier discount 2 .........................................
FUND Mean .................................................
A2–scen .......................................................
......................................................................
......................................................................
6
1
9
12
12
5
14
7
8.25
57
......................
......................
FUND
FUND
FUND
FUND
FUND
FUND
FUND
FUND
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TABLE IV.31—GLOBAL SOCIAL COST OF CARBON ESTIMATES ($/TCO2 IN 2007 IN 2007$), BASED ON 3% AND 5%
DISCOUNT RATES *—Continued
Model
Study
Climate scenario
Summary ............................................................................................
3%
Model-weighted Mean .................................
5%
33
5
* The sample includes all peer reviewed, non-equity-weighted estimates included in Tol (2008), Nordhaus (2008), Hope (2008), and Anthoff et
al. (2009), that are based on the most recent published version of FUND, PAGE, or DICE and use business-as-usual climate scenarios. All values are based on the best available information from the underlying studies about the base year and year dollars, rather than the Tol (2008) assumption that all estimates included in his review are 1995 values in 1995$. All values were updated to 2007 using a 3 percent annual growth
rate in the SCC, and adjusted for inflation using GDP deflator.
DOE used the model-weighted mean
values of $33 and $5 per ton (2007$), as
these represent the estimates associated
with the 3 percent and 5 percent
discount rates, respectively. The 3
percent and 5 percent estimates have
independent appeal and at this time a
clear preference for one over the other
is not warranted. These values were
then escalated to 2008$ and rounded to
$34 and $5. Thus, DOE has also
included—and centered its current
attention on—the average of the
estimates associated with these discount
rates, which is approximately $20 (in
2008$). (Based on the $20 global value,
the domestic value would be
approximately $1 per ton of CO2
equivalent.)
It is true that there is uncertainty
about interest rates over long time
horizons. Recognizing that point,
Newell and Pizer have made a careful
effort to adjust for that uncertainty. See
Newell and Pizer, supra. This is a
relatively recent contribution to the
literature.
There are several concerns with using
this approach in this context. First, it
would be a departure from current OMB
guidance. Second, an approach that
would average what emerges from
discount rates of 3 percent and 5
percent reflects uncertainty about the
discount rate, but based on a different
model of uncertainty. The Newell-Pizer
approach models discount rate
uncertainty as something that evolves
over time; in contrast, one alternative
approach would assume that there is a
single discount rate with equal
probability of 3 percent and 5 percent.
Table IV.32 reports on the application
of the Newell-Pizer adjustments. The
precise numbers depend on the
assumptions about the data generating
process that governs interest rates.
Columns (1a) and (1b) assume that
‘‘random walk’’ model best describes
the data and uses 3 percent and 5
percent discount rates, respectively.
Columns (2a) and (2b) repeat this,
except that it assumes a ‘‘meanreverting’’ process. As Newell and Pizer
report, there is stronger empirical
support for the random walk model.
TABLE IV.32—GLOBAL SOCIAL COST OF CARBON ESTIMATES ($/TCO2 IN 2007 IN 2007$),* USING NEWELL & PIZER
ADJUSTMENT FOR FUTURE DISCOUNT RATE UNCERTAINTY**
Random-walk model
Model
Study
Climate scenario
Mean-reverting model
3%
5%
3%
5%
(1a)
(1b)
(2a)
(2b)
Wahba & Hope 2006 ...............
Hope 2006 ...............................
Nordhaus 2008 ........................
FUND default ...........................
SRES A1b ...............................
SRES A2 .................................
No THC ....................................
THC continues .........................
Constant PRTP ........................
Gollier discount 1 .....................
Gollier discount 2 .....................
FUND Mean .............................
A2-scen ....................................
..................................................
..................................................
10
2
15
20
20
9
14
7
12
97
....................
....................
0
0
0
6
4
0
0
¥1
1
13
13
15
7
1
10
13
13
6
14
7
9
63
....................
....................
¥1
¥1
¥1
4
2
¥1
0
¥1
0
8
8
9
Summary ..................................................................
Model-weighted Mean .............
55
10
36
6
1
2
3
4
5
6
7
8
.......
.......
.......
.......
.......
.......
.......
.......
9 .......
10 .....
11 .....
FUND
FUND
FUND
FUND
FUND
FUND
FUND
FUND
....
....
....
....
....
....
....
....
Anthoff et al. 2009 ...................
Anthoff et al. 2009 ...................
Anthoff et al. 2009 ...................
Link and Tol 2004 ....................
Link and Tol 2004 ....................
Guo et al. 2006 ........................
Guo et al. 2006 ........................
Guo et al. 2006 ........................
PAGE ....
PAGE ....
DICE ......
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
* The sample includes all peer reviewed, non-equity-weighted estimates included in Tol (2008), Nordhaus (2008), Hope (2008), and Anthoff et
al. (2009), that are based on the most recent published version of FUND, PAGE, or DICE and use business-as-usual climate scenarios. All values are based on the best available information from the underlying studies about the base year and year dollars, rather than the Tol (2008) assumption that all estimates included in his review are 1995 values in 1995$. All values were updated to 2007 using a 3 percent annual growth
rate in the SCC, and adjusted for inflation using GDP deflator.
** Assumes a starting discount rate of 3 percent. Newell and Pizer (2003) based adjustment factors are not applied to estimates from Guo et
al. (2006) that use a different approach to account for discount rate uncertainty (rows 7–8).
The resulting estimates of the social
cost of carbon are necessarily greater.
When the adjustments from the random
walk model are applied, the estimates of
the social cost of carbon are $10 and $55
(2007$), with the 5 percent and 3
percent discount rates, respectively. The
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application of the mean-reverting
adjustment yields estimates of $6 and
$36 (2007$). Since the random walk
model has greater support from the data,
DOE also used the SCC values of $10
and $55 (2007$). When escalated to
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2008$, these values were approximately
$10 and $56.
In summary, in considering the
potential global benefits resulting from
reduced CO2 emissions, DOE used
values based on a social cost of carbon
of approximately $5, $10, $20, $34 and
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jlentini on DSKJ8SOYB1PROD with PROPOSALS2
$56 per metric ton avoided in 2007
(values expressed in 2008$). DOE also
calculated the domestic benefits based
on a value of approximately $1 per
metric ton avoided in 2007. To monetize
the CO2 emissions reductions expected
to result from amended standards for
heating products in 2013–2045, DOE
escalated the above values for 2007
using a three-percent escalation rate. As
indicated in the discussion above,
estimates of SCC are assumed to
increase over time since future
emissions are expected to produce
larger incremental damages as physical
and economic systems become more
stressed as the magnitude of climate
change increases. Although most studies
that estimate economic damages caused
by increased GHG emissions in future
years produce an implied growth rate in
the SCC, neither the rate itself nor the
information necessary to derive its
implied value is commonly reported.
However, applying a rate of 3 percent
per year is consistent with the range
recommended by IPCC (2007).
DOE recognizes that scientific and
economic knowledge about the
contribution of CO2 and other GHG 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 CO2 emissions reduction
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 greenhouse
gas 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
uncertainty involved with this
particular issue, DOE has included in
this proposed rule the most recent
values and analyses resulting from the
ongoing interagency review process.
3. Valuation of Other Emissions
Reductions
DOE also investigated the potential
monetary benefit of reduced NOX and
Hg emissions from the TSLs it
considered. As previously stated, DOE’s
analysis assumed the presence of
nationwide emission caps on SO2 and
caps on NOX emissions in the 28 States
covered by the CAIR. In the presence of
these caps, the NEMS–BT modeling
system that DOE used to forecast
emissions reduction indicated that no
physical reductions in power sector
emissions would occur for SO2, but that
the standards could put slight
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downward pressure on the prices of
emissions allowances in cap-and-trade
markets. Estimating this effect is very
difficult because such factors as credit
banking can change the trajectory of
prices. From its modeling to date, DOE
is unable to estimate a benefit from SO2
emissions reductions at this time. See
the environmental assessment in the
NOPR TSD for further details.
As noted above, new or amended
energy conservation standards would
reduce NOX emissions in those 22 States
that are not affected by the CAIR, in
addition to the reduction in site NOX
emissions nationwide. DOE estimated
the monetized value of NOX emissions
reductions resulting from each of the
TSLs considered for today’s NOPR
based on environmental damage
estimates from the literature. Available
estimates suggest a very wide range of
monetary values, ranging from $370 per
ton to $3,800 per ton of NOX from
stationary sources, measured in 2001$
(equivalent to a range of $442 to $4,540
per ton in 2008$). Refer to the OMB,
Office of Information and Regulatory
Affairs, ‘‘2006 Report to Congress on the
Costs and Benefits of Federal
Regulations and Unfunded Mandates on
State, Local, and Tribal Entities,’’
Washington, DC, for additional
information.
For Hg emissions reductions, DOE
estimated the monetized values
resulting from the TSLs considered for
today’s NOPR based on environmental
damage estimates from the literature.
The impact of mercury emissions from
power plants on humans is considered
highly uncertain. However, DOE
identified two estimates of the
environmental damage of mercury based
on estimates of the adverse impact of
childhood exposure to methyl mercury
on intelligence quotient (IQ) for
American children, and subsequent loss
of lifetime economic productivity
resulting from these IQ losses. The highend estimate is based on an estimate of
the current aggregate cost of the loss of
IQ in American children that results
from exposure to mercury of U.S. power
plant origin ($1.3 billion per year in
2000$), which works out to $33.3
million per ton emitted per year
(2008$). Refer to L. Trasande et al.,
‘‘Applying Cost Analyses to Drive
Policy that Protects Children,’’ 1076
Ann. N.Y. Acad. Sci. 911 (2006) for
additional information. DOE’s low-end
estimate is $0.66 million per ton emitted
(in 2004$) or $0.745 million per ton in
2008$. DOE derived this estimate from
an evaluation of mercury control that
used different methods and assumptions
from the first study but was also based
on the present value of the lifetime
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earnings of children exposed. See Ted
Gayer and Robert Hahn, ‘‘Designing
Environmental Policy: Lessons from the
Regulation of Mercury Emissions,’’
Regulatory Analysis 05–01, AEIBrookings Joint Center for Regulatory
Studies, Washington, DC (2004). A
version of this paper was published in
the Journal of Regulatory Economics in
2006.
EEI stated that the costs of
remediating emissions of CO2, SO2,
NOX, and Hg are included in the rates
customers pay, so monetizing their
values would be double counting. (EEI,
No. 40 at p. 6) DOE understands the
comment as referring to actions power
plant operators take to meet
environmental regulations, the costs of
which are reflected in electricity rates.
With regulations currently in place,
revised standards for heating products
would result in a reduction in CO2,
NOX, and Hg emissions by avoiding
electricity generation. Because these
emissions impose societal costs, their
reduction has an economic value that
can be estimated.
Earthjustice stated that DOE must
calculate and monetize the value of the
reductions in emissions of particulate
matter (PM) that will result from
standards; even if DOE cannot consider
secondary PM emissions, it must
consider primary emissions.
(Earthjustice, No. 47 at p. 5) DOE agrees
that PM impacts are of concern due to
human exposures that can impact
health. But impacts of PM emissions
reduction are much more difficult to
estimate than other emissions
reductions due to the complex
interactions between PM, other power
plant emissions, meteorology and
atmospheric chemistry that impact
human exposure to particulates. Human
exposure to PM usually occurs at a
significant distance from the power
plants that are emitting particulates and
particulate precursors. When power
plant emissions travel this distance they
undergo highly complex atmospheric
chemical reactions. While the
Environmental Protection Agency (EPA)
does keep inventories of direct PM
emissions of power plants, in its source
attribution reviews the EPA does not
separate direct PM emissions from
power plants from the particulates
indirectly produced through complex
atmospheric chemical reactions. This is
in part because SO2 emissions react
with direct PM emissions particles to
produce combined sulfate particulates.
Thus it is not useful to examine how the
standard impacts direct PM emissions
independent of indirect PM production
and atmospheric dynamics. DOE is not
currently able to run a model that can
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make these estimates reliably at the
national level.
Earthjustice stated that DOE must
consider coming climate change
legislation and a national cap on carbon
emissions and must account for the
effect of the standards in reducing
allowance prices. (Earthjustice, No. 47
at p. 4) Because no climate change
legislation has been enacted to date, the
timing and shape of any national cap on
carbon emissions is uncertain at this
point. Therefore, DOE did not account
for such a cap in its NOPR analysis.
V. Analytical Results
A. Trial Standard Levels
DOE analyzed the benefits and
burdens of a number of TSLs for each
of the three types of heating products
separately. For a given product
consisting of several product classes,
DOE developed some of the TSLs so that
each TSL is comprised of energy
efficiency levels from each product class
that exhibit similar characteristics. For
example, in the case of water heaters,
one of the TSLs consists of the max-tech
efficiency levels from each product class
being considered for this rulemaking.
DOE attempted to limit the number of
TSLs considered for the NOPR by
eliminating efficiency levels that do not
exhibit significantly different economic
and/or engineering characteristics from
the efficiency levels already selected as
a TSL. A description of each TSL DOE
analyzed for each of the three types of
heating products is provided below.
While DOE only presents the results for
those efficiency levels in TSL
combinations in today’s NOPR, DOE
presents the results for all efficiency
levels analyzed in the NOPR TSD. DOE
requests comments on the results for all
of the efficiency levels since DOE could
consider any combination of efficiency
levels for the final rule as a result of
comments from interested parties.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
1. Water Heaters
Table V.1 shows the seven TSLs DOE
analyzed for water heaters. Since
amended water heater standards would
apply to the full range of storage
volumes, DOE is presenting the TSLs for
water heaters in terms of the energy
efficiency equations, rather than only
showing the required efficiency level at
the representative capacities. As
discussed in section IV.C.7, DOE is
using the alternative energy-efficiency
equations developed in the engineering
analysis for the NOPR. DOE is grouping
the energy efficiency equations for each
of the four water heater product classes
to show the benefits and burdens of
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amended energy conservation
standards.
For TSL 1, 2, 3, and 4, DOE is using
the rated storage volume divisions and
the energy efficiency equations as
shown in section IV.C.7, which specify
a two-slope approach. TSL 1 consists of
the efficiency levels for each product
class that are approximately equal to the
current shipment-weighted average
efficiency. TSL 2 and TSL 3 consist of
efficiency levels with slightly higher
efficiencies compared to TSL 1 for most
of the product classes. TSL 4 represents
the maximum electric resistance water
heater efficiency across the entire range
of storage volumes that DOE analyzed
for electric storage water heaters, and
the maximum atmospherically vented
efficiency across the entire range of
storage volumes that DOE analyzed for
gas-fired storage water heaters.
For TSL 5, DOE further modified the
two-slope approach developed in the
engineering analysis. For this TSL, DOE
considers a pairing of efficiency levels
that would promote the penetration of
advanced technologies into the electric
and gas-fired storage water heater
markets and potentially save additional
energy by using a two-slope approach
with different requirements for each
subsection. Consequently, DOE pairs an
efficiency level requiring heat pump
technology for large-volume electric
storage water heaters with an efficiency
level achievable using electric resistance
technology for small-volume electric
storage water heaters. In addition, DOE
pairs an efficiency level requiring
condensing technology for large-volume
gas storage water heaters with an
efficiency level that can be achieved in
atmospherically vented gas-fired storage
water heaters with increased insulation
thickness for small storage volumes.
In addition to pairing different
technologies for small and large volume
products for TSL 5, DOE also modified
the division point between smallvolume and large-volume gas-fired and
electric storage water heaters. DOE used
an analysis of market data to determine
the initial division points (see section
IV.C.7 for details), which were 60
gallons for gas-fired storage water
heaters and 80 gallons for electric
storage water heaters. These division
points are used to modify the two-slope
equations for TSLs 1, 2, 3, and 4 (as well
as TSLs 6 and 7, described below).
Because DOE pairs two different
technologies for consideration as an
amended standard in TSL 5, DOE is
concerned that manufacturers may
attempt to circumvent the increased
standards for large-volume water heaters
by producing water heaters at volumes
just below the division points. As a
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65929
result, DOE has chosen to modify the
division points for TSL 5 to 55 gallons
for gas-fired and electric storage water
heaters to attempt to mitigate the
potential loophole. TSL 5 includes
efficiency levels that effectively require
heat pump technology for electric
storage water heater with rated storage
volumes above 55 gallons, and
efficiency levels that effectively require
condensing technology for gas-fired
storage water heaters with rated storage
volumes above 55 gallons. Using DOE’s
shipments model and market
assessment, DOE estimated
approximately 4 percent of gas-fired
storage water heater shipments and 11
percent of models would be subject to
the large-volume water heater
requirements using the TSL 5 division.
Similarly, DOE estimated approximately
9 percent of electric storage water heater
shipments and 27 percent of models
would be subject to the large volume
water heater requirements using the TSL
5 division.
DOE specifically seeks comment on
the different approach taken in TSL 5,
including the rated storage volume
division of 55 gallons between small
and large storage volumes for gas-fired
and electric storage water heaters at TSL
5. In particular, DOE is interested in
comments from interested parties
regarding whether DOE should consider
an alternative division in the final rule,
including (but not limited to), 66 gallons
or 75 gallons. In addition, DOE seeks
comments regarding whether different
divisions should be specified for gasfired and electric storage water heaters
such that a similar percentage of the
market is impacted in terms of
shipments and/or models.
TSL 6 uses the same divisions as TSL
1, 2, 3, and 4 for gas-fired water heaters.
TSL 6 is identical to TSL 4 except DOE
is considering a heat pump water heater
level for electric storage water heaters
across the entire range of storage
volumes, which is compatible with
ENERGY STAR criteria for electric
storage water heaters at the
representative rated storage volume.
DOE did use a division point for the
max-tech energy efficiency equations as
described in the engineering analysis.
TSL 7 consists of the max-tech
efficiency levels for each of the water
heater product classes at the time the
analysis was developed. TSL 6 and 7
both require efficiency levels that can be
met using heat pump technology for
electric storage water heaters. TSL 7,
however, requires a higher efficiency
level than TSL 6, which corresponds to
the max-tech efficiency level for the
representative rated storage capacity
(i.e., 2.2 EF at 50 gallons). TSL 7 also
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requires efficiency levels that can be
met using condensing technology for
gas-fired storage and instantaneous
water heaters.
Table V.1 demonstrates the energy
efficiency equations and associated two
slope divisions for TSLs 1 through 7.
TABLE V.1—TRIAL STANDARD LEVELS FOR RESIDENTIAL WATER HEATERS (ENERGY FACTOR)
Trial standard level
TSL 1 ...................................
Energy efficiency equation
For GSWHs with a Rated Storage Volume at or below
60 gallons:
EF = 0.675¥(0.0015 × Rated Storage Volume in gallons).
For GSWHs with a Rated Storage Volume above 60
gallons:
EF = 0.699¥(0.0019 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume at or below
80 gallons:
EF = 0.967¥(0.00095 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume above 80
gallons:
EF = 1.013¥(0.00153 × Rated Storage Volume in gallons).
For OSWHs (over the Entire Rated Storage Volume range):
EF = 0.64¥(0.0019 × Rated Storage Volume in gallons).
For GIWHs (over the Entire Rated Storage Volume range):
EF = 0.82¥(0.0019 × Rated Storage Volume in gallons).
TSL 2 ...................................
For GSWHs with a Rated Storage Volume at or below
60 gallons:
EF = 0.675¥(0.0012 × Rated Storage Volume in gallons).
For GSWHs with a Rated Storage Volume above 60
gallons:
EF = 0.717¥(0.0019 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume at or below
80 gallons:
EF = 0.966¥(0.0008 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume above 80
gallons:
EF = 1.026¥(0.00155 × Rated Storage Volume in gallons).
For OSWHs (over the Entire Rated Storage Volume range):
EF = 0.66¥(0.0019 × Rated Storage Volume in gallons).
For GIWHs (over the Entire Rated Storage Volume range):
EF = 0.82¥(0.0019 × Rated Storage Volume in gallons).
TSL 3 ...................................
For GSWHs with a Rated Storage Volume at or below
60 gallons:
EF = 0.675¥(0.0012 × Rated Storage Volume in gallons).
For GSWHs with a Rated Storage Volume above 60
gallons:
EF = 0.717¥(0.0019 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume at or below
80 gallons:
EF = 0.965¥(0.0006 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume above 80
gallons:
EF = 1.051¥(0.00168 × Rated Storage Volume in gallons).
For OSWHs (over the Entire Rated Storage Volume range):
EF = 0.66¥(0.0019 × Rated Storage Volume in gallons).
For GIWHs (over the Entire Rated Storage Volume range):
EF = 0.82¥(0.0019 × Rated Storage Volume in gallons).
For GSWHs with a Rated Storage Volume at or below
60 gallons:
EF = 0.675¥(0.0012 × Rated Storage Volume in gallons).
For GSWHs with a Rated Storage Volume above 60
gallons:
EF = 0.717¥(0.0019 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume at or below
60 gallons:
EF = 0.960¥(0.0003 × Rated Storage Volume in gallons).
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
TSL 4 ...................................
For ESWHs with a Rated Storage Volume above 60
gallons:
EF = 1.088¥(0.0019 × Rated Storage Volume in gallons).
For OSWHs (over the Entire Rated Storage Volume range):
EF = 0.68¥(0.0019 × Rated Storage Volume in gallons).
For GIWHs (over the Entire Rated Storage Volume range):
EF = 0.82¥(0.0019 × Rated Storage Volume in gallons).
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TABLE V.1—TRIAL STANDARD LEVELS FOR RESIDENTIAL WATER HEATERS (ENERGY FACTOR)—Continued
Trial standard level
TSL 5 ...................................
For GSWHs with a Rated Storage Volume at or below
55 gallons:
EF = 0.675¥(0.0012 × Rated Storage Volume in gallons).
For GSWHs with a Rated Storage Volume above 55
gallons:
EF = 0.831¥(0.00078 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume at or below
55 gallons:
EF = 0.960¥(0.0003 × Rated Storage Volume in gallons).
For ESWHs with a Rated Storage Volume above 55
gallons:
EF = 2.057¥(0.00113 × Rated Storage Volume in gallons).
For OSWHs (over the Entire Rated Storage Volume range):
EF = 0.68¥(0.0019 × Rated Storage Volume in gallons).
For GIWHs (over the Entire Rated Storage Volume range):
EF = 0.82¥(0.0019 × Rated Storage Volume in gallons).
TSL 6 ...................................
For GSWHs with a Rated Storage Volume at or below
60 gallons:
EF = 0.675¥(0.0012 × Rated Storage Volume in gallons).
For GSWHs with a Rated Storage Volume above 60
gallons:
EF = 0.717¥(0.0019 × Rated Storage Volume in gallons).
For ESWHs (over the Entire Rated Storage Volume range):
EF = 2.057¥(0.00113 × Rated Storage Volume in gallons).
For OSWHs (over the Entire Rated Storage Volume range):
EF = 0.68¥(0.0019 × Rated Storage Volume in gallons).
For GIWHs (over the Entire Rated Storage Volume range):
EF = 0.82¥(0.0019 × Rated Storage Volume in gallons).
TSL 7 ...................................
For GSWHs (over the Entire Rated Storage Volume range):
EF = 0.831¥(0.00078 × Rated Storage Volume in gallons).
For ESWHs (over the Entire Rated Storage Volume range):
EF = 2.057¥(0.00113 × Rated Storage Volume in gallons).
For OSWHs (over the Entire Rated Storage Volume range):
EF = 0.74¥(0.0019 × Rated Storage Volume in gallons).
For GIWHs (over the Entire Rated Storage Volume range):
EF = 0.95¥(0.0019 × Rated Storage Volume in gallons).
2. Direct Heating Equipment
Table V.2 demonstrates the six TSLs
DOE analyzed for DHE. TSL 1 consists
of the efficiency levels that are close to
that include electronic ignition and fan
assist (where applicable), and TSL 6
consists of the max-tech efficiency
levels.
the current shipment-weighted average
efficiency. TSL 2, TSL 3 and TSL 4
consist of efficiency levels that have
gradually higher efficiency than TSL 1.
TSL 5 consists of the efficiency levels
TABLE V.2—TRIAL STANDARD LEVELS FOR DIRECT HEATING EQUIPMENT (AFUE)
TSL 1
(percent)
Product class
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Gas
Gas
Gas
Gas
Gas
Wall Fan (over 42,000 Btu/h) ...............................................
Wall Gravity (over 27,000 and up to 46,000 Btu/h) .............
Floor (over 37,000 Btu/h) .....................................................
Room (over 27,000 and up to 46,000 Btu/h) .......................
Hearth (over 27,000 and up to 46,000 Btu/h) .....................
3. Gas-Fired Pool Heaters
Table V.3 shows the six TSLs DOE
analyzed for pool heaters. TSL 1
consists of the efficiency level that is
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TSL 2
(percent)
75
66
58
66
67
TSL 3
(percent)
76
68
58
67
67
close to the current shipment-weighted
average efficiency. TSL2 and TSL 3
consist of the efficiency levels that have
gradually higher efficiency than TSL 1.
TSL 4 is the highest efficiency level
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TSL 4
(percent)
77
71
58
68
67
80
71
58
68
72
TSL 5
(percent)
75
72
58
83
72
TSL 6
(percent)
80
72
58
83
93
with positive NPV. TSL 5 is the highest
analyzed non-condensing efficiency
level, and TSL 6 consists of the maxtech efficiency level.
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TABLE V.3—TRIAL STANDARD LEVELS FOR POOL HEATERS
[Thermal efficiency]
TSL 1
(percent)
Product class
Gas ...............................................................................................
B. Economic Justification and Energy
Savings
1. Economic Impacts on Consumers
a. Life-Cycle Cost and Payback Period
Consumers affected by new or
amended standards usually experience
higher purchase prices and lower
operating costs. Generally, these
impacts are best captured by changes in
life-cycle costs and payback period.
Therefore, DOE calculated the LCC and
PBP for the potential standard levels
TSL 2
(percent)
81
TSL 3
(percent)
82
considered in this rulemaking. DOE’s
LCC and PBP analyses provided key
outputs for each TSL, which are
reported by product in Table V.4
through Table V.13, below. In each
table, the first two outputs are the
average total LCC and the average LCC
savings. The next three outputs show
the percentage of households where the
purchase of a product complying with
each TSL would create a net life-cycle
cost, no impact, or a net life-cycle
savings for the purchaser. The last
outputs are the median PBP and the
TSL 4
(percent)
83
TSL 5
(percent)
84
TSL 6
(percent)
86
95
average PBP for the consumer
purchasing a design that complies with
the TSL. The results for each TSL are
relative to the efficiency distribution in
the base case (no amended standards).
DOE based its LCC and PBP analyses
for heating products on energy
consumption under conditions of actual
use, whereas it based the rebuttable
presumption PBP test on consumption
under conditions prescribed by the DOE
test procedure, as required by EPCA. (42
U.S.C. 6295(o)(2)(B)(iii))
TABLE V.4—GAS-FIRED STORAGE WATER HEATERS: LCC AND PBP RESULTS
LCC
Energy
factor
TSL
1 .......................................
2, 3, 4 ...............................
5 .......................................
6 .......................................
7 .......................................
0.62
0.63
* 0.63
0.67
0.80
Average
LCC
2008$
Average
LCC
savings
2008$
3,369
3,369
3,355
3,618
3,522
Payback period
Households with
Net cost
%
69
68
78
¥150
¥55
No impact
%
9
15
16
67
62
Net benefit
%
22
17
16
6
1
69
68
68
27
36
Median
years
Average
years
1.4
2.7
3.0
20.9
14.1
4.6
11.6
12.1
24.6
14.2
* For TSL 5, the EF and the results represent shipments-weighted averages f the EFs and results that apply to small- and large-volume water
heaters, respectively. For the other TSLs the EF and the results refer to the representative rated volume (40 gal).
TABLE V.5—ELECTRIC STORAGE WATER HEATERS: LCC AND PBP RESULTS
LCC
Energy
factor
TSL
1
2
3
4
5
6
7
.......................................
.......................................
.......................................
.......................................
.......................................
.......................................
.......................................
0.92
0.93
0.94
0.95
* 1.04
2.00
2.20
Average
LCC
2008$
Average
LCC
savings
2008$
3,372
3,361
3,351
3,342
3,306
3,145
3,095
Payback period
Households with
Net cost
%
16
23
32
39
96
224
273
No impact
%
10
11
20
25
25
45
45
Net benefit
%
32
29
14
10
10
5
1
59
60
66
65
65
50
54
Median
years
Average
years
2.8
3.0
4.5
5.8
5.9
8.3
8.2
7.8
8.0
8.6
8.8
9.1
25.9
21.5
* For TSL 5, the EF and the results represent shipments-weighted averages of the EFs and results that apply to small- and large-volume water
heaters, respectively. For the other TSLs the EF and the results refer to the representative rated volume (50 gal).
TABLE V.6 OIL-FIRED STORAGE WATER HEATERS: LCC AND PBP RESULTS
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
LCC
Energy
factor
TSL
1 .......................................
2 .......................................
3, 4, 5, 6 ...........................
7 .......................................
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0.60
0.62
0.68
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Average
LCC
2008$
Average
LCC
savings
2008$
8,616
8,377
8,190
7,863
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%
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288
395
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No impact
%
0
0
0
0
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%
69
52
45
7
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48
55
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years
0.7
0.4
0.5
1.4
Average
years
0.8
0.3
0.7
1.7
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TABLE V.7—GAS-FIRED INSTANTANEOUS WATER HEATERS: LCC AND PBP RESULTS
LCC
Energy
factor
TSL
1, 2, 3, 4, 5 ......................
6 .......................................
7 .......................................
Average
LCC
2008$
0.82
0.92
0.95
Average
LCC
savings
2008$
5,409
5,665
5,798
Payback period
Households with
Net cost
%
0
¥181
¥307
No impact
%
11
70
83
Net benefit
%
85
15
6
4
15
12
Median
years
Average
years
23.5
34.1
39.5
30.4
50.2
58.7
TABLE V.8—GAS WALL FAN DHE: LCC AND PBP RESULTS
LCC
TSL
AFUE %
1, 5 ...................................
2 .......................................
3 .......................................
4, 6 ...................................
75
76
77
80
Average
LCC
2008$
Average
LCC
savings
2008$
6,879
6,842
6,825
6,793
Payback period
Households with
Net cost
%
73
90
104
135
No impact
%
3
5
30
44
Net benefit
%
59
55
14
5
38
41
56
52
Median
years
Average
years
3.1
3.9
6.0
9.8
3.1
6.7
15.0
22.6
TABLE V.9—GAS WALL GRAVITY DHE: LCC AND PBP RESULTS
LCC
TSL
AFUE %
1 .......................................
2 .......................................
3, 4 ...................................
5, 6 ...................................
66
68
71
72
Average
LCC
2008$
Average
LCC
savings
2008$
6,533
6,458
6,349
6,473
Payback period
Households with
Net cost
%
25
83
192
68
No impact
%
12
19
39
59
Net benefit
%
70
40
0
0
18
41
61
41
Median
years
Average
years
8.1
6.5
8.3
13.0
14.8
10.9
14.1
26.5
TABLE V.10—GAS FLOOR DHE: LCC AND PBP RESULTS
LCC
TSL
AFUE %
1, 2, 3, 4, 5, 6 ..................
58
Average
LCC
2008$
Average
LCC
savings
2008$
7,404
Payback period
Households with
Net cost
%
13
No impact
%
25
Net benefit
%
57
18
Median
years
Average
years
14.7
20.4
TABLE V.11—GAS ROOM DHE: LCC AND PBP RESULTS
LCC
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
TSL
AFUE %
1 .......................................
2 .......................................
3, 4 ...................................
5, 6 ...................................
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67
68
83
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Average
LCC
2008$
Average
LCC
savings
2008$
7,702
7,630
7,567
6,892
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Net cost
%
42
96
143
646
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No impact
%
19
19
20
26
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Net benefit
%
50
25
25
25
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31
56
55
49
11DEP2
Median
years
8.1
4.9
5.3
7.0
Average
years
13.4
9.4
10.2
15.2
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TABLE V.12—GAS HEARTH DHE: LCC AND PBP RESULTS
LCC
TSL
AFUE %
1, 2, 3 ...............................
4, 5 ...................................
6 .......................................
Average
LCC
2008$
67
72
93
Average
LCC
savings
2008$
5,195
5,388
5,571
Payback period
Households with
Net cost
%
96
¥70
¥253
No impact
%
9
69
81
Net benefit
%
51
13
0
40
17
19
Median
years
Average
years
0.0
25.9
37.5
7.9
77.6
78.2
TABLE V.13—GAS-FIRED POOL HEATERS: LCC AND PBP RESULTS
LCC
Thermal
efficiency %
TSL
1
2
3
4
5
6
.......................................
.......................................
.......................................
.......................................
.......................................
.......................................
Average
LCC
2008$
81
82
83
84
86
95
Average
LCC
savings
2008$
6,383
6,395
6,395
6,461
7,034
7,809
24
18
39
¥13
¥555
¥1,323
Payback period
Households with
Net cost
%
No impact
%
6
31
52
* 59
90
96
Net benefit
%
64
46
24
22
6
1
30
22
24
20
5
3
Median
years
2.5
7.4
10.6
13.0
28.6
28.1
Average
years
3.5
10.1
18.7
19.5
42.4
37.2
* For TSL 4, DOE determined that 14 percent of the consumers will experience a net cost smaller than 2 percent of their total LCC (see chapter 8 of the TSD).
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
b. Analysis of Consumer Subgroups
For gas-fired and electric storage
water heaters, and gas wall fan and gas
wall gravity DHE, DOE estimated
consumer subgroup impacts for lowincome households and senior-only
households. In addition, for gas-fired
and electric storage water heaters, DOE
estimated consumer subgroup impacts
for households in multi-family housing
and households in manufactured homes
as well. (As a reminder and as explained
in section IV.6, not all products in this
rulemaking were included in DOE’s
consumer subgroup analysis.)
For gas-fired storage water heaters, the
impacts of the proposed standard (0.63
EF) are roughly the same for the senioronly sample and the low-income sample
as they are for the full household
sample for this product class. For the
multi-family sample and the
manufactured home sample, the average
LCC savings are somewhat lower than
they are for the full household sample,
and the fraction of households
experiencing a cost (negative savings) is
higher. In both cases, however, the
average LCC savings is positive, and
more than half of the households in the
identified subgroups would experience
an LCC benefit.
For electric storage water heaters, the
impacts of the proposed TSL 4 standard
(0.95 EF) are roughly the same for the
senior-only sample as they are for the
full household sample for this product
class. The impacts are slightly more
negative for the low-income sample, and
they are moderately more negative for
the multi-family sample and the
manufactured home sample. The
average LCC savings are ¥$2 for the
latter two subgroups, but in both cases,
more than half of the households in the
identified subgroups would experience
an LCC benefit.
In the case of a standard for electric
storage water heaters at TSL 5, which
would require 2.0 EF only for largevolume water heaters, the negative
subgroup impacts seen in the case of
TSL 6 are substantially less because
only a small fraction of the households
in the subgroups has large-volume water
heaters for which the standard would
effectively require a heat pump water
heater.
In the case of a standard for electric
storage water heaters at TSL 6, the
average LCC savings are lower for all of
the subgroups than for the full
household sample for this product class.
The multi-family subgroup would
experience an average negative LCC
savings of $359 (i.e., the average LCC
would increase), and three-fourths of
the households in the subgroup would
experience a net cost. For the other
subgroups, the fraction of households
that would experience a net cost is close
to or just above 50 percent, which is
slightly higher than for the full
household sample. The impact on the
multi-family subgroup is primarily due
to the lower hot water use among these
households.
For gas wall fan and gas wall gravity
DHE, DOE estimated that the impacts of
the proposed standards are roughly the
same for the senior-only sample and the
low-income sample as they are for the
full household sample for these product
classes.
Chapter 11 of the NOPR TSD presents
the detailed results of the consumer
subgroup analysis.
TABLE V.14—COMPARISON OF SUBGROUP IMPACTS FOR ELECTRIC STORAGE WATER HEATERS
Average LCC
savings
(2008$)
Subgroup
Households
with net cost
(%)
Median payback period
(years)
0.95 EF
Senior-only ...................................................................................................................................
Low-income ..................................................................................................................................
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17
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29
5.3
6.3
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TABLE V.14—COMPARISON OF SUBGROUP IMPACTS FOR ELECTRIC STORAGE WATER HEATERS—Continued
Average LCC
savings
(2008$)
Subgroup
Households
with net cost
(%)
Median payback period
(years)
¥2
¥2
39
35
34
25
6.8
7.0
5.8
30
143
¥359
81
224
Multi-family ...................................................................................................................................
Mobile Home ................................................................................................................................
All Households .............................................................................................................................
52
49
76
51
45
9.8
9.3
23.8
9.6
8.3
2.0 EF
Senior-only ...................................................................................................................................
Low-income ..................................................................................................................................
Multi-family ...................................................................................................................................
Mobile Home ................................................................................................................................
All Households .............................................................................................................................
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
c. Rebuttable Presumption Payback
As discussed above, EPCA provides a
rebuttable presumption that 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 (42 U.S.C.
6295(o)(2)(B)(iii)) 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).
In the present case, DOE calculated a
rebuttable presumption payback period
for each TSL. Rather than using
distributions for input values, DOE used
discrete values and, as required by
EPCA, based the calculation on the
assumptions in the DOE test procedures
for the three types of heating products.
As a result, DOE calculated a single
rebuttable presumption payback value,
and not a distribution of payback
periods, for each standard level. Table
V.15 through Table V.17 show the
rebuttable presumption payback periods
that are less than 3 years. For gas-fired
and electric storage water heaters and
gas wall gravity DHE and gas room DHE,
there were no payback periods under 3
years.
While DOE examined the rebuttablepresumption criterion, it considered
whether the standard levels considered
for today’s rule are economically
justified through a more detailed
analysis of the economic impacts of
these levels pursuant to 42 U.S.C.
6295(o)(2)(B)(i). The results of this
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20:45 Dec 10, 2009
Jkt 220001
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).
TABLE V.15—WATER HEATERS:
REBUTTABLE PAYBACK PERIODS
Product class
Oil-Fired Storage ......
Gas-Fired Instantaneous ....................
Energy
factor
PBP
(years)
0.54
0.56
0.58
0.60
0.62
0.66
0.68
1.0
0.7
0.9
0.5
0.7
1.4
1.3
0.69
0.9
TABLE V.16—DIRECT HEATING EQUIPMENT: REBUTTABLE PAYBACK PERIODS
Product class
Gas Wall Fan DHE ...
Gas Hearth DHE ......
AFUE
%
PBP
(years)
75
76
67
2.9
2.9
2.0
TABLE V.17—POOL HEATERS:
REBUTTABLE PAYBACK PERIODS
below depict the financial impacts on
manufacturers (represented by changes
in INPV) and the conversion costs DOE
estimates manufacturers would incur at
each TSL. DOE shows the results by
grouping product classes made by the
same manufacturer and uses the
scenarios that show the likely changes
in industry value following amended
energy conservation standards. In the
following discussion, the INPV results
refer the difference in industry value
between the base case and the standards
case that result from the sum of
discounted cash flows from the base
year (2010) through the end of the
analysis period. The results also discuss
the difference in cash flow between the
base case and the standards case in the
year before the compliance date of
amended energy conservation
standards. This figure gives a
representation of how large the required
conversion costs are relative to the cash
flow generated by the industry in the
absence of amended energy
conservation standards. In the
engineering analysis, DOE presents its
findings of the common technology
options that achieve the efficiencies for
each of the representative product
classes. To refer to the description of
technology options and the required
efficiencies at each TSL, see section
IV.C of today’s notice.
a. Water Heater Cash-Flow Analysis
Results
Thermal efficiency
PBP
%
years
DOE modeled two different markup
scenarios to estimate the potential
79 ......................................
1.1 impacts of amended energy
81 ......................................
1.9
conservation standards on residential
water heater manufacturers. To assess
2. Economic Impacts on Manufacturers
the lower end of the range of potential
DOE performed an MIA to estimate
impacts on water heater manufacturers,
the impact of amended energy
DOE modeled the preservation of return
conservation standards on
on invested capital scenario. Besides the
manufacturers of residential water
impact of the main NIA shipment
heaters, DHE, and pool heaters. Chapter scenario and the required capital and
12 of the NOPR TSD explains this
product conversion costs on INPV, this
analysis in further detail. The tables
case models that manufacturers would
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maintain the base-case return on
invested capital in the standards case.
This scenario represents the lower end
of the range of potential impacts on
manufacturers because manufacturers
generate a historical rate of additional
operating profit on the physical and
financial investments required by
energy conservation standards.
To assess the higher end of the range
of potential impacts on the residential
water heater industry, DOE modeled the
preservation of operating profit markup
scenario in which higher energy
conservation standards result in lower
manufacturer markups. This scenario
models manufacturers’ concerns about
the higher costs of more efficient
technology harming profitability. The
scenario represents the upper end of the
range of potential impacts on
manufacturers only because no
additional operating profit is earned on
the investments required the meet the
amended energy conservation
standards. The results of these scenarios
for the residential water heater industry
are presented in Table V.18 through
Table V.23.
i. Cash-Flow Analysis Results for GasFired and Electric Storage Water Heaters
TABLE V.18—MANUFACTURER IMPACT ANALYSIS FOR GAS-FIRED AND ELECTRIC STORAGE WATER HEATERS—
PRESERVATION OF RETURN ON INVESTED CAPITAL MARKUP SCENARIO
INPV ..........................
Change in INPV ........
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
Trial standard level
Base
case
1
2
3
4
5
6
(2008$ millions) ........
(2008$ millions) ........
(%) ............................
(2008$ millions) ........
842.7
................
................
................
838.9
(3.8)
¥0.45%
11.0
837.7
(5.1)
¥0.60%
13.2
837.8
(4.9)
¥0.59%
13.2
839.2
(3.5)
¥0.41%
13.2
821.8
(20.9)
¥2.48%
28.9
840.7
(2.0)
¥0.24%
55.7
905.7
62.9
7.47%
72.6
(2008$ millions) ........
................
0.0
3.9
3.9
37.1
58.0
69.3
189.2
(2008$ millions) ........
................
11.0
17.0
17.0
50.3
86.9
125.0
261.8
Units
7
TABLE V.19—MANUFACTURER IMPACT ANALYSIS FOR GAS-FIRED AND ELECTRIC STORAGE WATER HEATERS—
PRESERVATION OF OPERATING PROFIT MARKUP SCENARIO
INPV ..........................
Change in INPV ........
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
1
2
3
4
5
6
7
(2008$ millions) ........
(2008$ millions) ........
(%) ............................
(2008$ millions) ........
842.7
................
................
................
830.4
(12.3)
¥1.46%
11.0
812.0
(30.7)
¥3.64%
13.2
807.4
(35.3)
¥4.19%
13.2
$763.9
(78.8)
¥9.35%
13.2
712.8
(129.9)
¥15.41%
28.9
$536.9
(305.8)
¥36.29%
55.7
$305.1
(537.6)
¥63.79%
72.6
(2008$ millions) ........
................
0.0
3.9
3.9
37.1
58.0
69.3
189.2
(2008$ millions) ........
................
11.0
17.0
17.0
50.3
86.9
125.0
261.8
TSL 1 represents an improvement in
efficiency from the baseline level of 0.59
EF to 0.62 EF for gas-fired storage water
heaters for the representative rated
storage volume of 40 gallons. For
electric storage water heaters TSL 1
represents an improvement in efficiency
from the baseline level of 0.90 EF to
0.92 EF for the representative rated
storage volume of 50 gallons. At TSL 1,
DOE estimates the impacts on INPV to
range from ¥$3.8 million to ¥$12.3
million, or a change in INPV of ¥0.45
percent to ¥1.46 percent. At this level,
the industry cash flow is estimated to
decrease by approximately 4.8 percent,
to $58.1 million, compared to the basecase value of $61.0 million in the year
leading up to the standards. Currently,
over 75 percent of the gas-fired storage
water heaters are sold at the baseline
level. However, all manufacturers also
offer a full line of gas-fired storage water
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case
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heaters that meet the gas-fired
efficiencies at TSL 1. Although the
majority of the electric storage water
heater shipments do not meet TSL 1,
every manufacturer also offers a full line
of electric storage water heaters at or
above this level. Because manufacturers
have existing products and
manufacturers could reach the required
efficiencies with relatively minor
changes to the foam insulation thickness
at TSL 1, manufacturers of gas-fired and
electric storage water heaters would
have minimal conversion costs at TSL 1.
Because the technology required at TSL
1 is similar to the baseline, the INPV
impacts are similar for both markup
scenarios. It is hence unlikely that TSL
1 would greatly reduce manufacturers’
profitability.
TSL 2 represents an improvement in
efficiency from the baseline level of 0.59
EF to 0.63 EF for gas-fired storage water
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heaters for the representative rated
storage volume of 40 gallons. For
electric storage water heaters, TSL 2
represents an improvement in efficiency
from the baseline level of 0.90 EF to
0.93 EF for the representative rated
storage volume of 50 gallons. At TSL 2,
DOE estimates the impacts on INPV to
range from ¥$5.1 million to ¥$30.7
million, or a change in INPV of ¥0.60
percent to ¥3.64 percent. At this level,
the industry cash flow is estimated to
decrease by approximately 8.7 percent,
to $55.7 million, compared to the basecase value of $61.0 million in the year
leading up to the standards. Currently,
over 80 percent of the gas-fired storage
water heaters sold do not meet TSL 2.
At TSL 2, manufacturers are expected to
meet the gas-fired efficiency
requirements by adding additional
insulation to their existing products.
The conversion costs at TSL 2 are
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relatively minor for gas-fired storage
water heaters because most
manufacturers have a full line of
products at the required efficiency for
TSL 2 and only minor changes in the
manufacturing process would be
required. Although the majority of the
electric storage water heater market is
below the efficiency specified for
electric storage water heaters at TSL 2,
more than 28 percent of the market is
at or above this level. Manufacturers
would have increasing conversion costs
for both capital and product conversion
for electric storage water heaters to
modify production facilities to
accommodate the extra insulation
required at TSL 2. Because the
technology required at TSL 2 is similar
to the baseline for gas-fired and electric
storage water heaters, however, it is
unlikely that TSL 2 would greatly
impact manufacturers’ profitability.
Similar to TSL 2, TSL 3 represents an
improvement in efficiency from the
baseline level of 0.59 EF to 0.63 EF for
gas-fired storage water heaters for the
representative rated storage volume of
40 gallons. Because the efficiency
requirements for gas-fired storage water
heaters are the same at TSL 3 as at TSL
2, the impacts on manufacturers are the
same as at TSL 2 for the gas-fired storage
efficiency requirements. There are small
impacts on manufacturers to improve
the efficiency of the majority of the gasfired storage shipments from the
baseline. However, because these
changes are expected to be relatively
minor increases to the insulation
thickness, the impacts on the industry
are not substantial because these
changes do not greatly alter the current
manufacturing process. TSL 3
represents a further improvement in
efficiency for electric storage water
heaters from the baseline level of 0.90
EF to 0.94 EF for the representative
rated storage volume of 50 gallons. To
achieve the efficiency levels for TSL 3,
electric storage manufacturers would be
expected to further increase tank
insulation thickness, with still relatively
small conversion costs because many
manufacturers already manufacture
storage water heaters at TSL 3. DOE
estimates the INPV impacts to range
from ¥$4.9 million to ¥$35.3 million,
or a change in INPV of ¥0.59 percent
to ¥4.19 percent. At this level, the
industry cash flow is estimated to
decrease by approximately 8.7 percent
to $55.7 million, compared to the basecase value of $61.0 million in the year
leading up to the standards.
Similar to TSL 2 and TSL 3, TSL 4
represents an improvement in efficiency
from the baseline level of 0.59 EF to
0.63 EF for gas-fired storage water
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heaters for the representative rated
storage volume of 40 gallons. Because
the efficiency requirements for gas-fired
storage water heaters are the same at
TSL 4 as at TSL 2 and TSL 3, the
impacts on gas-fired manufacturers are
the same. There are small impacts on
manufacturers to improve the efficiency
of the majority of the gas-fired storage
shipments from the baseline. However,
because these changes are expected to
be relatively minor increases to the
insulation thickness, the impacts on the
industry are not substantial because
these changes do not greatly alter the
current manufacturing process. TSL 4
represents a further improvement in
efficiency from the baseline level of 0.90
EF to 0.95 EF for electric storage water
heaters at the representative rated
storage volume of 50 gallons. Based on
a review of units on the market at these
efficiency levels, DOE expects that
manufacturers would likely further
increase insulation levels. Because not
all manufacturers have models at this
efficiency currently available on the
market, however, DOE expects that
electric storage water heater
manufacturers would incur higher
conversion costs at TSL 4 than at TSL
3. At TSL 4, DOE estimates the INPV
impacts to range from ¥$3.5 million to
¥$78.8 million, or a change in INPV of
¥0.41 percent to ¥9.35 percent. At this
level, the industry cash flow is
estimated to decrease by approximately
33.2 percent to $40.8 million, compared
to the base-case value of $61.0 million
in the year leading up to the standards.
Only a small number of electric storage
water heaters on the market meet the
efficiency level for electric storage water
heaters required by TSL 4. Electric
storage manufacturers would have
increasing conversion costs for both
capital and product conversion to
greatly increase the production of low
volume products. The capital
conversion costs for electric storage
water heaters are more substantial than
for gas-fired storage water heaters
because each production line would
require additional foaming stations to
accommodate the greatly increased
insulation thicknesses and, due to
slower production speeds, adding
additional production lines in existing
facilities to maintain current shipment
volumes. Manufacturers also noted that
they were concerned about TSL 4 for
electric storage water heaters because of
problems with the test procedure that
could make it difficult replicate the
efficiencies required at this TSL.
TSL 5 has the same efficiency
requirements as TSL 4 for gas-fired and
electric storage water heaters with rated
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storage volumes less than 55 gallons.
Because the efficiency requirements for
gas-fired and electric storage water
heaters with rated storage volumes less
than 55 gallons are equal to TSL 4, at
TSL 5 manufacturers share the same
concerns for these rated storage volumes
as at TSL 4. However, the efficiency
requirements for gas-fired storage water
heaters with rated storage volumes
greater than 55 gallons effectively
require condensing technology, and the
efficiency requirements for electric
storage water heaters with rated storage
volumes greater than 55 gallons
effectively require heat pump
technology. At TSL 5, DOE estimates the
INPV impacts to range from ¥$20.9
million to ¥$129.9 million, or a change
in INPV of ¥2.48 percent to ¥15.41
percent. At this level, the industry cash
flow is estimated to decrease by
approximately 55.6 percent to $27.1
million, compared to the base-case
value of $61.0 million in the year
leading up to the standards. The higher,
negative impacts on INPV are largely
caused by the additional conversion
costs required to substantially change
the technology commonly used in large
size gas-fired and electric storage water
heaters today. DOE estimates the
approximately 4 percent of gas-fired
storage water heater shipments with
rated volumes greater than 55 gallons
would require an additional $13 million
in conversion costs to use condensing
technology. DOE estimates the
approximately 9 percent of gas-fired
storage water heater shipments with
rated volumes greater than 55 gallons
would require an additional $24 million
in conversion costs to use heat pump
technology.
Much of the additional capital
conversion costs calculated for large
volume sizes at TSL 5 involve creating
an additional gas-fired and electric
assembly line in a facility adjacent to a
current production facility. Because
high-volume manufacturing facilities
are typically arranged for units with
similar assembly processes, the more
complex technology used for larger
rated volumes at TSL 5 could not be
accommodated on existing production
lines. The estimated product conversion
costs at TSL 5 would involve retraining
existing service and installation
personnel, who have little experience
installing and servicing storage water
heaters that use these advanced
technologies. To minimize unit damage
and warranty claims and improve
market acceptance, manufacturers
would likely have to expend significant
additional resources to hire training
staff to provide more technical support.
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The other portion of the product
conversion costs for large rated volumes
are the product development effort to
redesign existing products.
Manufacturers could face constraints
regarding the abilities of their
engineering teams to develop multiple
water heater families at TSL 5, as most
engineering departments have limited
experience with either technology. At a
minimum, the efficiency requirements
at TSL 5 would require manufacturers to
convert existing commercial condensing
gas products for residential use.
However, multiple manufacturers
would also have to develop completely
new platforms in order to remain costcompetitive. Even if a manufacturer
were to offer incur these high
conversion costs, the high product
development and capital conversion
costs for a small segment of the overall
market make it likely that consumers
will have fewer product families to
choose from after the compliance date of
the final rule.
Even if manufacturers offer gas
condensing and electric heat pump
water heaters for the large gallon sizes
at TSL 5, there could be additional,
negative impacts on consumers that
could lead to a smaller market for these
products. Consumers might no longer
purchase water heaters with rated
storage volumes above 55 gallons
because of substantially higher
increased first costs than most products
currently on the market, the unfamiliar
technologies, and size limitations.
Because of these changes in the market,
at TSL 5, manufacturers could decide
that the demand for residential heat
pump and condensing gas water heaters
would drop to a point where the high
product conversion and capital costs
required for a small portion of total
shipments are not justified. As a result,
manufacturers would no longer
manufacture residential storage water
heaters at rated storage volumes above
55 gallons. In addition, consumers
could be impacted if fewer contractors
were willing to install these more
complex products, especially if field
technicians did not obtain any
additional licenses and test equipment
that could be required to service heat
pump water heaters. These additional
requirements would also likely increase
installation and service costs beyond
current levels since consumers would
have fewer servicers/installers to choose
from.
Similar to TSL 2 through TSL 4,
TSL 6 represents an improvement in
efficiency from the baseline level of 0.59
EF to 0.63 EF for gas-fired storage water
heaters for the representative rated
storage volume of 40 gallons. Similarly,
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the impacts on manufacturers due to the
gas-fired storage efficiencies are
relatively minor because the required
efficiencies for all volume sizes can
likely be met with relatively minor
changes to the insulation thickness. For
electric storage water heaters, TSL 6
represents an improvement in efficiency
from the baseline level of 0.90 EF to
2.0 EF for electric storage water heaters
at the representative rated storage
volume of 50 gallons. At TSL 6, DOE
estimates the impacts on INPV to range
from ¥$2.0 million to ¥$305.8 million,
or a change in INPV of ¥0.24 percent
to ¥36.29 percent. At TSL 6, the
industry cash flow is estimated to
decrease by approximately 75.7 percent,
to $14.8 million, compared to the basecase value of $61.0 million in the year
leading up to the standards. To achieve
efficiencies at or above TSL 6 would
require the use of heat pumps for
electric storage water heaters for all
rated volumes, a technology option that
has yet to see wide adoption in the U.S.
market. The higher expected purchased
part content and market pressures
would be expected to reduce
manufacturer profits margins
substantially. Although most electric
storage water heater manufacturers
indicated that they are in the process of
developing heat pump water heaters, all
manufacturers believe that an efficiency
level that requires heat pump water
heater technology is not appropriate as
an amended energy conservation
standard. Manufacturers stated that they
would face substantial costs to switch
their entire electric storage water heater
production over to heat pump electric
storage water heaters. Several
manufacturers expect that they will
have to buy the heat pump modules
from outside vendors since most water
heater manufacturers have no
experience manufacturing heat pumps
and have limited space in their facilities
to produce heat pump systems. Multiple
manufacturers stated that even if they
were to simply buy and integrate heat
pump modules, there would be
substantial product development and
capital conversion costs because present
facilities are not adequate to handle the
heat pump modules. DOE estimates that
manufacturers would incur almost $70
million in capital conversion costs to
modify production facilities to
exclusively manufacture heat pump
electric storage water heaters. These
capital conversion cost estimates do not
include the cost of building
manufacturing capacity to produce the
heat pump modules because DOE
believes manufacturers will likely
purchase these as subassemblies.
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Furthermore, manufacturers stated
that they would consider moving all or
part of their existing production
capacity abroad if the energy
conservation standard is set at TSL 6
because many manufacturers expect that
they would have to redesign their
facilities completely to accommodate a
minimum energy conservation standard
at this TSL. According to these
manufacturers, building a new facility
entails less business disruption risk
than attempting to completely redesign
and upgrade existing facilities, and
lower labor rates in Mexico and other
countries abroad may entice
manufacturers to move their production
facilities outside of the U.S. In addition,
manufacturers are very concerned about
the significant number of customers
who would face extremely costly
installations for electric storage water
heater replacements if a standard
effectively requiring heat pump
technology is mandated. According to
manufacturers, a significant percentage
of electric storage water heaters are
installed in space-constrained
environments which cannot
accommodate the additional space
required for the heat pump module.
This is especially true for mobile homes
and other consumer sub-groups that use
smaller capacity tanks.
Another concern of manufacturers at
TSL 6 is the amount of additional
training that would be necessary to
upgrade the installation, distribution,
and maintenance networks on the scale
necessary to support an electric storage
water heater market that used heat
pump technology exclusively. Stated
more simply, manufacturers are
concerned that the typical installer or
repair person would not have the
requisite knowledge to troubleshoot or
repair heat pump water heaters.
Manufacturers also expressed concern
about profitability if amendments to the
minimum energy conservation standard
for electric storage water heaters were to
require the use of heat pump
technology. An amended energy
conservation standard that effectively
mandated heat pump technology would
completely change the nature of their
business. The production costs for an
integrated heat pump water heater at the
50-gallon representative rated storage
volume are approximately four times
the baseline production costs.
Specifically, manufacturers believe that
because this technology results in much
more expensive units than the majority
of products on the market today, not all
of the increased costs could be passed
on to the customer. In addition, the
significantly higher production costs
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would require an additional $256
million in working capital to purchase
significantly more expensive
components, carry more costly
inventory, and handle higher accounts
receivable. DOE estimates that the
working capital requirement and
conversion costs would cause electric
storage water heater manufacturers to
incur a total one-time investment of at
least $375 million in an electric storage
market valued at approximately $311
million. Finally, manufacturers believe
it is unlikely that they could earn the
same return on these extremely large
investments, so profitability would be
expected to decrease after the
compliance date of the amended energy
conservation standards.
TSL 7 represents an improvement in
efficiency from the baseline level of
0.59 EF to 0.80 EF for gas-fired storage
water heaters for the representative
rated storage volume of 40 gallons. TSL
7 represents an improvement in
efficiency from the baseline level of 0.90
EF to 2.2 EF for electric storage water
heaters at the representative rated
storage volume of 50 gallons. At TSL 7,
DOE estimates the impacts on INPV to
range from $62.9 million to ¥$537.6
million, or a change in INPV of 7.47
percent to ¥63.79 percent. At TSL 7,
the industry cash flow is estimated to
decrease by approximately 171.6
percent, to ¥$43.7 million, compared to
the base-case value of $61.0 million in
the year leading up to the standards.
Because TSL 7 also requires improved
heat pump technology (with additional
efficiency-related improvements to both
the heat pump module and the water
heater tank), electric storage water
heater manufacturers shared the same
concerns at TSL 7 as they had at TSL
6. Because additional, more-costly
improvements to heat pump technology
are required, however, electric storage
water heater manufacturers were more
concerned about the potential for energy
conservation standards to greatly
disrupt the industry if the amended
energy conservation standard were set at
TSL 7.
For gas-fired storage water heaters,
TSL 7 requires manufacturers to
produce fully-condensing gas-fired
storage water heaters, which is
significantly more complex than the
insulation changes required at most
lower TSLs. Currently, no manufacturer
offers residential gas-fired storage water
heaters with condensing technology.
Manufacturers would need to redesign
their products at the condensing level,
which would force manufacturers to
incur significant product and capital
conversion costs. Some loss in product
utility may also occur for units that are
presently installed in space-constrained
applications because condensing water
heaters require greater installation space
to accommodate bigger heat exchangers,
fully-installed blowers, and other
components that non-condensing
models do not feature. At the
condensing level, manufacturers would
be required to purchase substantial
tooling to fabricate new coil and tank
designs and make changes to all
subassembly and main assembly lines.
DOE estimates that manufacturers
would incur approximately $111
million in capital conversion costs to
modify their production facilities. Some
gas-fired storage water heater
manufacturers stated during interviews
that they would consider moving
facilities offshore at TSL 7 to take
advantage of lower labor costs. In
addition, due to the complexity and
large size of storage water heaters at this
efficiency, manufacturers are concerned
that installations will be far more
difficult and could force many
consumers to pay substantially higher
installed costs if their replacement
water heater does not fit into their
existing space. Manufacturers are also
concerned about profitability if
standards were set at a level that would
effectively require condensing
technology. An amended energy
conservation standard that effectively
mandated condensing gas-fired storage
water heaters would completely change
the existing structure of the industry.
Because this technology results in much
more expensive units than the majority
of products on the market today,
manufacturers argued that not all of the
increased costs could be passed on to
the customer. In addition, the
significantly higher production costs
would require at least an additional
$145 million in working capital to
purchase significantly more expensive
components, carry more costly
inventory, and handle higher accounts
receivable. DOE estimates that the
working capital requirement and
conversion costs would cause gas-fired
storage water heater manufacturers to
incur a total one-time investment of at
least $276 million in a gas-fired storage
market valued at approximately $532
million. While there is a slightly
positive impact if manufacturers get the
same return on these investments as in
the base case, manufacturers believe
that they will not earn the same return
from the substantially higher capital
requirements at TSL 7.
ii. Cash-Flow Analysis Results for OilFired Storage Water Heaters
TABLE V.20—MANUFACTURER IMPACT ANALYSIS FOR OIL-FIRED STORAGE WATER HEATERS—PRESERVATION OF RETURN
ON INVESTED CAPITAL MARKUP SCENARIO
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
INPV ..........................
Change in INPV ........
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
VerDate Nov<24>2008
Trial standard level
Base
case
1
2
3
4
5
6
7
(2008$ millions) ........
(2008$ millions) ........
(%) ............................
(2008$ millions) ........
8.7
................
................
................
8.5
(0.2)
¥1.93%
0.3
8.5
(0.2)
¥1.78%
0.3
8.5
(0.2)
¥1.96%
0.3
8.5
(0.2)
¥1.96%
0.3
8.5
(0.2)
¥1.96%
0.3
8.5
(0.2)
¥1.96%
0.3
7.4
(1.3)
¥14.84%
1.0
(2008$ millions) ........
................
0.2
0.2
0.2
0.2
0.2
0.2
3.6
(2008$ millions) ........
................
0.5
0.5
0.5
0.5
0.5
0.5
4.6
Units
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TABLE V.21—MANUFACTURER IMPACT ANALYSIS FOR OIL-FIRED STORAGE WATER HEATERS—PRESERVATION OF
OPERATING PROFIT MARKUP SCENARIO
INPV ..........................
Change in INPV ........
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
1
2
3
4
5
6
7
(2008$ millions) ........
(2008$ millions) ........
(%) ............................
(2008$ millions) ........
8.7
................
................
................
8.3
(0.3)
¥3.89%
0.3
8.4
(0.3)
¥3.58%
0.3
8.3
(0.4)
¥4.31%
0.3
8.3
(0.4)
¥4.31%
0.3
8.3
(0.4)
¥4.31%
0.3
8.3
(0.4)
¥4.31%
0.3
5.2
(3.5)
¥39.86%
1.0
(2008$ millions) ........
................
0.2
0.2
0.2
0.2
0.2
0.2
3.6
(2008$ millions) ........
................
0.5
0.5
0.5
0.5
0.5
0.5
4.6
TSL 1 represents an improvement in
efficiency for oil-fired storage water
heaters from the baseline level of 0.53
EF to 0.58 EF for the representative
rated storage volume of 32 gallons. At
TSL 1, DOE estimates the impacts on
INPV to range from ¥$0.2 to ¥$0.3
million, or a change in INPV of ¥1.93
percent to ¥3.89 percent. At this level,
the industry cash flow would be
expected to decrease by approximately
28.5 percent, to $0.4 million, compared
to the base-case value of $0.6 million in
the year leading up to the standards. At
TSL 1, one of the two major
manufacturers would have to incur
relatively small product and capital
conversion costs to slightly modify their
existing product line. DOE research
suggests that this TSL can be met with
changes to the insulation thickness of
baseline products. However, if more
costly design changes were required it
could have more of an impact on the
industry.
TSL 2 represents an improvement in
efficiency from the baseline level of 0.53
EF to 0.60 EF for the representative
rated storage volume of 32 gallons. At
TSL 2, DOE estimates the impacts on
INPV to range from ¥$0.2 million to
¥$0.3 million, or a change in INPV of
¥1.78 percent to ¥3.58 percent. At this
level, the industry cash flow is
estimated to decrease by approximately
28.5 percent, to $0.4 million, compared
to the base-case value of $0.6 million in
the year leading up to the standards.
Similar to TSL 1, at TSL 2 DOE has
tentatively concluded, based on a
review of existing products on the
market, that TSL 2 could be met with
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Trial standard level
Base
case
Units
changes to the type and thickness of the
insulation. The impacts at TSL 1 are
slightly worse than at TSL 2 because the
technology option for existing oil-fired
storage water heaters on the market
results in lower product costs at TSL 2.
However, if TSL 2 is met with similar
insulation changes, only one of two
major manufacturers would still be
required to slightly modify their current
residential oil-fired storage product
lines at TSL 2.
TSLs 3 through TSL 6 represent an
improvement in efficiency from the
baseline level of 0.53 EF to 0.62 EF for
the representative rated storage volume
of 32 gallons. At these levels, DOE
estimates the impacts on INPV to range
from ¥$0.2 million to ¥$0.4 million, or
a change in INPV of ¥1.96 percent to
¥4.31 percent. At this level, the
industry cash flow decreases by
approximately 28.5 percent, to $0.4
million, compared to the base-case
value of $0.6 million in the year leading
up to the standards. At these TSLs, one
major manufacturer would have to incur
relatively minor product and capital
conversion costs to modify their existing
oil-fired residential storage water heater
product line. DOE has tentatively
concluded based on a review of existing
products on the market that the
efficiency requirements at TSL 3
through TSL 6 could be met with
changes to the type and thickness of the
insulation. Due to the low volume of oilfired storage water heaters, if any
manufacturer had to make substantial
product or capital conversion costs to
reach the amended energy conservation
standard using a more complex
technology, these substantial costs
could force them to consider exiting the
residential oil-fired storage water heater
market.
TSL 7 (the max-tech level) represents
an improvement in efficiency from the
baseline level of 0.53 EF to 0.68 EF for
the representative rated storage volume
of 32 gallons. At TSL 7, DOE estimates
the impacts on INPV to range from
¥$1.3 million to ¥$3.5 million, or a
change in INPV of ¥14.84 percent to
¥39.86 percent. At this level, the
industry cash flow is estimated to
decrease by approximately 342.5
percent, to ¥$1.3 million, compared to
the base-case value of $0.6 million in
the year leading up to the standards. At
TSL 7, at least one major manufacturer
would have to incur very substantial
product and capital conversion to
redesign the combustion and baffling
system to include a multi flue design.
Given the small size of the residential
oil-fired storage water heater market,
this manufacturer stated that these
extremely large substantial product and
capital conversion costs would be
difficult to justify. At TSL 7, it is
possible that this manufacturer would
exit the residential oil-fired storage
water heater market. Because there are
only two main manufacturers that
supply the vast majority of U.S.
shipments of oil-fired storage water
heaters, any manufacturer exiting the
market could lead to a market
disruption.
iii. Cash-Flow Analysis Results for GasFired Instantaneous Water Heaters
TABLE V.22—MANUFACTURER IMPACT ANALYSIS FOR GAS-FIRED INSTANTANEOUS WATER HEATERS—PRESERVATION OF
RETURN ON INVESTED CAPITAL MARKUP SCENARIO
Trial standard level
Units
Base case
1
INPV ..................
Change in INPV
VerDate Nov<24>2008
(2008$ millions)
(2008$ millions)
20:45 Dec 10, 2009
603.5
..................
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2
3
4
5
6
7
604.7
1.2
604.7
1.2
604.7
1.2
604.7
1.2
604.7
1.2
604.7
1.2
683.8
80.3
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TABLE V.22—MANUFACTURER IMPACT ANALYSIS FOR GAS-FIRED INSTANTANEOUS WATER HEATERS—PRESERVATION OF
RETURN ON INVESTED CAPITAL MARKUP SCENARIO—Continued
Trial standard level
Units
Base case
1
Product Conversion Costs.
Capital Conversion Costs.
Total Investment
Required.
2
3
4
5
6
7
(%) ....................
(2008$ millions)
..................
..................
0.20%
0.0
0.20%
0.0
0.20%
0.0
0.20%
0.0
0.20%
0.0
0.20%
0.0
13.31%
8.0
(2008$ millions)
..................
0.0
0.00
0.00
0.0
0.0
0.0
9.6
(2008$ millions)
..................
0.0
0.0
0.0
0.0
0.0
0.0
17.6
TABLE V.23—MANUFACTURER IMPACT ANALYSIS FOR GAS-FIRED INSTANTANEOUS STORAGE WATER HEATERS—
PRESERVATION OF OPERATING PROFIT MARKUP SCENARIO
Trial standard level
Units
Base case
1
INPV ..................
Change in INPV
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Product Conversion Costs.
Capital Conversion Costs.
Total Investment
Required.
3
4
5
6
7
(2008$ millions)
(2008$ millions)
(%) ....................
(2008$ millions)
603.5
..................
..................
..................
601.7
(1.8)
¥0.30%
0.0
601.7
(1.8)
¥0.30%
0.0
601.7
(1.8)
¥0.30%
0.0
601.7
(1.8)
¥0.30%
0.0
601.7
(1.8)
¥0.30%
0.0
601.7
(1.8)
¥0.30%
0.0
537.6
(65.9)
¥10.91%
8.0
(2008$ millions)
..................
0.0
0.0
0.0
0.0
0.0
0.0
9.6
(2008$ millions)
..................
0.0
0.0
0.0
0.0
0.0
0.0
17.6
TSL 1 through TSL 6 represent an
improvement in efficiency from the
baseline gas-fired instantaneous water
heater efficiency level of 0.62 EF to 0.82
EF for the representative input capacity
of 199 kBtu/h. At TSL 1 through TSL 6,
DOE estimates the INPV impacts to
range from $1.2 million to ¥$1.8
million, or a change in INPV of 0.20
percent to ¥0.30 percent. At this level,
the industry cash flow is estimated to
remain at the base-case value of $75.0
million in the year leading up to the
standards. DOE research suggests that
over 80 percent of gas-fired
instantaneous products sold today meet
or exceed this efficiency, and nearly all
manufacturers of gas-fired instantaneous
water heaters currently make products
that meet or exceed the efficiency
required by TSL 1 through TSL 6.
Hence, there appears to be little risk that
TSL 1 through TSL 6 would greatly
harm manufacturers or reduce the
number of manufacturers that sell these
products.
TSL 7 (the max-tech level) represents
an improvement in efficiency from the
baseline level of 0.62 EF to 0.95 EF for
the representative input capacity of 199
kBtu/h. At TSL 7, DOE estimates the
INPV impacts to range from $80.3
million to ¥$65.9 million, or a change
in INPV of 13.31 percent to ¥10.91
percent. At this level, the industry cash
flows are estimated to decrease by
approximately 5.9 percent to $70.5
VerDate Nov<24>2008
2
20:45 Dec 10, 2009
Jkt 220001
million, compared to the base-case
value of $75.0 million in the year
leading up to the standards. Only one
manufacturer currently offers a gas-fired
instantaneous water heater that meets
the max-tech efficiency on the U.S.
market. Most manufacturers would
incur substantial product conversion
and capital conversion costs to upgrade
their existing products at TSL 7. To
reach 0.95 EF, a more complex
condensing model would need to be
developed. Because only one
manufacturer offers products that meet
this efficiency, TSL 7 could greatly
reduce the number of gas-fired
instantaneous water heaters offered for
sale in the United States.
b. Direct Heating Equipment Cash-Flow
Analysis Results
Traditional DHE manufacturers are
extremely concerned about the potential
for amended energy conservation
standards to harm their business. The
vast majority of the traditional DHE
market is controlled by three
manufacturers. The small shipment
volume of products in the traditional
market has greatly reduced the number
of competitors in the past decade. The
traditional DHE market is mostly a
replacement market met by these three
companies that have acquired product
lines as competitors were bought and
absorbed or exited the market. Most
DHE manufacturers offer a wide scope
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of products manufactured at low
production rates to ensure that they can
maintain a viable portion of the
replacement market in order to remain
in business. Because the traditional DHE
market consists of a large number of
relatively low-volume, mostly
replacement models, manufacturers
stated that they cannot justify large
investments needed to redesign their
existing product lines. Manufacturers
are concerned that amended energy
conservation standards could greatly
impact the availability of replacement
products for the majority of their
customers due to the limited resources
that would be available to update
existing products and make changes to
their existing facilities. In addition,
manufacturers were concerned that
energy conservation standards could
lower profitability at higher TSLs
because demand is expected to decline
in response to increases in first cost that
could cause consumers to switch to
other types of heating appliances.
Gas hearth manufacturers were also
concerned about potentially detrimental
impacts from amended energy
conservation standards. While there are
three major gas hearth DHE
manufacturers, DOE identified an
additional 12 manufacturers in the
market and technology assessment (see
chapter 3 of the TSD). Because
consumers generally are more interested
in the appearance of these products than
E:\FR\FM\11DEP2.SGM
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efficiency, every manufacturer typically
offers a wide range of product lines and
an even greater number of individual
products. Manufacturers are concerned
that higher energy conservation
standards could harm their business
because they do not have the resources
to upgrade all these existing product
lines and could be forced to offer fewer
products after the compliance date for
the amended energy conservation
standards. Manufacturers were also
concerned that higher price points
could lead to lower profitability.
Because of the large number of
manufacturers and the recent decline in
shipments, manufacturers were
concerned that additional production
costs could not be passed on to
consumers or that markups would be
lowered to avoid higher price points
leading to lower sales.
To assess the lower end of the range
of potential impacts of amended
standards on DHE manufacturers, DOE
modeled the industry assuming the
preservation of return on invested
capital scenario. Besides the impact of
shipments and the required capital and
product conversion costs on INPV, this
scenario assumes that manufacturers are
able to maintain their base-case return,
even on additional invested capital. In
this scenario, operating profit increases
after the compliance date of the
amended energy conservation standards
because manufacturers continue to earn
a historical rate of return on the
investments required by the amended
energy conservation standards.
To assess the higher end of the range
of potential impacts of amended
standards on the DHE industry, DOE
modeled the preservation of operating
profit markup scenario. In this scenario,
higher energy conservation standards
result in lower manufacturer percentage
markups. The preservation of operating
profit markup scenario models
manufacturers’ concerns about the low
volume of shipments and declining
profitability if higher energy
conservation standards were
implemented. The preservation of
operating profit scenario also models
gas hearth manufacturer concerns that
amended energy conservation standards
would impact profitability due to the
need to lower their markups to keep
customers from switching to noncovered hearth products if the energy
conservation standards significantly
raised the installed prices of covered
products. In the preservation of
operating profit scenario, manufacturer
markups decline and operating profit
remains the same after the compliance
date of the amended energy
conservation standards as in the base
case. Industry value is harmed because
manufacturers do not earn additional
return on the investments required by
the amended standards.
i. Cash-Flow Analysis Results for
Traditional Direct Heating Equipment
(Gas Wall Fan, Gas Wall Gravity, Gas
Floor, and Gas Room Direct Heating
Equipment)
TABLE V.24—MANUFACTURER IMPACT ANALYSIS FOR TRADITIONAL DIRECT HEATING EQUIPMENT—PRESERVATION OF
RETURN ON INVESTED CAPITAL MARKUP SCENARIO
Trial standard level
Units
Base case
1
INPV .............................
Change in INPV ...........
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
2
3
4
5
6
(2008$ millions) ...........
(2008$ millions) ...........
(%) ...............................
(2008$ millions) ...........
17.9
..................
..................
..................
17.5
(0.4)
¥2.27%
0.6
17.3
(0.6)
¥3.42%
1.0
16.9
(1.1)
¥5.91%
1.9
16.7
(1.3)
¥7.16%
2.4
16.2
(1.8)
¥9.99%
3.5
15.7
(2.2)
¥12.28%
4.3
(2008$ millions) ...........
..................
1.2
2.4
4.5
5.6
4.7
6.8
(2008$ millions) ...........
..................
1.84
3.40
6.39
7.98
8.14
11.03
TABLE V.25—MANUFACTURER IMPACT ANALYSIS FOR TRADITIONAL DIRECT HEATING EQUIPMENT—PRESERVATION OF
OPERATING PROFIT MARKUP SCENARIO
Trial standard level
Units
Base case
1
INPV .............................
Change in INPV ...........
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
3
4
5
6
(2008$ millions) ...........
(2008$ millions) ...........
(%) ...............................
(2008$ millions) ...........
17.9
..................
..................
..................
16.3
(1.6)
¥9.11%
0.6
14.9
(3.1)
¥17.20%
1.0
11.9
(6.0)
¥33.54%
1.9
10.4
(7.6)
¥42.14%
2.4
9.9
(8.0)
¥44.84%
3.5
7.2
(10.8)
¥59.98%
4.3
(2008$ millions) ...........
..................
1.2
2.4
4.5
5.6
4.7
6.8
(2008$ millions) ...........
..................
1.84
3.40
6.39
7.98
8.14
11.03
For traditional DHE, TSL 1 represents
an improvement in efficiency from the
baseline level of 74-percent AFUE to 75percent AFUE for gas wall fan DHE, an
improvement in efficiency from the
baseline level of 64-percent AFUE to 66percent for gas wall gravity DHE, an
improvement in efficiency from the
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baseline level of 57-percent AFUE to 58percent AFUE for gas floor DHE (the
max-tech level), and an improvement in
efficiency from the baseline level of 64percent AFUE to 66-percent AFUE for
gas room DHE at their respective
representative input rating ranges. DOE
research suggests that manufacturers
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would use an intermittent ignition and
a two-speed blower for gas wall fan DHE
and an improved heat exchanger design
for gas wall gravity, gas floor units, and
gas room DHE to achieve the efficiencies
required by TSL 1. At TSL 1, DOE
estimates the impacts on INPV to range
from $0.4 to ¥$1.6 million, or a change
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Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
in INPV of ¥2.27 percent to ¥9.11
percent. At this level, the industry cash
flow is estimated to decrease by
approximately 45.7 percent, to $0.8
million, compared to the base-case
value of $1.4 million in the year leading
up to the standards. While some
manufacturers may need to make
redesigns to some of their products even
at TSL 1, manufacturers generally have
a significant number of products that
meet the required efficiencies for most
traditional DHE product types, and for
this reason, a complete exit from the
market by any manufacturer is unlikely.
TSL 2 represents an improvement in
efficiency from the baseline level of 74percent AFUE to 76-percent for gas wall
fan DHE, an improvement in efficiency
from the baseline level of 64-percent
AFUE to 68-percent AFUE for gas wall
gravity DHE, an improvement in
efficiency from the baseline level of 57percent AFUE to 58-percent AFUE for
gas floor DHE (the max-tech level), and
an improvement in efficiency from the
baseline level of 64-percent AFUE to 67percent for gas room DHE at the
representative input rating ranges for
each product type. DOE research
suggests that at TSL 2, manufacturers
would opt to use an improved heat
exchanger and intermittent ignition for
gas wall fan DHE, and make further
improvements to the heat exchanger for
gas wall gravity and gas room DHE, and
use the same improved heat exchanger
for gas floor DHE as at TSL 1 to reach
the efficiency levels required by TSL 2.
At TSL 2, DOE estimates the impacts in
INPV to range from ¥$0.6 million to
¥$3.1 million, or a change in INPV of
¥3.42 percent to ¥17.20 percent. At
this level, the industry cash flow is
estimated to decrease by approximately
86.1 percent, to $0.2 million, compared
to the base-case value of $1.4 million in
the year leading up to the standards. At
TSL 2, every manufacturer would face
higher product development costs in
order to offer a similar range of product
offerings. However, at TSL 2, it is likely
that more products would be
discontinued because more of the
current products on the market fall
below the required efficiencies. As a
result, manufacturers must either
expend resources to cover the necessary
product conversion and capital
conversion costs, or they will be forced
to discontinue some of their existing
product lines. While TSL 2 would have
a significant impact on manufacturers,
most manufacturers would not be
expected to face a complete redesign for
most traditional DHE product types.
Even if manufacturers lowered the
number of product lines offered in
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20:45 Dec 10, 2009
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certain product classes, manufacturers
would have enough existing products
that meet or exceed the required
efficiencies to upgrade most of their
existing product lines and maintain
viable production volumes after the
compliance date of the amended energy
conservation standards.
TSL 3 represents an improvement in
efficiency from the baseline level of 74percent AFUE to 77-percent for gas wall
fan DHE, an improvement in efficiency
from the baseline level of 64-percent
AFUE to 71-percent AFUE for gas wall
gravity units, an improvement in
efficiency from the baseline level of 57percent AFUE to 58-percent AFUE for
gas floor DHE (the max-tech level), and
an improvement in efficiency from the
baseline level of 64-percent AFUE to 68percent for gas room DHE at the
representative input rating ranges. DOE
research suggests that manufacturers
would improve baseline units by adding
an intermittent ignition, a two-speed
blower, and an improved heat
exchanger for gas wall fan units, make
further improvements to the heat
exchanger used to reach TSL 2 for gas
wall gravity and gas room units, and use
the same improved heat exchanger for
gas floor DHE as at TSL 1 and TSL 2 to
reach the efficiency levels of TSL 3. At
TSL 3, DOE estimates the INPV impacts
to range from ¥$1.1 million to ¥$6.0
million, or a change in INPV of ¥5.91
percent to ¥33.54 percent. At this level,
the industry cash flow is estimated to
decrease by approximately 161.8
percent to ¥$0.9 million, compared to
the base-case value of 1.4 million in the
year leading up to the standards. The
large estimated impact on INPV suggests
that manufacturers would be
substantially harmed if profitability
were impacted.
At TSL 3, products increasingly rely
on purchased parts, making it more
likely that manufacturers’ profitability
would decline. At TSL 3, it is likely that
some manufacturers would reduce the
number of product lines offered in order
to lower the product conversion and
capital conversion costs required at TSL
3. Discontinuing product lines would
still have a negative impact on the
manufacturers that selectively upgrade
existing product lines since many
manufacturers rely on aggregated
production scale from all products they
sell to secure favorable purchased part
and raw material prices. The fixed
portion of product conversion costs,
such as certification and the total capital
conversion costs, typically require a
minimum shipment volume in order to
be economically justifiable to the
manufacturer. However, at TSL 3, most
manufacturers have existing products
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65943
that meet the required efficiencies in
three out of the four product types of
traditional DHE. Because manufacturers
have a substantial number of product
lines that meet the required efficiencies
at TSL3, even if manufacturers
selectively upgrade their existing
product lines, they would be expected
to maintain a viable production volume
after the compliance date of the
amended energy conservation and not
exit the market completely.
TSL 4 is the max-tech level for gas
wall fan DHE. TSL 4 represents an
improvement in efficiency from the
baseline level of 74-percent AFUE to 80percent for gas wall fan DHE at the
representative input rating range. The
efficiency requirements for gas wall
gravity, gas floor, and gas room DHE are
the same at TSL 4 as at TSL 3. To
achieve the max-tech level for gas wall
fan DHE, DOE research suggests that
manufacturers would need to use an
electronic ignition and induced draft.
DOE anticipates that manufacturers
would make the same improvements to
the heat exchangers as necessary to
achieve TSL 3 for gas wall gravity, gas
floor, and gas-room DHE. At TSL 4, DOE
estimates the INPV impacts to range
from ¥$1.3 million to ¥$7.6 million, or
a change in INPV of ¥7.16 percent to
¥42.14 percent. At this level, the
industry cash flow is estimated to
decrease by approximately 202.3
percent to ¥$1.4 million, compared to
the base-case value of $1.4 million in
the year leading up to the standards.
Most manufacturers’ products are
below the max-tech level for gas wall
fan DHE, which further increases the
total capital and product conversion
costs over TSL 3. At TSL 4, most
manufacturers would have to
completely redesign their gas wall fan
products and purchase new tooling. The
discrepancy between the number of unit
shipments and the number of product
lines requiring significant product
development to meet the potential
energy conservation standards is a large
driver of the negative impacts at TSL 4.
When faced with these substantial costs,
most manufacturers would likely
discontinue products in this product
class or possibly exit the market
altogether. In addition, at TSL 4 every
manufacturer would face significant
conversion costs in every product type,
making it much more likely that the
industry would offer far fewer products
and that the industry would have fewer
competitors after the compliance date of
amended standards. Besides the
likelihood of multiple manufacturers
discontinuing product lines or exiting
the market, the large impact on INPV
shows that manufacturers would also be
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Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
substantially harmed if profitability
were impacted for existing or
redesigned products.
TSL 5 represents an improvement in
efficiency from the baseline level of 74percent AFUE to 75-percent AFUE for
gas wall fan DHE, an improvement in
efficiency from the baseline level of 64percent AFUE to 72-percent AFUE for
gas wall gravity units (the max-tech
level), an improvement in efficiency
from the baseline level of 57-percent
AFUE to 58-percent AFUE for gas floor
DHE (the max-tech level), and an
improvement in efficiency from the
baseline level of 64-percent AFUE to 83percent AFUE (the max-tech level) for
gas room DHE at the representative
input rating ranges for each product
type. To achieve the efficiencies
required by TSL 5, DOE research
suggests that manufacturers would need
to use an intermittent ignition and a
two-speed blower for gas wall fan DHE,
use an electronic ignition for gas wall
gravity DHE, use an improved heat
exchanger for gas floor DHE, and use
electronic ignition and a multiple heat
exchanger design for gas room DHE. At
TSL 5, DOE estimates the impacts on
INPV to range from ¥$1.8 million to
¥$8.0 million, or a change in INPV of
¥9.99 percent to ¥44.84 percent. At
this level, the industry cash flow is
estimated to decrease by approximately
195.5 percent, to ¥$1.3 million,
compared to the base-case value of $1.4
million in the year leading up to the
standards.
Most traditional DHE models
available on the market today are below
the max-tech level for gas wall gravity
and gas room DHE, which leads to
higher total capital and product
conversion costs and more negative
impacts on INPV at TSL 5 than TSL 4.
DOE research suggests that at TSL 5,
most manufacturers would have to
completely redesign and buy new
tooling in order to offer gas wall gravity
and gas room products at these
efficiency levels. The small number of
unit shipments and the large number of
product lines that would require
significant product development to meet
the energy conservation standards is a
large driver of the negative impacts at
TSL 5. Hence, the potential number of
product lines being discontinued and
the number of manufacturers exiting the
market at TSL 5 would be expected to
be greater than at TSL 4, with even
greater repercussions on consumer
choice, employment, and competition.
TSL 6 is set at the max-tech level for
all traditional DHE product classes. The
efficiency requirements for gas wall
gravity, gas floor, and gas room DHE are
the same at TSL 6 as at TSL 5. However,
TSL 6 also represents an improvement
from 75-percent to 80-percent AFUE for
gas wall fan DHE (the max-tech level).
To achieve the max-tech level for gas
wall fan DHE, DOE research suggests
that manufacturers would need to use
an electronic ignition and induced draft.
As to the other products, DOE
anticipates that manufacturers would
need to use an electronic ignition for gas
wall gravity DHE, use an improved heat
exchanger for gas floor DHE, and use
electronic ignition and a multiple heat
exchanger design for gas room DHE. At
the max-tech TSL (TSL 6), DOE
estimates the INPV impacts to range
from ¥$2.2 million to ¥$10.8 million,
or a change in INPV of ¥12.28 percent
to ¥59.98. At this level, the industry
cash flow is estimated to decrease by
approximately 269.5 percent to ¥$2.4
million, compared to the base-case
value of $1.4 million in the year leading
up to the standards. Most products
currently available are below the maxtech level for all product classes. At the
max-tech level, most manufacturers
would be faced with complete product
redesigns for almost all product lines
and significant plant changes to remain
in the market. Most manufacturers
would be expected to discontinue
products or exit the market altogether.
Due to the low volume of shipments in
the industry, it unlikely that any
manufacturer could offer close to the
range of products currently offered
today. Hence, some product classes may
cease to be commercially available. It is
very likely that multiple manufacturers
would exit the market at the max-tech
level for every product class.
ii. Cash-Flow Analysis Results for Gas
Hearth Direct Heating Equipment
TABLE V.26—MANUFACTURER IMPACT ANALYSIS FOR GAS HEARTH DIRECT HEATING EQUIPMENT—PRESERVATION OF
RETURN ON INVESTED CAPITAL MARKUP SCENARIO
Trial standard level
Units
Base case
1
INPV .............................
Change in INPV ...........
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
2
3
4
5
6
(2008$ millions) ...........
(2008$ millions) ...........
(%) ...............................
(2008$ millions) ...........
86.4
..................
..................
..................
85.5
(0.9)
¥1.07%
0.53
85.5
(0.9)
¥1.07%
0.53
85.5
(0.9)
¥1.07%
0.53
88.8
2.4
2.80%
1.40
88.8
2.4
2.80%
1.40
96.6
10.2
11.82%
8.07
(2008$ millions) ...........
..................
0.20
0.20
0.20
0.53
0.53
4.03
(2008$ millions) ...........
..................
0.73
0.73
0.73
1.93
1.93
12.09
TABLE V.27—MANUFACTURER IMPACT ANALYSIS FOR GAS HEARTH DIRECT HEATING EQUIPMENT—PRESERVATION OF
OPERATING PROFIT MARKUP SCENARIO
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Trial standard level
Units
Base case
1
INPV .............................
Change in INPV ...........
Product Conversion
Costs.
Capital Conversion
Costs.
VerDate Nov<24>2008
2
3
4
5
6
(2008$ millions) ...........
(2008$ millions) ...........
(%) ...............................
(2008$ millions) ...........
86.4
..................
..................
..................
86.2
(0.2)
¥0.22%
0.53
86.2
(0.2)
¥0.22%
0.53
86.2
(0.2)
¥0.22%
0.53
71.6
(14.8)
¥17.13%
1.40
71.6
(14.8)
¥17.13%
1.40
31.2
(55.1)
¥63.83%
8.07
(2008$ millions) ...........
..................
0.20
0.20
0.20
0.53
0.53
4.03
20:45 Dec 10, 2009
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TABLE V.27—MANUFACTURER IMPACT ANALYSIS FOR GAS HEARTH DIRECT HEATING EQUIPMENT—PRESERVATION OF
OPERATING PROFIT MARKUP SCENARIO—Continued
Trial standard level
Units
Base case
1
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Total Investment Required.
(2008$ millions) ...........
TSL 1 through TSL 3 represents an
improvement in efficiency from the
baseline level of 64-percent AFUE to 67percent AFUE for gas hearth DHE at the
27,000 Btu/h to 46,000 Btu/h
representative input rating range. To
reach 67-percent AFUE from baseline
efficiency, manufacturers would likely
use an electronic ignition. At TSL 1
through TSL 3, DOE estimates the
impacts on INPV to range from ¥$0.2
million to ¥$0.9 million, or a change in
INPV of ¥0.22 percent to ¥1.07
percent. At this level, the industry cash
flow is estimated to decrease by
approximately 7.6 percent, to $2.6
million, compared to the base-case
value of $2.8 million in the year leading
up to the standards. Most manufacturers
offer multiple products that meet this
efficiency level. Because there are so
many product lines at the baseline
efficiency, however, there could be
fairly substantial product conversion
costs at this TSL because manufacturers
would have to slightly redesign all of
the baseline products. In addition, some
manufacturers could be required to
make other minor changes to their
production lines to accommodate other
improvements such as additional
baffling. DOE research suggests that
such changes may be inexpensive since
they would not require the industry to
replace major hard tooling at TSL 1
through TSL 3. Because of the small
change in product costs at TSL 1
through TSL 3, it is unlikely that
manufacturer profitability would
decrease appreciably to maintain the
existing shipments.
TSL 4 and TSL 5 represent an
improvement in efficiency from the
baseline level of 64-percent AFUE to 72percent AFUE for gas hearth DHE at the
27,000 Btu/h to 46,000 Btu/h
representative input rating range. DOE
research suggests that fan-assisted gas
hearth DHE products could reach 72percent AFUE from baseline efficiency.
At TSL 4 and TSL 5, DOE estimates the
impacts on INPV to range from $2.4
million to ¥$14.8 million, or a change
in INPV of 2.80 percent to ¥17.13
percent. At this level, the industry cash
flow is estimated to decrease by
approximately 19.9 percent, to $2.3
million, compared to the base-case
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2
0.73
3
0.73
value of $2.8 million in the year leading
up to the standards. At TSL 4 and TSL
5, gas hearth manufacturers would
likely reduce the scope of their product
offerings to lower the required
conversion costs to comply with the
energy conservation standard. Many of
the smaller manufacturers could
consider existing the market when faced
with fairly substantial product and
capital conversion costs that are not
justified by their shipment volumes.
Much of the capital conversion costs are
expected to involve changes to handle
new materials like additional insulation
and baffling, changes to the heat shields,
and new stamping dies for many
manufacturers that need to greatly alter
their existing designs. Manufacturers
will also incur additional product
conversion costs for product
development and certification because
most products currently sold would not
meet the efficiency requirements of TSL
4 and TSL 5. While most of the changes
above the baseline require
manufacturers to purchase or
manufacture more costly components
that increase MPC, the resulting higher
MSPs also concerned manufacturers.
Manufacturers stated that the market is
very price sensitive, so any increase in
unit price could invariably lead to fewer
sales. Hence, manufacturers expect that
the industry would have to lower its
profit margins in order to reduce
shipments impacts that could result
from cost increases related to potential
energy efficiency improvements.
TSL 6 represents an improvement in
efficiency from the baseline level of 64percent AFUE to 93-percent AFUE for
gas hearth DHE at the 27,000 Btu/h to
46,000 Btu/h representative input rating
range. To reach 93-percent AFUE from
the baseline efficiency, manufacturers
would need to use a condensing design.
At the max-tech TSL (TSL 6), DOE
estimates the impacts on INPV to range
from $10.2 million to ¥$55.1 million,
or a change in INPV of 11.82 percent to
¥63.83 percent. At this level, the
industry cash flow is estimated to
decrease by approximately 128.8
percent, to ¥$0.8 million, compared to
the base-case value of $2.8 million in
the year leading up to the standards.
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0.73
5
1.93
6
1.93
12.09
At TSL 6, manufacturers indicated
they would greatly reduce the scope of
their product offerings to lower the
required costs to comply with an
amended energy conservation standard
at this level. Because there are very few
products on the market today that use
this technology, the product
development costs greatly increase at
this TSL. DOE research suggests that
manufacturers would likely need a
secondary heat exchanger at the maxtech level, which could alter the size
and structure of most existing product
lines. Manufacturers expressed concern
regarding their ability to use existing
tooling and equipment, much of which
may become obsolete when hearths
have to be redesigned from the ground
up to accommodate the efficiency
requirements at this level. It is also very
likely that many of the 10 small
business manufacturers could be forced
to exit the market when faced with these
substantial conversion costs since they
do not have the access to capital, the
product development resources, or the
shipment volumes to justify these
conversion costs.
Manufacturers also stated that they
were concerned about consumer utility
issues at TSL 6. Smaller units would
likely be significantly impacted at this
TSL because the low inherent interior
volume makes it much more difficult to
accommodate a secondary heat
exchanger without narrowing the area
available for the logs and flame.
Manufacturers also indicated that it gets
progressively more difficult to imitate a
natural, wood-burning flame appearance
at this efficiency level, which could hurt
sales and reduce consumer utility.
Finally, manufacturers were concerned
that the MPCs at the max-tech level are
estimated to be more than double the
baseline costs for the representative
input rating range. In order to maintain
shipments of gas hearth DHE with
substantially higher costs and potential
consumer utility impacts, manufacturers
believe that profitability would be
greatly impacted.
c. Pool Heaters Cash-Flow Analysis
Results
Pool heater manufacturers expressed
concern that amended energy
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conservation standards could cause
significant harm to their industry,
because pool heaters are a luxury item
and have low annual usage that would
prevent the majority of consumers from
recouping the greater initial price at
higher efficiencies. Since pool heaters
are considered a luxury product,
manufacturers expect sales to decline as
unit costs increase. As the required
efficiencies approach a condensing
technology, manufacturers would have
to make more substantial changes to
their existing products that add
significant costs that would encourage
repair instead of replacement of failed
units, cause fuel switching (e.g., to heat
pumps or solar systems), or make
customers abandon heating their pool
altogether.
To assess the lower end of the range
of potential impacts on pool heater
manufacturers, DOE modeled the
preservation of return on invested
capital markup scenario. Besides the
impact of changes in shipments on
INPV and the required capital and
product conversion costs, this case
represents the lower end of the potential
impacts on manufacturers because it
assumes that manufacturers would earn
a similar return on the investments
required by amended energy
conservation standards. To assess the
higher end of the range of potential
impacts on pool heater manufacturers,
DOE modeled the preservation of
operating profit markup scenario (i.e.,
constant absolute profit, regardless of
cost increases, which leads to declining
profit margins at higher costs). This
scenario models manufacturers
concerns that margins would be harmed
at higher price points because they
expect to lower their profit margins to
minimize impacts due to lower sales.
TABLE V.28—MANUFACTURER IMPACT ANALYSIS FOR GAS-FIRED POOL HEATERS—PRESERVATION OF RETURN ON
INVESTED CAPITAL MARKUP SCENARIO
Trial standard level
Units
Base case
1
INPV .............................
Change in INPV ...........
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
2
3
4
5
6
(2008$ millions) ...........
(2008$ millions) ...........
(%) ...............................
(2008$ millions) ...........
61.4
..................
..................
..................
61.4
0.1
0.13%
0.0
61.8
0.4
0.66%
0.0
61.1
(0.2)
¥0.39%
2.6
61.9
0.5
0.88%
2.6
64.5
3.1
5.03%
4.6
74.2
12.9
20.96%
5.5
(2008$ millions) ...........
..................
0.0
0.3
1.2
1.4
4.4
7.1
(2008$ millions) ...........
..................
0.0
0.3
3.8
4.0
9.0
12.6
TABLE V.29—MANUFACTURER IMPACT ANALYSIS FOR GAS-FIRED POOL HEATERS—PRESERVATION OF OPERATING PROFIT
MARKUP SCENARIO
Trial standard level
Units
Base case
1
INPV .............................
Change in INPV ...........
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Product Conversion
Costs.
Capital Conversion
Costs.
Total Investment Required.
3
4
5
6
(2008$ millions) ...........
(2008$ millions) ...........
(%) ...............................
(2008$ millions) ...........
61.4
..................
..................
..................
61.2
(0.2)
¥0.29%
0.0
60.3
(1.0)
¥1.66%
0.0
55.8
(5.6)
¥9.06%
2.6
53.9
(7.5)
¥12.15%
2.6
41.8
(19.5)
¥31.82%
4.6
16.8
(44.5)
¥72.59%
5.5
(2008$ millions) ...........
..................
0.0
0.3
1.2
1.4
4.4
7.1
(2008$ millions) ...........
..................
0.0
0.3
3.8
4.0
9.0
12.6
TSL 1 represents an improvement in
efficiency from the baseline level of 78percent thermal efficiency to 81-percent
thermal efficiency for the representative
input rating of 250,000 Btu/h. At TSL 1,
DOE estimates the INPV impacts to
range from $0.1 million to ¥$0.2
million, or a change in INPV of 0.13
percent to ¥0.29 percent. At this level,
the industry cash flow would not be
expected to change from the base-case
value of $2.7 million in the year leading
up to the standards. Over 60 percent of
current gas-fired pool heaters meet or
exceed the efficiency requirements at
TSL 1. DOE research suggests that
changes to the heat exchanger would
allow baseline products to meet TSL 1.
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These changes would not require major
modifications to existing units, resulting
in minimal impacts to manufacturers at
TSL 1.
TSL 2 represents an improvement in
efficiency from the baseline level of 78percent thermal efficiency to 82-percent
thermal efficiency for the representative
input rating of 250,000 Btu/h. At TSL 2,
DOE estimates the INPV impacts to
range from $0.4 to ¥$1.0 million, or a
change in INPV of 0.66 percent to ¥1.66
percent. At this level, the industry cash
flow is expected to decrease by
approximately 3.9 percent to $2.6
million, compared to the base-case
value of $2.7 million in the year leading
up to the standards. Almost half of the
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pool heaters currently are sold at or
above this efficiency level, and nearly
all manufacturers make products that
can achieve the efficiency required at
TSL 2. DOE research suggests that minor
improvements to heat exchangers and
insulation surrounding the combustion
chamber would need to be made to
convert lower-efficiency units to this
efficiency, causing manufacturers to
incur small capital conversion costs.
However, because the basic designs of
atmospheric pool heaters that comprise
the majority of current shipments
remain relatively unchanged at TSL 2,
there are minimal impacts on
manufacturers.
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TSL 3 represents an improvement in
efficiency from the baseline level of 78percent thermal efficiency to 83-percent
thermal efficiency for the representative
input rating of 250,000 Btu/h. At TSL 3,
DOE estimates the INPV impacts to
range from ¥$0.2 to ¥$5.6 million, or
a change in INPV of ¥0.39 percent to
¥9.06 percent. At this level, the
industry cash flow is estimated to
decrease by approximately 43.0 percent
to $1.6 million, compared to the basecase value of $2.7 million in the year
leading up to the standards. DOE
research suggests that most
manufacturers would have to improve
some of their product lines to reach an
83-percent thermal efficiency by using
power venting technology. DOE
research also suggests that while the
manufacturing production costs are not
expected to increase significantly, most
manufacturers would incur some
product and capital conversion costs to
increase their production of existing
lower volume products at TSL 3. TSL 3
would eliminate most common
atmospheric models on the market
today, which could hurt profitability if
consumer demand for gas-fired pool
heaters holds at its current level despite
the higher production costs at this TSL.
TSL 4 represents an improvement in
efficiency from the baseline level of 78percent thermal efficiency to 84-percent
thermal efficiency for the representative
input rating of 250,000 Btu/h. At TSL 4,
DOE estimates the INPV impacts to
range from $0.5 million to ¥$7.5
million, or a change in INPV of 0.88
percent to ¥12.15 percent. At this level,
the industry cash flow is estimated to
decrease by approximately 45.9 percent
to $1.5 million, compared to the basecase value of $2.7 million in the year
leading up to the standards. Similar to
TSL 3, TSL 4 would require fairly
substantial capital and product
conversion costs. Because this efficiency
level eliminates all atmospheric models
that are currently on the market and
requires additional improvements over
TSL 3, the capital conversion costs are
even higher at TSL 4. DOE research
suggests that manufacturers would have
to design products that use power
venting and an improved heat
exchanger, which could be costly to
develop. Manufacturers stated that the
high component costs at TSL 4 would
result in substantially higher costs for
consumers. The higher production costs
and conversion costs make it more
likely that manufacturers’ concerns
about reduced profitability would be
realized at TSL 4.
TSL 5 represents an improvement in
efficiency from the baseline level of 78percent thermal efficiency to 86-percent
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thermal efficiency for the representative
input rating of 250,000 Btu/h. At TSL 5,
DOE estimates the INPV impacts to
range from $3.1 million to ¥$19.5
million, or a change in INPV of 5.03
percent to ¥31.82 percent. At this level,
the industry cash flow is estimated to
decrease by approximately 108.9
percent to ¥$0.2 million, compared to
the base-case value of $2.7 million in
the year leading up to the standards.
Over 90 percent of current shipments
are below this efficiency level.
Manufacturers would incur significant
conversion costs at TSL 5 and would
likely significantly reduce the scope of
their product offerings. DOE research
suggests that manufacturers would
switch remaining units to sealed
combustion systems and improved heat
exchanger designs, adding substantial
production cost and eliminating
unpowered units from the market.
Manufacturers believe that consumers
would look for alternatives to gas-fired
pool heaters or not replace failed units
due to the higher product costs that
would result from an amended energy
conservation standard at TSL 5.
Manufacturers also indicated that
problems at efficiencies they consider
near-condensing could force some
companies to only offer fully
condensing units with even greater
negative paybacks for consumers. A
further concern of manufacturers relates
to the current installer and maintenance
base for pool heaters, which would
require significant additional training to
be able to properly install, troubleshoot,
and service increasingly complex pool
heaters.
TSL 6 (max-tech level) represents an
improvement in efficiency from the
baseline level of 78-percent thermal
efficiency to 95-percent thermal
efficiency for the representative input
rating of 250,000 Btu/h. At TSL 6, DOE
estimates the INPV impacts to range
from $12.9 million to ¥$44.5 million,
or a change in INPV of 20.96 percent to
¥72.59 percent. At this level, the
industry cash flow is estimated to
decrease by approximately 157.2
percent to ¥$1.6 million, compared to
the base-case value of $2.7 million in
the year leading up to the standards.
Almost all gas-fired pool heaters
currently on the market are well below
this efficiency level. Manufacturers
would face significant conversion costs
at TSL 6 in order to develop condensing
systems or refine existing designs to
achieve lower cost condensing pool
heaters. DOE research suggests that heat
exchanger materials would need to
withstand acidic condensate created by
condensing pool heaters. In light of
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strong concerns about consumer
reaction to a substantially-increased first
cost at TSL 6, manufacturers do not
believe this efficiency level could be
justified for residential pool heater
consumers due to low usage and
significantly higher costs.
Manufacturers believe that consumers
would not be willing to purchase such
an expensive product and would either
find an alternative to gas-fired pool
heaters or no longer purchase a gas-fired
pool heater. In addition, at TSL 6
manufacturers are also concerned about
the industry’s ability to educate and
retrain installers and servicers of pool
heaters in time for the compliance date
of the standard. Condensing units with
sealed combustion are more complex
than the vast majority of atmospheric
units on the market today and would
require significant additional training
for safe installation and maintenance.
Manufacturers also expect product
support costs to increase significantly as
complexity increases the likelihood and
frequency of events such as component
failures and unit lockouts that would
require manufacturer support and
servicing, as well as increased warranty
costs. Besides increasing warranty costs
for manufacturers, the issues and costs
associated with proper unit
maintenance post-warranty could
potentially cause them to switch fuel
sources (e.g., switching to heat pump or
solar water heaters) or abandon pool
heating altogether.
d. Impacts on Employment
DOE quantitatively assessed the
impacts of potential amended energy
conservation standards on employment
for each of the three types of heating
products that are the subject of this
rulemaking. DOE used the GRIM to
estimate the domestic labor
expenditures and number of domestic
production workers in the base case and
at each TSL from 2008 to 2045 for the
residential water heater industry and
from 2008 to 2043 for the DHE and pool
heater industries. DOE used statistical
data from the U.S. Census Bureau, 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 are a
function of the labor intensity of the
equipment, the sales volume, and an
assumption that wages remain fixed in
real terms over time.
In each GRIM, DOE used the labor
content of each product and the
manufacturing production costs from
the engineering analysis to estimate the
annual labor expenditures in the
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residential water heater, DHE, and pool
heater industries. DOE used Census data
and interviews with manufacturers to
estimate the portion of the total labor
expenditures that is for U.S. (i.e.,
domestic) labor.
The estimates of production workers
in this section only cover workers up to
the line-supervisor level that are
directly involved in fabricating and
assembling a product within the
Original Equipment Manufacturer
(OEM) facility. Workers that perform
services that are closely associated with
production operations, such as material
handing with a forklift, are also
included as production labor. DOE’s
estimates only account for production
workers that manufacture the specific
products covered by this rulemaking.
For example, a worker on a commercial
water heater line would not be included
with the estimate of the number of
residential water heater production
workers.
The employment impacts shown in
Table V.30 through Table V.34 represent
the potential production employment
that could result following amended
energy conservation standards. The
upper end of the results in these tables
estimates the maximum potential
increase in production workers after
amended energy conservation
standards. The upper end of the results
assumes manufacturers would continue
to produce the same scope of covered
products in the same production
facilities. The upper end of the range
also assumes that domestic production
is not shifted to lower-labor-cost
countries. Because there is a real risk of
manufacturers exiting the market or no
longer offering the same scope of
covered products in response to
amended energy conservation
standards, the lower end of the range of
employment results in Table V.30
through Table V.34 include the estimate
of the total number of U.S. production
workers in the industry that could lose
their job if all existing production were
to no longer be made domestically.
While the results present a range of
employment impacts following the
compliance date of amended energy
conservation standards, the discussion
below also includes a qualitative
discussion of the likelihood of negative
employment impacts at the various
TSLs. Finally, the employment impacts
shown are independent of the
employment impacts from the broader
U.S. economy, which are documented
in chapter 15, Employment Impact
Analysis, of the NOPR TSD.
i. Gas-Fired and Electric Storage Water
Heater Employment Impacts
Using the GRIM, DOE estimates that
would be 3,690 domestic gas-fired and
electric storage water heater production
workers in 2015 without amended
energy conservation standards. Using
Census Bureau data and interviews with
manufacturers, DOE estimates that
approximately two-thirds of gas-fired
and electric storage water heaters sold
in the United States are manufactured
domestically. Table V.30 shows the
range of the impacts of potential
amended energy conservation standards
on U.S. production workers in the gasfired and electric storage water heater
market.
TABLE V.30.—POTENTIAL CHANGES IN THE TOTAL NUMBER OF DOMESTIC GAS-FIRED AND ELECTRIC STORAGE WATER
HEATER PRODUCTION WORKERS IN 2015
Baseline
Total Number
of Domestic
Production
Workers in
2015 (without
changes in
production
locations) ..
Potential
Changes in
Domestic
Production
Workers in
2015 * ........
1
2
3
4
5
6
7
3,690
3,758
3,842
3,881
3,977
4,396
7.768
9,823
......................
(3,690)¥68
(3,690)¥152
(3,690)¥191
(3,690)¥287
(3,690)¥706
(3,690)¥4,078
(3,690)¥6,133
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
* DOE presents a range of potential employment impacts. Numbers in parentheses indicate negative numbers.
During manufacturer interviews, gasfired and electric storage water heater
manufacturers stated that they expect
employment levels to remain relatively
constant at TSL 1 through TSL 4. At
these TSLs, baseline gas-fired and
electric storage water heaters would be
improved by increasing the insulation
thickness around the tank. These
improvements would not greatly alter
the manufacturing process and are not
likely to significantly change
employment levels.
At TSL 5, domestic employment
would be likely to increase if
manufacturers built their dedicate heat
pump line for large rated storage
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volumes in the United States. However,
because the labor content to assemble
fully integrated heat pump water heaters
is much higher than most models
currently on the market, manufacturers
could also decide to build these lines in
existing overseas production facilities.
At TSL 5, the sourcing decisions would
also impact the likely employment
impacts. If manufacturers built a
dedicated condensing line for large
rated storage volumes in the United
States, domestic employment could
increase.
TSL 6 and TSL 7 could also impact
domestic gas-fired and electric storage
water heater employment. These TSLs
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effectively would require the use of
integrated heat pump water heater
technology for electric storage water
heaters for all rate volumes.
Manufacturers stated that at these
levels, they initially would expect to
purchase fully-assembled heat pump
modules from off-shore suppliers
because they do not have the
manufacturing experience or the space
in their existing facilities to
accommodate assembling the heat hump
modules. Once purchased,
manufacturers would attach the
modules to water heaters on lines
modified to accommodate the very
different assembly and testing
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requirements of heat pump water
heaters. While the industry typically has
manufacturing facilities with a mix of
dedicated and non-dedicated assembly
lines by fuel type, flexible assembly
lines may have to be discontinued at
TSL 6, because heat pump water heaters
are top-heavy, take longer to test, and
take significantly longer to assemble
than electric storage water heaters that
use resistance-heater elements. Present
facilities would likely need line
extensions to accommodate the
additional labor required for assembling
heat pump water heaters. Therefore, if
manufacturers source the heat pump
modules and continue to assemble
electric storage water heaters in their
existing facilities, it is likely that
employment would increase. However,
the expected increase in the labor
required to manufacture heat pump
water heaters may also accelerate the
trend of water heater manufacturers
locating new production facilities
outside the United States, especially if
a manufacturer decides to assemble heat
pump modules in-house. Because TSL 7
requires additional improvements over
TSL 6, the potential positive impacts on
employment at TSL 7 are greater if
manufacturers do not relocate because
the additional improvements also
require more labor.
At TSL 7 (the max-tech level) gasfired storage water heaters would have
to operate in a fully-condensing mode.
DOE research suggests that condensing
gas-fired water heaters would be more
complex than standard power-vent
products and less efficient products and
therefore would require additional labor
to assemble. If manufacturers did not
change their sourcing decisions at TSL
7, it is likely there would be positive
employment impacts for gas-fired
storage water heaters.
ii. Oil-Fired Storage Water Heater
Employment Impacts
Using the GRIM, DOE estimates there
would be 38 oil-fired storage water
heater production workers in the U.S. in
2015 in the absence of amended energy
conservation standards. Using the
Census data and interviews with
manufacturers, DOE estimates that
approximately 95 percent of oil-fired
water heaters sold in the United States
are manufactured domestically. Table
V.31 shows the impacts of amended
energy conservation standards on U.S.
production workers in the oil-fired
water heater market.
TABLE V.31—POTENTIAL CHANGES IN THE TOTAL NUMBER OF DOMESTIC OIL-FIRED STORAGE WATER HEATER
PRODUCTION WORKERS IN 2015
Trial standard level
Baseline
Total Number of Domestic Production Workers in 2015 (without
changes in production locations)
Potential Changes in Domestic Production Workers in 2015 * ............
1
2
3
4
5
6
7
38
37
40
37
37
37
37
47
..................
(38)¥(1)
(38)¥2
(38)¥(1)
(38)¥(1)
(38)¥(1)
(38)¥(1)
(38)¥9
*DOE presents a range of potential employment impacts. Numbers in parentheses indicate negative numbers.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
At TSL 1 through TSL 6, DOE does
not expect substantial changes to
domestic employment in the oil-fired
storage water heater market if
manufacturers are able to use the
insulation type and thickness
technology options in the engineering
analysis to reach the efficiency
requirements at these TSLs. At TSL 7,
DOE research suggests that if all current
suppliers continue to compete, domestic
employment would likely increase
slightly, because the non-proprietary,
higher-efficiency heat exchangers
required to reach this TSL would also
require more labor to assemble.
However, given the size of the oil-fired
storage water heater market and the
expected product conversion costs,
companies that do not currently make
oil-fired storage water heaters at these
efficiency levels could exit the market.
If the remaining manufacturers do not
need to increase employment levels to
meet the total market demand,
employment in the residential oil-fired
market could decline.
iii. Gas-Fired Instantaneous Water
Heater Employment Impacts
DOE’s research suggests that currently
no gas-fired instantaneous water heaters
are made domestically. All
manufacturers or their domestic
distributors do maintain offices in the
United States to handle technical
support, training, certification, and
other requirements. However, as
amended energy conservation standards
for instantaneous water heaters are
raised, the additional complexity of
standards-compliant water heaters may
require additional training and field
support, thereby resulting in higher
employment levels. Thus domestic
employment may increase marginally
due to amended energy conservation
standards.
iv. Traditional Direct Heating
Equipment Employment Impacts
Using the GRIM, DOE estimates there
would be 300 traditional DHE
production workers in the U.S. in 2013
in the absence of amended energy
conservation standards. Using the
Census Bureau data and interviews with
manufacturers, DOE estimates that
approximately 100 percent of the
traditional DHE sold in the United
States is manufactured domestically.
Table V.32 shows the impacts of
amended energy conservation standards
on U.S. production workers in the
traditional DHE market.
TABLE V.32—POTENTIAL CHANGES IN THE TOTAL NUMBER OF DOMESTIC TRADITIONAL DIRECT HEATING PRODUCTION
WORKERS IN 2013
Trial standard level
Baseline
Total Number of Domestic Production Workers in
2013 (without changes in production locations)
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TABLE V.32—POTENTIAL CHANGES IN THE TOTAL NUMBER OF DOMESTIC TRADITIONAL DIRECT HEATING PRODUCTION
WORKERS IN 2013—Continued
Trial standard level
Baseline
Potential Changes in Domestic Production Workers in 2013 * .......................................................
1
..................
2
(300)¥5
3
4
5
6
(300)¥30
(300)¥44
(300)¥50
(300)¥48
(300)¥61
*DOE presents a range of potential employment impacts. Numbers in parentheses indicate negative numbers.
There could be negative employment
impacts for DHE at any of the
considered TSLs if manufacturers’
expectations are realized regarding
higher prices yielding reduced demand.
Besides increasing component costs,
more stringent TSLs put additional
pressure on manufacturers that could
require them to invest in low-volume
products, discontinue product lines that
do not meet the required efficiency
level, or exit the market altogether.
While multiple manufacturers could
be adversely affected by amended
energy conservation standards, at TSL 1
and TSL2, most businesses have
existing products in at least three of the
four traditional DHE product types. If
manufacturers chose to expand
production of those products that meet
the required efficiencies, employment
could increase. However, multiple small
businesses would be adversely affected
at any TSL and could decide to
discontinue some product lines rather
than invest in product lines with very
low volumes. Any manufacturer that
decided to discontinue product lines
could reduce total employment within
the industry if it impacted the
availability of substitute replacement
products. Net employment impacts if
manufacturers discontinued product
lines at TSL 1 and TSL 2 would depend
on total product demand and the source
of replacement production labor. At TSL
3 and above, products become
increasingly more complex, require
higher capital and product conversion
costs, and, hence, are likely to lead to
the discontinuation of more product
lines. Additionally, every manufacturer
would face product conversion costs
that required a complete redesign for at
least one product class at TSL 3 and
above. An amended energy conservation
standard at TSL 3 and above could
cause small businesses to exit the
market completely or stop producing
certain product classes. If small and
large manufacturers discontinued
product lines or exited the market,
domestic employment would be
impacted if replacements were not
available or a manufacturer exited the
market and its market share was not
captured by another manufacturer.
v. Gas Hearth Direct Heating Equipment
Employment Impacts
Using the GRIM, DOE estimates there
would be 1,243 gas hearth DHE
production workers in the U.S. in 2013
in the absence of amended energy
conservation standards. Based upon
interviews with manufacturers, DOE
estimates that approximately 80 percent
of gas hearth DHE sold in the United
States is manufactured domestically.
Table V.33 shows the impacts of
potential amended energy conservation
standards on U.S. production workers in
the gas hearth DHE market.
TABLE V.33—POTENTIAL CHANGES IN THE TOTAL NUMBER OF DOMESTIC GAS HEARTH DIRECT HEATING EQUIPMENT
PRODUCTION WORKERS IN 2013
Trial standard level
Baseline
Total Number of Domestic Production
Workers in 2013 (without changes in
production locations) ........................
Potential Changes in Domestic Production Workers in 2013 * ................
1
2
3
4
5
6
1,243
1,250
1,250
1,250
1,759
1,759
2,089
..................
(1,243)¥7
(1,243)¥7
(1,243)¥7
(1,243)¥516
(1,243)¥516
(1,243)¥846
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
* DOE presents a range of potential employment impacts. Numbers in parentheses indicate negative numbers.
DOE does not expect significant
employment impacts at TSL 1 through
TSL 3. A substantial portion of the
industry already has products that meet
the requisite efficiencies required by
these TSLs and DOE research suggests
manufacturers can make products at
these TSLs by replacing standing pilot
ignition systems with electronic ignition
systems. For TSL 4 through TSL 6,
manufacturers would be increasingly
likely to exit the market or reduce their
product offerings. At TSL 4 and TSL 5,
air circulating blowers are required and,
at TSL 6, condensing operation is
required, making these products
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increasingly complex. At these levels,
manufacturers suggested the size of the
gas hearth DHE market covered by
today’s rulemaking could be impacted
due possible consumer reactions, which
could also put additional pressure on
domestic firms to consolidate or exit the
market. A smaller market could reduce
employment if the higher labor content
required to manufacturer standardscompliant products is more than offset
by a decline industry sales.
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vi. Gas-Fired Pool Heater Employment
Impacts
Using the GRIM, DOE estimates there
would be 644 gas-fired pool heater
production workers in the U.S. in 2013
in the absence of amended energy
conservation standards. Using the
Census Bureau data and interviews with
manufacturers, DOE estimates that
approximately 100 percent of gas-fired
pool heaters sold in the United States
are manufactured domestically. Table
V.34 shows the impacts of potential
amended energy conservations
standards on U.S. production workers in
the gas-fired pool heater industry.
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TABLE V.34—POTENTIAL CHANGES IN THE TOTAL NUMBER OF DOMESTIC POOL HEATER PRODUCTION WORKERS IN 2013
Trial standard level
Baseline
Total Number of Domestic Production Workers in
2013 (without changes in production locations)
Potential Changes in Domestic Production Workers in 2013 * .......................................................
1
2
3
4
5
6
644
657
678
710
737
807
975
..................
(644)¥13
(644)¥34
(644)¥66
(644)¥93
(644)¥163
(644)¥331
* DOE presents a range of potential employment impacts. Numbers in parentheses indicate negative numbers.
DOE expects no significant direct
employment impacts on gas-fired pool
heater manufacturers for TSL 1 through
TSL 4 because the technology options at
these TSLs involve mostly component
changes that do not greatly alter the
labor content. For example, the
technology changes for existing
products that meet TSL 3 and TSL 4
involve power venting. While this
technology would alter the installation
of much of the installed base and cause
manufacturers to increase the
production of low-volume products, the
basic assembly of the pool heaters at the
point of manufacture is not substantially
changed. Therefore, it is unlikely that
employment levels would be
substantially impacted. However, the
existing products in the market at TSL
5 are near-condensing products and
products at TSL 6 use fully condensing
technology. The higher-efficiency
products are typically more complex
and take longer to assemble, resulting in
an increase in employment if shipments
levels are maintained. However,
manufacturers have stated that the
higher prices of higher-efficiency
products could result in a smaller
number of annual shipments, which
could cause a corresponding reduction
in industry employment as well. At TSL
5 and TSL 6, manufacturers are
particularly concerned that the closer
their products become to condensing
technology, the higher the product costs
would be and the more likely it is that
amended energy conservation standards
would cause a drop in industry-wide
shipments. If manufacturers
experienced a drop in total shipments,
the domestic employment in the gasfired pool heater industry could be
negatively affected.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
e. Impacts on Manufacturing Capacity
i. Residential Gas-Fired and Electric
Storage Water Heaters
Amended energy conservation
standards could cause short-term
capacity constraints for gas-fired storage
water heaters at TSL 7 and cause shortterm capacity constraints for electric
storage water heaters at TSL 6 and
TSL 7. However, for the remaining
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TSLs, manufacturers could maintain
capacity levels and continue to meet
market demand under amended energy
conservation standards.
DOE research suggests for the
efficiency requirements for gas-fired
storage water heaters could be met by
adding more foam insulation to all
volume sizes at TSL 1 through TSL 4
and TSL 6. These changes would not
require gas-fired storage water heater
manufacturers to greatly alter their
existing production facilities or
equipment and would not cause
capacity constraints. DOE also
acknowledges that TSL 5 could also
result in a constrained market for large
volume sizes if manufacturers do not
make the required investments to offer
gas-fired condensing water heaters at
relatively low shipment volumes. DOE
also recognizes there will likely be
significant impacts on manufacturers at
any TSL that effectively requires gasfired condensing.
The dramatically different technology
required at the max-tech level for gasfired storage water heaters introduces
problems that could cause short-term
capacity constraints in the market. At
TSL 7 (the max-tech level), all
manufacturers would need to redesign
all of their existing products because
none currently offers residential water
heaters that use condensing technology.
Manufacturers would also have to
retrain their installers and servicers to
handle technology that varies
tremendously from the majority of
exiting products on the market. The
fundamental fabrication and production
equipment of gas-fired storage water
heaters are substantially different for
water heaters that use condensing
technology. Equipment to manufacturer
required heat exchangers and new tank
designs would be required, as well as
substantial changes to all subassembly
and main assembly lines to handle the
new technology. DOE estimates that
manufacturers would incur over $110
million in capital conversion costs to
make these plant modifications if all
residential gas-fired storage water
heaters required condensing technology.
For comparison, the base-case estimate
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for the net PPE for gas-fired storage
water heaters is approximately $166
million. This comparison of the estimate
of current net PPE to the required
capital conversion costs indicates the
plant and equipment changes require
manufacturers to almost completely
modify or replace a substantial portion
of their existing production assets for
gas-fired storage water heaters. DOE also
estimates that these changes would
strand approximately $26 million of
existing assists, mainly the book value
of tank and coil equipment that can no
longer be used with condensing
technology. In addition, manufacturers
believe that there could be problems
with quality control to manufacture
substantially more complex products on
high-speed production lines. These
problems could further increase the
capital costs required if the line rates
required manufacturers to install
additional production lines.
Manufacturers indicated that these
potential problems and the extremely
substantial changes that are required to
their facilities could cause a constrained
market until the production equipment
is installed and the high-speed
manufacturing of what are currently
low-volume commercial products can
be expanded to meet the demand of the
gas-fired residential water heater
market. Although these changes are
substantial, DOE believes that the 5-year
period before compliance with the
standard is required would allow
manufacturers sufficient time to make
the necessary changes to meet demand
for those products. The full range of
products may not be available initially,
however, since manufacturers would
likely prioritize high-volume product
lines ahead of lower-volume product
lines.
For electric storage water heaters, TSL
1 through TSL 3 would require only
minor changes to existing products to
increase the tank insulation thickness.
At TSL 4, more substantial plant
modifications would be required
because changes to the insulation
thickness would require more foaming
stations and additional production lines
due to a lower throughput. However,
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electric storage water heater
manufacturers would be able to
maintain manufacturing capacity levels
and continue to meet market demand
under amended energy conservation
standards for these TSLs. These TSLs do
not require prohibitively costly or
complex changes to existing facilities or
most products on the market today.
DOE also acknowledges that TSL 5
could also result in a constrained
market for large volume sizes if
manufacturers do not make the required
investments to offer electric heat pump
water heaters at relatively low shipment
volumes. DOE also recognizes there will
likely be significant impacts on
manufacturers at any TSL that
effectively requires electric heat pump
water heaters.
Electric storage water heater
manufacturers indicated that there
could be potential capacity impacts at
TSL 6 or TSL 7, which would effectively
require heat pump technology.
However, manufacturers of electric
storage water heaters indicated that
significant changes to production
facilities would be required if amended
energy conservation standards
effectively mandated heat pump water
heaters for all rated volume sizes (TSL
6 and TSL 7). Several manufacturers
stated that they could move all or part
of their production to Mexico to take
advantage of lower labor costs if more
complex heat pump water heaters were
required. DOE believes manufacturers
would likely source the heat pump
module initially if they were required to
exclusively manufacture heat pump
water heaters. However, such a dramatic
increase in the demand for heat pump
modules could strain suppliers,
especially in the short-term. Finally,
manufacturers also stated that they have
very little experience with
manufacturing heat pump water heaters.
Manufacturers indicated that the
changes to their facilities (including
potential plant sourcing decisions)
could cause a constrained market until
the production equipment is installed
and any problems with high-speed
manufacturing are resolved. As
discussed in section IV.B.3.b, DOE
acknowledges there could be issues
with converting entire production lines
to manufacture heat pump water heaters
before the compliance date of this
standard. Given the five-year delay in
the compliance date with the amended
standard from the issuance from the
final rule, and the fact that many
manufacturers are already developing
heat pump water heaters, DOE believes
manufacturers may be able to convert all
their product lines before the
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compliance date of an amended energy
conservation standard.
ii. Residential Oil-Fired Storage Water
Heaters
While amended energy conservation
standards could impact current market
shares in the oil-fired storage water
heater market, it is unlikely that
standards would result in a constrained
market. For oil-fired storage water
heaters, the fundamental fabrication and
assembly equipment would not be
expected to change significantly in
order to comply with TSL 1 through
TSL 6. While DOE research suggests that
products that meet TSL 1 through TSL
6 require relatively minor changes to the
insulation material or thickness, the
product conversion costs necessary at
these TSLs could cause at least one
manufacturer with significant market
share to exit the residential oil-fired
storage water heater market due to the
low total shipment volumes. At any
efficiency level that would likely
require a multi-flue heat exchanger (i.e.,
TSL 7), all but one manufacturer would
need to make a significant and costly
redesign of existing residential oil-fired
product lines and related manufacturing
facilities. These substantial changes
could cause manufacturers to exit the
residential oil-fired storage water heater
market. However, even TSL 7 is
unlikely to result in a constrained
market even if any manufacturer exited
the oil-fired residential water heater
market. One residential oil-fired storage
water heater manufacturer with
significant market share has products
that meet the max-tech level. Due to the
low shipment volumes of oil-fired
storage water heaters, this manufacturer
could meet the total industry demand
and industry-wide capacity would not
be impacted.
iii. Gas-Fired Instantaneous Water
Heaters
There may be short-term capacity
constraints for gas-fired instantaneous
water heaters at TSL 7. DOE research
suggests that all gas-fired instantaneous
water heaters are currently imported. If
the amended energy conservation
standards required more-efficient
products than those currently offered,
foreign manufacturers and parent
companies would have to decide
whether the relatively small market for
gas-fired instantaneous water heaters in
the United States could justify the
required investments. DOE expects that
TSL 1 through TSL 6 would be unlikely
to disrupt supply to the United States
because of the number of existing
product lines that manufacturers could
offer without substantial product
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develop would not greatly change at the
required efficiencies. The number of
existing product lines on the market
drops substantially at TSL 7. There
could be capacity constraints in
response to amended energy
conservation standards at TSL 7 if
manufacturers that do not have
compliant products chose not to
develop them for the United States
market due to the current size of the
market.
iv. Traditional Direct Heating
Equipment
Amended energy conservation
standards could lead to a constrained
traditional DHE market. DOE does not
expect that traditional DHE
manufacturers would need to
substantially modify existing facilities
in response to amended energy
conservation standards at TSL 1 or TSL
2. However, at TSL 3 though TSL 6,
some manufacturers would face
complete product redesigns for either
gas wall fan or gas room DHE. A
complete redesign would entail
significant product development,
tooling, certification, and testing costs.
Some manufacturers indicated that low
shipment volumes would make these
costs unjustifiable for many product
lines, thereby leading to the
discontinuation of those lines. Small
businesses with less access to capital
would be even more likely to face this
problem than higher-volume, more
diversified competitors, possibly
resulting in further industry
consolidation. Pressure that forced
manufacturers to consolidate or exit the
market could also strain the remaining
manufacturers’ capacity to increase
production to meet industry demand.
However at TSL 3, DOE believes that
manufacturers have enough existing
products in multiple product classes
that they could selectively upgrade
enough product lines to meet industry
demand and remain in business.
However, DOE believes setting an
amended energy conservation standard
above TSL 3 could lead to
manufacturing capacity problems for
certain product classes if manufacturers
cannot make the tooling changes in time
to meet the standard, if manufacturers
do not have the resources to develop
products that meet the required
efficiencies, or if manufacturers
discontinue product lines rather than
invest an amount equal to the required
conversion costs.
v. Gas Hearth Direct Heating Equipment
Gas hearth DHE manufacturers did
not indicate that amended energy
conservation standards would lead to a
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constrained market. Rather, such
manufacturers are concerned that more
stringent energy conservation standards
could exert additional pressures on
companies to consolidate or exit the
market. Manufacturers predict that unit
shipments would decline increasingly
as the amended energy conservation
standard is set closer to max-tech (i.e.,
TSL 6). Manufacturers also indicated
that the high capital conversion costs
would lead all manufacturers to drop
product lines or not convert all existing
product lines at TSL 4 through TSL 6
because of the smaller market for
covered gas hearth products that is
anticipated in the event of a more
stringent amended energy conservation
standard. The reduction in market
demand and the lower number of
product lines available would likely
lead to an overcapacity of covered
products within the industry, even if
multiple lower-volume competitors exit
the market.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
vi. Gas-Fired Pool Heaters
Manufacturers indicated that, while
other potentially negative impacts were
possible at lower TSLs, industry
capacity could be impacted at more
stringent TSLs. At TSL 1 through TSL
4, DOE research suggests that
manufacturers could retool without
causing capacity constraints in the
market. If DOE were to set amended
energy conservation standards at nearcondensing or condensing level, most
gas-fired pool heater manufacturers
stated that short-term production
capacity could be affected. While only
TSL 6 requires fully-condensing
products, manufacturers indicated that
adoption of amended standards at TSL
5 and above could cause them to
manufacture only fully-condensing
products in order to minimize longevity
and warranty issues. Thus, TSL 5 and
TSL 6 would require manufacturers to
incur significant product and capital
conversion costs. Consequently, DOE
believes setting an amended energy
conservation standard at or above TSL
5 could lead to short-term capacity
problems if manufacturers cannot make
the necessary tooling, equipment, and
assembly changes in time to meet the
standard.
f. Cumulative Regulatory Burden
While any one regulation may not
impose a significant burden on
manufacturers, the combined effects of
several 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
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burden. In addition to energy
conservation standards, other
regulations can significantly affect
manufacturers’ financial operations.
Multiple regulations affecting the same
manufacturer can strain company-wide
resources and can 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 several
requirements, in addition to amended
energy conservation standards for the
three types of heating products that
manufacturers will face for products
manufactured three years before and
three years after the anticipated
compliance date of the amended energy
conservation standards.
During interviews and in their written
comments, manufacturers stated that the
most significant of these additional
regulations are regional ultra-low-NOX
requirements and environmental and
safety regulations. In response to the
preliminary analysis, BWC commented
that there is a substantial cost increase
to comply with ultra-low-NOX
requirements. (BWC, No. 46 at p. 1)
Noritz also stated that ultra-low-NOX
requirements are the most significant
regulation that will affect the gas-fired
instantaneous water heating industry
(Noritz, No. 36 at p. 3). AHRI and
Rheem stated that gas-fired
instantaneous water heater
manufacturers will have to comply with
ultra-low-NOX emissions requirements
in 2012. (AHRI, Public Meeting
Transcript, No. 34.4 at p. 134; Rheem,
No. 48 at p. 7)
Low and ultra-low-NOX regulations
for gas-fired water heaters are being
implemented regionally by air quality
management districts, including the
South Coast Air Quality Management
District (SCAQMD), the Bay Area Air
Quality Management District
(BAAQMD), the San Joaquin Valley
Unified Air Pollution Control District
(the Valley Air District), and the Texas
Commission on Environmental Equality
(TCEQ). The ultra-low-NOX regional
standards currently in place only cover
gas-fired storage water heaters, but
manufacturers are concerned that these
standards could eventually affect
additional types of gas-fired equipment.
While the SCAQMD, the BAAQMD, and
the Valley Air District all mandate ultralow-NOX requirements, the TCEQ only
has low-NOX requirements.
DOE accounted for the added cost for
manufacturers of gas-fired storage water
heaters to comply with regional ultra-
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low NOX requirements (see section
IV.C.2). DOE agrees with Noritz, AHRI,
and Rheem that ultra-low-NOX
requirements may affect instantaneous
gas water heaters beginning in 2012.
While the SCAQMD does not
distinguish between gas-fired storage
and gas-fired instantaneous water
heaters, the BAAQMD and the Valley
Air District have separate ultra-low-NOX
regulations for natural gas-fired
instantaneous water heaters. Although
the compliance dates of these
regulations are pending, DOE is not
aware of any ultra-low-NOX
instantaneous gas-fired water heaters
currently on the market. Consequently,
DOE could not create a separate cost
curve to account for the additional cost
of instantaneous water heaters that will
meet the upcoming ultra-low-NOX
emissions requirements.
There are also existing FVIR and low
and ultra-low-NOX requirements for gasfired storage water heaters, ignition
source requirements, amended energy
conservation standards for other
products made by heating products
manufacturers, State energy
conservation standards for other
products, and international energy
conservation standards. The cumulative
burden focuses on other productspecific Federal requirements with a
compliance date three years prior to and
three years after the anticipated
compliance dates of the amended
energy conservation standards of this
rulemaking. However, DOE discusses
these and other regulations and includes
the full details of the cumulative
regulatory burden in chapter 12 of the
NOPR TSD.
g. Impacts on Small Businesses
As discussed in section IV.H.1.c,
using average cost assumptions to
develop an industry cash-flow estimate
is not adequate for assessing differential
impacts among manufacturer subgroups.
Small manufacturers, niche equipment
manufacturers, and manufacturers
exhibiting a cost structure substantially
different from the industry average
could be affected disproportionately.
DOE used the results of the industry
characterization to group manufacturers
exhibiting similar characteristics.
Consequently, the only subgroup DOE
identified was small manufacturers.
DOE evaluated the impact of amended
energy conservation standards on small
manufacturers, as defined by SBA. As a
result, DOE identified five residential
water heater manufacturers, 12 DHE
manufacturers, and one small gas-fired
pool heater manufacturer that are
classified as small businesses per the
SBA definition. DOE describes the
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differential impacts on these small
businesses in section VI.B of today’s
notice. For a complete discussion of the
impacts on small businesses, see
chapter 12 of the NOPR TSD.
3. National Impact Analysis
(no standards) to anticipated energy
consumption of these products under
each TSL. Table V.35 through Table
V.37 present DOE’s NES estimates by
product type and class for each TSL.
Chapter 10 of the NOPR TSD describes
these estimates in more detail.
a. Significance of Energy Savings
To estimate the energy savings
attributable to potential standards, DOE
compared the energy consumption of
the heating products under the base case
TABLE V.35—WATER HEATERS: CUMULATIVE NATIONAL ENERGY SAVINGS IN QUADS
Product class
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
TSL 7
Gas-Fired Storage ...................................
Electric Storage ........................................
Oil-Fired Storage ......................................
Gas-Fired Instantaneous .........................
0.83
0.35
0.01
0.08
1.29
0.49
0.01
0.08
1.29
0.90
0.01
0.08
1.29
1.21
0.01
0.08
1.46
2.18
0.01
0.08
1.29
9.05
0.01
0.08
5.33
10.62
0.03
0.87
Total ..................................................
1.26
1.88
2.28
2.60
3.74
10.44
16.85
TABLE V.36—DIRECT HEATING EQUIPMENT: CUMULATIVE NATIONAL ENERGY SAVINGS IN QUADS
Product class
Gas
Gas
Gas
Gas
Gas
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
Wall Fan .......................................................
Wall Gravity ..................................................
Floor .............................................................
Room ............................................................
Hearth ...........................................................
0.007
0.008
0.0001
0.002
0.136
0.01
0.02
0.0001
0.00
0.14
0.01
0.06
0.0001
0.01
0.14
0.02
0.06
0.0001
0.01
0.30
0.01
0.10
0.0001
0.03
0.30
0.02
0.10
0.0001
0.03
0.93
Total ..............................................................
0.15
0.17
0.22
0.39
0.44
1.08
TABLE V.37—POOL HEATERS: CUMULATIVE NATIONAL ENERGY SAVINGS IN QUADS
TSL 1
Gas-Fired .........................................................................
b. Net Present Value of Consumer Costs
and Benefits
DOE estimated the cumulative NPV to
the Nation of total heating product
consumer costs and savings that would
result from particular standard levels. In
accordance with the OMB Circular A–4,
DOE calculated the NPV using both a
7-percent and a 3-percent real discount
rate. The 7-percent rate is an estimate of
the average before-tax rate of return to
private capital in the U.S. economy, and
reflects the returns to real estate and
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
0.02
0.03
0.08
0.10
0.13
0.28
value. This rate can be approximated by
the real rate of return on long-term
government debt (i.e., yield on Treasury
notes minus annual rate of change in the
Consumer Price Index), which has
averaged about 3 percent on a pre-tax
basis for the last 30 years.
Table V.38 through Table V.40 show
the consumer NPV results for each
TSL DOE considered for the three types
of heating products, using both a 7percent and a 3-percent discount rate.
See chapter 10 of the NOPR TSD for
more detailed NPV results.
small business capital as well as
corporate capital. DOE used this
discount rate to approximate the
opportunity cost of capital in the private
sector, as OMB analysis has found the
average rate of return to capital to be
near this rate. In addition, DOE used the
3-percent rate to capture the potential
effects of amended standards on private
consumption (e.g., through higher prices
for products and reduced purchases of
energy). This rate represents the rate at
which society discounts future
consumption flows to their present
TABLE V.38—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFITS FOR WATER HEATERS
[Impacts for units sold from 2015 to 2045]
Product class
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
TSL 7
billion 2008 dollars
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Discounted at 3%
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7.58
2.19
0.12
0.30
9.04
3.16
0.20
0.30
9.04
4.73
0.28
0.30
9.04
6.02
0.28
0.30
9.63
11.67
0.28
0.30
9.04
31.90
0.28
0.30
11.27
41.94
0.47
¥5.68
Total ...............
Discounted at 7%
Gas-Fired Storage
Electric Storage ....
Oil-Fired Storage ..
Gas-Fired Instantaneous.
10.20
12.71
14.36
15.64
21.89
41.52
47.99
Gas-Fired Storage
Electric Storage ....
Oil-Fired Storage ..
2.94
0.69
0.05
3.09
1.03
0.09
3.09
1.32
0.12
3.09
1.59
0.12
3.17
3.35
0.12
3.09
5.22
0.12
¥1.10
8.50
0.19
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TABLE V.38—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFITS FOR WATER HEATERS—Continued
[Impacts for units sold from 2015 to 2045]
Gas-Fired Instantaneous.
0.01
0.01
0.01
0.01
0.01
0.01
¥4.84
Total ...............
3.69
4.20
4.53
4.79
6.64
8.43
2.75
TABLE V.39—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFITS FOR DIRECT HEATING EQUIPMENT
[Impacts for units sold from 2013 to 2043]
Product class
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
billion 2008 dollars
Discounted at 3% .......
0.07
0.07
0.0003
0.02
1.52
0.09
0.22
0.0003
0.05
1.52
0.11
0.52
0.0003
0.08
1.52
0.14
0.52
0.0003
0.08
¥1.06
0.07
0.37
0.0003
0.35
¥1.06
0.14
0.37
0.0003
0.35
¥3.49
1.68
1.87
2.22
¥0.33
¥0.26
¥2.63
Wall Fan ..............
Wall Gravity ........
Floor ....................
Room ..................
Hearth .................
0.03
0.03
0.0001
0.01
0.64
0.04
0.09
0.0001
0.02
0.64
0.04
0.20
0.0001
0.03
0.64
0.04
0.20
0.0001
0.03
¥1.16
0.03
0.06
0.0001
0.14
¥1.16
0.04
0.06
0.0001
0.14
¥3.78
Total .....................
Gas
Gas
Gas
Gas
Gas
Wall Fan ..............
Wall Gravity ........
Floor ....................
Room ..................
Hearth .................
Total .....................
Discounted at 7% .......
Gas
Gas
Gas
Gas
Gas
0.71
0.79
0.91
¥0.89
¥0.93
¥3.54
TABLE V.40—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFITS FOR POOL HEATERS
[Impacts for units sold from 2013 to 2043]
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
billion 2008 dollars
Discounted at 3% .............................................................
Discounted at 7% .............................................................
c. Net Present Value of Benefits From
Energy Price Impacts
DOE estimated the cumulative NPV of
the economy-wide savings in natural gas
expenditures during the forecast period
due to the projected decline in natural
gas prices resulting from amended
0.16
0.08
0.18
0.07
0.40
0.14
standards on water heaters. DOE
calculated the cumulative NPV for the
efficiency levels in each product class
corresponding to each TSL using both a
7-percent and a 3-percent discount rate
(Table V.41). (The impact of amended
standards for direct heating equipment
0.25
0.03
¥1.97
¥1.27
¥4.51
¥2.94
and pool heaters was not estimated for
the reasons explained in section IV.F.)
See chapter 10 of the NOPR TSD for
further details. As discussed in section
IV.F.2.g, DOE was not able to estimate
the impact of the considered TSLs on
electricity prices.
TABLE V.41—CUMULATIVE NPV OF THE ECONOMY-WIDE SAVINGS IN NATURAL GAS EXPENDITURES DUE TO THE
PROJECTED DECLINE IN NATURAL GAS PRICES RESULTING FROM AMENDED STANDARDS FOR WATER HEATERS*
Discount Rate
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
TSL 7
billion $2008
3 percent ..................................................
7 percent ..................................................
3.0
1.4
4.5
2.2
5.1
2.5
5.6
2.7
7.1
3.4
23.6
12.0
47.7
24.2
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
* Impacts for units sold from 2015 to 2045.
d. Impacts on Employment
Employment impacts consist of direct
and indirect impacts. Direct
employment impacts are any changes in
the number of employees of
manufacturers of the appliance products
that are the subject of this rulemaking,
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their suppliers, and related service
firms. Indirect employment impacts are
changes in employment in the larger
economy that occur due to the shift in
expenditures and capital investment
caused by the purchase and operation of
more-efficient appliances. The MIA
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addresses the direct employment
impacts that concern manufacturers of
the three heating products (see section
V.B.2 above).
To estimate the indirect employment
impacts of potential amended energy
conservation standards, DOE used an
input/output model of the U.S. economy
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(see section IV.I)). The input/output
model results suggest that amended
standards would be likely to increase
the net demand for labor in the
economy slightly. Table V.42 presents
the estimated net indirect employment
impacts from the TSLs that DOE
considered for water heaters. The
estimated impacts from the potential
amended standards for DHE and pool
heaters would be much smaller. (Note
that the input/output model DOE uses
does not report the quality or wage level
of the jobs.) See chapter 14 of the NOPR
TSD for more detailed results.
TABLE V.42—NET INCREASE IN NATIONAL INDIRECT EMPLOYMENT UNDER WATER HEATER TSLS
2015
thousands
Trial standard level
1
2
3
4
5
6
7
¥0.17
¥0.46q
-0.55
¥0.62
¥0.77
¥2.47
¥6.98
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
...............................................................................................
While DOE’s analysis suggests that
amended standards could increase the
net demand for labor in the economy,
the estimated gains would be very small
relative to total national employment.
Therefore, DOE has tentatively
concluded that the considered standard
levels would be likely to produce
employment benefits sufficient to fully
offset any adverse impacts on
employment in the manufacturing
industries related to the three types of
heating products that are the subject of
this rulemaking.
4. Impact on Utility or Performance of
Products
As discussed in section III.D.1.d, DOE
has tentatively concluded that none of
the efficiency levels considered in this
notice would reduce the utility or
performance of the three types of
heating products. Furthermore,
manufacturers of these products
currently offer heating products that
meet or exceed the proposed standards.
(42 U.S.C. 6295(o)(2)(B)(i)(IV))
5. Impact of Any Lessening of
Competition
DOE has also considered any
lessening of competition likely to result
from amended standards. The Attorney
General determines the impact, if any,
of any lessening of competition likely to
result from a proposed standard, and
transmits its determination to the
Secretary, together with an analysis of
2020
thousands
2030
thousands
1.02
1.20
1.97
2.58
5.63
18.48
19.37
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, DOE has
provided DOJ with copies of this notice
and the TSD for review. DOE will
consider DOJ’s comments on the
proposed rule in preparing the final
rule, and DOE will publish and respond
to DOJ’s comments in that document.
6. Need of the Nation To Conserve
Energy
Improving the energy efficiency of
heating products when economically
justified would likely improve the
security of the Nation’s energy system
by reducing overall demand for energy.
(42 U.S.C. 6295(o)(2)(B)(i)(VI)) Reduced
electricity demand may also improve
the reliability of the electricity system.
Energy savings from amended
standards for heating products could
also produce environmental benefits in
the form of reduced emissions of air
pollutants and greenhouse gases
associated with energy production and
the use of fossil fuels at the sites where
heating products are used. Table V.43
and Table V.44 provide DOE’s estimate
of cumulative CO2, NOX, and Hg
emissions reductions that would be
expected to result from the TSLs
considered in this rulemaking. In the
environmental assessment (chapter 16
of the NOPR TSD), DOE reports the
estimated annual change in CO2, NOX,
and Hg emissions attributable to each
TSL.
2044
thousands
2.58
3.36
5.27
6.75
13.95
45.72
54.03
3.32
4.38
6.70
8.49
17.82
55.67
68.11
For DHE, DOE estimates a very slight
increase in Hg emissions under the
proposed standard. The reason for this
result is that the more-efficient products
save natural gas, but they also use more
electricity due to electronic ignition
and, for some DHE TSLs, use of a fan.
This results in higher electricity
generation than in the reference case,
which leads to higher emissions.
However, because the increase in
electricity that these more efficient
products are projected to use is
comparatively small when compared to
the reduction in natural gas usage, there
will be an overall efficiency gain from
the proposed standard. For CO2 and
NOX, the higher emissions from the
power sector would also be canceled out
by lower household emissions from gas
combustion, resulting in a total
emissions decrease under the
considered TSLs. This is not the case for
Hg because there are no household Hg
emissions to offset.
As discussed in section IV.K, DOE
does not report SO2 emissions
reductions from power plants because
there is uncertainty about the effect of
energy conservation standards on the
overall level of SO2 emissions in the
United States due to SO2 emissions
caps. DOE also 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.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
TABLE V.43—SUMMARY OF EMISSIONS REDUCTIONS UNDER WATER HEATER TSLS
[Cumulative throughout forecast period]
TSL
Emission Type
1
CO2 (Mt) .....................................
NOX (kt) .....................................
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4
5
6
7
136.8
106
146.6
113
153.8
118
217.0
165
346.0
254
965.5
730
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TABLE V.43—SUMMARY OF EMISSIONS REDUCTIONS UNDER WATER HEATER TSLS—Continued
[Cumulative throughout forecast period]
TSL
Emission Type
1
Hg (t) ..........................................
2
0.11
3
0.16
4
0.19
5
0.20
6
7
0.60
2.18
4.43
TABLE V.44—SUMMARY OF EMISSIONS REDUCTIONS UNDER DIRECT HEATING EQUIPMENT AND POOL HEATER TSLS
[Cumulative throughout forecast period]
TSL
Emission Type
1
2
3
4
5
6
Direct Heating Equipment
CO2 (Mt) ...........................................................................
NOX (kt) ...........................................................................
Hg (t) ................................................................................
6.32
5.79
(0.02)
7.02
6.42
(0.02)
8.52
7.74
(0.02)
16.69
15.2
(0.00)
18.46
16.9
(0.01)
42.97
39.6
(0.01)
1.05
0.94
0.00
3.31
2.98
0.01
4.21
3.74
0.00
5.74
5.10
0.00
12.12
10.77
0.00
Pool Heaters
CO2 (Mt) ...........................................................................
NOX (kt) ...........................................................................
Hg (t) ................................................................................
DOE estimated the cumulative
monetary value of the economic benefits
associated with CO2 emissions
reductions expected to result from
amended standards for the three types
of heating products. As discussed in
section IV.K, in considering the
potential global benefits resulting from
reduced CO2 emissions, DOE used
0.610
0.55
0.00
values based on a social cost of carbon
of approximately $5, $10, $20, $34 and
$56 per metric ton avoided in 2007
(values expressed in 2008$). DOE also
calculated the domestic benefits based
on a value of approximately $1 per
metric ton avoided in 2007. To monetize
the CO2 emissions reductions expected
to result from amended standards for
heating products in 2013–2045, DOE
escalated the above values for 2007
using a three-percent escalation rate. For
each of the three types of heating
products, DOE calculated the
cumulative monetary value for each TSL
using both a 7-percent and 3-percent
discount rate (see Table V.45 through
Table V.50).
TABLE V.45—ESTIMATES OF THE VALUE OF CO2 EMISSIONS REDUCTIONS FOR WATER HEATERS UNDER TRIAL STANDARD
LEVELS USING 7% DISCOUNT RATE
Value of estimated CO2 emission reductions (million 2008$)*
Domestic
Global
TSL
CO2 value of
$1/metric ton
CO2
1
2
3
4
5
6
7
.............................................................
.............................................................
.............................................................
.............................................................
.............................................................
.............................................................
.............................................................
CO2 value of
$5/metric ton
CO2
48.0
74.1
79.4
83.4
112
171
487
CO2 value of
$10/metric ton
CO2
CO2 value of
$20/metric ton
CO2
CO2 value of
$34/metric ton
CO2
CO2 value of
$56/metric ton
CO2
421
650
697
732
983
1,497
4,268
800
1,235
1,324
1,390
1,869
2,845
8,110
1,390
2,145
2,299
2,414
3,246
4,941
14,085
2,317
3,575
3,832
4,024
5,409
8,235
23,476
211
325
348
366
492
749
2,134
* Unit values are approximate and are based on escalating 2007$ to 2008$ for consistency with other values presented in this notice.
TABLE V.46—ESTIMATES OF THE VALUE OF CO2 EMISSIONS REDUCTIONS FOR WATER HEATERS UNDER TRIAL STANDARD
LEVELS USING 3% DISCOUNT RATE
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Value of estimated CO2 emission reductions (million 2008$)*
Domestic
Global
TSL
CO2 value of
$1/metric ton
CO2
1 ...............................................................
2 ...............................................................
3 ...............................................................
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CO2 value of
$5/metric ton
CO2
110
169
181
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CO2 value of
$10/metric ton
CO2
CO2 value of
$20/metric ton
CO2
CO2 value of
$34/metric ton
CO2
CO2 value of
$56/metric ton
CO2
961
1,482
1,588
1,826
2,816
3,017
3,171
4,890
5,239
5,285
8,151
8,732
480
741
794
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TABLE V.46—ESTIMATES OF THE VALUE OF CO2 EMISSIONS REDUCTIONS FOR WATER HEATERS UNDER TRIAL STANDARD
LEVELS USING 3% DISCOUNT RATE—Continued
Value of estimated CO2 emission reductions (million 2008$)*
Domestic
Global
TSL
CO2 value of
$1/metric ton
CO2
4
5
6
7
...............................................................
...............................................................
...............................................................
...............................................................
CO2 value of
$5/metric ton
CO2
190
265
416
1,170
CO2 value of
$10/metric ton
CO2
CO2 value of
$20/metric ton
CO2
CO2 value of
$34/metric ton
CO2
CO2 value of
$56/metric ton
CO2
1,666
2,325
3,648
10,263
3,166
4,417
6,932
19,500
5,499
7,672
12,040
33,868
9,166
12,787
20,066
56,447
833
1,162
1,824
5,132
* Unit values are approximate and are based on escalating 2007$ to 2008$ for consistency with other values presented in this notice.
TABLE V.47—ESTIMATES OF THE VALUE OF CO2 EMISSIONS REDUCTIONS FOR DIRECT HEATING EQUIPMENT UNDER
TRIAL STANDARD LEVELS USING 7% DISCOUNT RATE
Value of estimated CO2 emission reductions (million 2008$)*
Domestic
Global
TSL
CO2 value of
$1/metric ton
CO2
1
2
3
4
5
6
.........................................................
.........................................................
.........................................................
.........................................................
.........................................................
.........................................................
CO2 value of
$5/metric ton
CO2
3.69
4.09
4.96
9.78
10.8
25.2
CO2 value of
$10/metric ton
CO2
16.2
18.0
21.8
42.9
47.4
111
CO2 value of
$20/metric ton
CO2
CO2 value of
$34/metric ton
CO2
CO2 value of
$56/metric ton
CO2
61.5
68.2
82.8
163
180
420
107
119
144
283
313
730
178
198
240
472
521
1,216
32.4
35.9
43.6
85.8
94.8
221
* Unit values are approximate and are based on escalating 2007$ to 2008$ for consistency with other values presented in this notice.
TABLE V.48—ESTIMATES OF THE VALUE OF CO2 EMISSIONS REDUCTIONS FOR DIRECT HEATING EQUIPMENT UNDER
TRIAL STANDARD LEVELS USING 3% DISCOUNT RATE
Value of estimated CO2 emission reductions (million 2008$)*
Domestic
Global
TSL
CO2 value of
$1/metric ton
CO2
1
2
3
4
5
6
.........................................................
.........................................................
.........................................................
.........................................................
.........................................................
.........................................................
CO2 value of
$5/metric ton
CO2
7.81
8.68
10.5
20.6
22.8
53.1
CO2 value of
$10/metric ton
CO2
34.3
38.1
46.2
90.5
100
233
CO2 value of
$20/metric ton
CO2
CO2 value of
$34/metric ton
CO2
CO2 value of
$56/metric ton
CO2
130
145
176
344
380
886
226
251
305
598
661
1,538
377
419
508
996
1,101
2,564
68.5
76.1
92.4
181
200
466
* Unit values are approximate and are based on escalating 2007$ to 2008$ for consistency with other values presented in this notice.
TABLE V.49—ESTIMATES OF THE VALUE OF CO2 EMISSIONS REDUCTIONS FOR POOL HEATERS UNDER TRIAL STANDARD
LEVELS USING 7% DISCOUNT RATE
Value of estimated CO2 emission reductions
(million 2008$)*
Domestic
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
TSL
CO2 value of
$1/metric ton
CO2
1
2
3
4
5
6
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
Global
CO2 value of $5/
metric ton CO2
0.37
0.64
2.02
2.55
3.47
7.33
CO2 value of
$10/metric ton
CO2
1.63
2.81
8.86
11.2
15.2
32.8
CO2 value of
$20/metric ton
CO2
CO2 value of
$34/metric ton
CO2
CO2 value of
$56/metric ton
CO2
6.21
10.7
33.7
42.5
57.9
122
10.8
18.5
58.5
73.
101
212
18.0
30.9
97.4
123
168
354
3.27
5.61
17.7
22.4
30.5
64.3
* Unit values are approximate and are based on escalating 2007$ to 2008$ for consistency with other values presented in this notice.
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TABLE V.50—ESTIMATES OF THE VALUE OF CO2 EMISSIONS REDUCTIONS FOR POOL HEATERS UNDER TRIAL STANDARD
LEVELS USING 3% DISCOUNT RATE
Value of estimated CO2 emission reductions
(million 2008$)*
Domestic
TSL
CO2 value of
$1/metric ton
CO2
1
2
3
4
5
6
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
.....................................................
Global
CO2 value of $5/
metric ton CO2
0.75
1.30
4.09
5.21
7.10
15.0
CO2 value of
$10/metric ton
CO2
3.31
5.69
18.0
22.8
31.1
65.7
CO2 value of
$20/metric ton
CO2
CO2 value of
$34/metric ton
CO2
CO2 value of
$56/metric ton
CO2
12.6
21.6
68.2
86.8
118
250
21.8
37.5
118
151
205
434
36.4
62.5
197
251
342
723
6.62
11.4
35.9
45.7
62.2
131
* Unit values are approximate and are based on escalating 2007$ to 2008$ for consistency with other values presented in this notice.
DOE also estimated a range for the
cumulative monetary value of the
economic benefits associated with NOX
and Hg emissions reductions
anticipated to result from amended
standards for the three types of heating
products under consideration in this
rulemaking. Table V.51 through Table
V.54 present the results for NOX
emissions reductions. Table V.53
presents the results for Hg emissions
reductions for water heaters. The values
for Hg emissions reductions for direct
heating equipment and pool heater TSLs
are negligible.
TABLE V.51—ESTIMATES OF THE VALUE OF NOX EMISSIONS REDUCTIONS FOR WATER HEATERS UNDER TRIAL
STANDARD LEVELS
Value at
7% discount rate
million 2008$
TSL
1
2
3
4
5
6
7
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
7.44–76.4
11.5–118
12.3–126
12.9–132
16.4–168
23.0–236
69.1–710
Value at
3% discount rate
million 2008$
15.9–163
24.5–252
26.2–269
27.4–282
36.6–377
54.1–556
159–1,632
TABLE V.52—ESTIMATES OF THE VALUE OF NOX EMISSIONS REDUCTIONS FOR DIRECT HEATING EQUIPMENT UNDER
TRIAL STANDARD LEVELS
Value at
7% discount rate
million 2008$
TSL
1
2
3
4
5
6
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
0.71–7.26
0.78–8.04
0.94–9.68
1.87–19.2
2.07–21.3
4.86–50.0
Value at
3% discount rate
million 2008$
1.41–14.51
1.56–16.07
1.89–19.39
3.73–38.32
4.13–42.50
9.67–99.45
TABLE V.53—ESTIMATES OF THE VALUE OF NOX EMISSIONS REDUCTIONS FOR POOL HEATERS UNDER TRIAL STANDARD
LEVELS
Value at
7% discount rate
million 2008$
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
TSL
1
2
3
4
5
6
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
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0.07–0.75
0.12–1.28
0.39–4.05
0.49–5.03
0.67–6.86
1.41–14.49
11DEP2
Value at
3% discount rate
million 2008$
0.14–1.43
0.24–2.45
0.75–7.73
0.94–9.66
1.28–13.16
2.70–27.80
65960
Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
TABLE V.54—ESTIMATES OF THE VALUE OF MERCURY EMISSIONS REDUCTIONS FOR WATER HEATERS UNDER TRIAL
STANDARD LEVELS
Value at
7% discount rate
million 2008$
TSL
1
2
3
4
5
6
7
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
...................................................................................................................................................................
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.55 presents the
NPV values for water heaters that would
result if DOE were to add the low- and
high-end estimates of the potential
benefits resulting from reduced CO2,
NOX and Hg emissions to the NPV of
consumer savings calculated for each
TSL considered in this rulemaking, at
both a 7- and 3-percent discount rate.
Table V.56 presents the NPV values for
DHE that would result if DOE were to
add the low- and high-end estimates of
the potential global benefits resulting
from reduced CO2 emissions to the NPV
of consumer savings calculated for each
TSL considered in this rulemaking, at
both a 7- and 3-percent discount rate.
Table V.57 presents the same NPV
values for pool heaters. For CO2, only
the low and high global benefit values
are used for these tables ($5 and $56 in
2008$).
Although adding the value of
consumer savings to the values of
emission reductions provides a valuable
perspective, please note the following:
1) the national consumer savings are
domestic U.S. consumer monetary
savings found in market transactions,
while the values of emission reductions
are based on ranges of estimates of
imputed marginal social costs, which, in
the case of CO2, are meant to reflect
global benefits; and 2) the assessments
of consumer savings and emissionrelated benefits are performed with
different computer models, leading to
different time frames for the analyses.
For water heaters, for example, the
present value of national consumer
savings is measured for the period
2015–2065 (30 years from 2015 to 2045,
Value at
3% discount rate
million 2008$
0.03–1.20
0.04–1.82
0.05–2.07
0.05–2.25
0.16–6.94
0.49–21.7
0.99–44.1
0.05–2.17
0.07–3.30
0.08–3.74
0.09–4.09
0.28–12.53
0.93–41.7
1.90–84.8
plus the longest lifetime of the
equipment shipped in the 30th year).
However, the time frames of the benefits
associated with the emission reductions
differ. For example, the value of CO2
emission reductions is meant to reflect
the present value of all future climaterelated impacts, even those beyond
2065.
DOE seeks comment on its
presentation of NPV values and on the
consideration of GHG emissions in
future energy conservation standards
rulemakings, including alternative
methodological approaches to including
GHG emissions in its analysis. More
specifically, DOE seeks comment on
both how it integrates monetized GHG
emissions or Social Cost of Carbon
values, as well as other monetized
benefits or costs, into its analysis and
models, and also on suggested
alternatives to the current approach.
TABLE V.55—ESTIMATES OF ADDING NPV OF CONSUMER SAVINGS TO NPV OF LOW- AND HIGH-END GLOBAL MONETIZED
BENEFITS FROM CO2, NOX, AND HG EMISSIONS REDUCTIONS AT ALL TSLS FOR WATER HEATERS AT 3- AND 7-PERCENT DISCOUNT RATES
CO2 value of $5/metric ton
CO2* and low values for NOX
and Hg**
billion 2008$
7-percent
discount rate
TSL
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
1
2
3
4
5
6
7
CO2 value of $56/metric ton
CO2* and high values for NOX
and Hg***
billion 2008$
7-percent
discount rate
.....................................................................................................................
.....................................................................................................................
.....................................................................................................................
.....................................................................................................................
.....................................................................................................................
.....................................................................................................................
.....................................................................................................................
3-percent
discount rate
3.90
4.54
4.89
5.17
7.14
9.20
4.95
10.7
13.5
15.2
16.5
23.1
43.4
53.3
* These values per ton represent the global negative externalities of CO2.
** Low Value corresponds to a value of $442 per ton of NOX emissions and $0.745 million per ton of Hg emissions.
*** High Value corresponds to a value of $4,540 per ton of NOX emissions and $33.3 million per ton of Hg emissions.
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11DEP2
6.08
7.90
8.49
8.95
12.2
16.9
27.0
3-percent
discount rate
15.6
21.1
23.4
25.1
35.1
62.2
106
Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
65961
TABLE V.56—ESTIMATES OF ADDING NPV OF CONSUMER SAVINGS TO NPV OF LOW- AND HIGH-END GLOBAL MONETIZED
BENEFITS FROM CO2, NOX, AND HG EMISSIONS REDUCTIONS AT ALL TSLS FOR DHE AT 3- AND 7-PERCENT DISCOUNT RATES
CO2 value of $5/metric ton
CO2* and low values for NOX
and Hg**
billion 2008$
7-percent
discount rate
TSL
1
2
3
4
5
6
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
CO2 value of $56/metric ton
CO2* and high values for NOX
and Hg***
billion 2008$
3-percent
discount rate
7-percent
discount rate
3-percent
discount rate
0.722
0.804
0.938
(0.840)
(0.855)
(3.42)
1.72
1.91
2.27
(0.233)
(0.156)
(2.38)
0.890
0.991
1.16
(0.394)
(0.392)
(2.27)
2.07
2.31
2.75
0.707
0.884
0.038
* These values per ton represent the global negative externalities of CO2.
** Low Value corresponds to a value of $442 per ton of NOX emissions and $0.745 million per ton of Hg emissions.
*** High Value corresponds to a value of $4,540 per ton of NOX emissions and $33.3 million per ton of Hg emissions.
TABLE V.57—ESTIMATES OF ADDING NPV OF CONSUMER SAVINGS TO NPV OF LOW- AND HIGH-END MONETIZED BENEFITS FROM CO2, NOX, AND HG EMISSIONS REDUCTIONS AT ALL TSLS FOR POOL HEATERS AT 3- AND 7-PERCENT
DISCOUNT RATES
CO2 value of $5/metric ton
CO2* and low values for NOX
and Hg**
billion 2008$
7-percent
discount rate
TSL
1
2
3
4
5
6
CO2 value of $56/metric ton
CO2* and high values for NOX
and Hg***
billion 2008$
7-percent
discount rate
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
3-percent
discount rate
0.077
0.078
0.147
0.044
(1.25)
(2.90)
0.019
0.033
0.100
0.121
0.166
0.353
0.094
0.107
0.239
0.161
(1.09)
(2.57)
3-percent
discount rate
0.053
0.092
0.287
0.358
0.489
1.03
* These values per ton represent the global negative externalities of CO2.
** Low Value corresponds to a value of $442 per ton of NOX emissions and $0.745 million per ton of Hg emissions.
*** High Value corresponds to a value of $4,540 per ton of NOX emissions and $33.3 million per ton of Hg emissions.
TABLE V.58—ESTIMATES OF ADDING NPV OF CONSUMER SAVINGS TO NPV OF LOW- AND HIGH-END MONETIZED BENEFITS FROM CO2 EMISSIONS REDUCTIONS AT ALL TSLS FOR WATER HEATERS, DHE AND POOL HEATERS AT 3- AND
7-PERCENT DISCOUNT RATE
CO2 value of $5/metric ton
CO2* and low values for NOX
and Hg**
billion 2008$
7-percent
discount rate
TSL
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
1
2
3
4
5
6
7
CO2 value of $56/metric ton
CO2* and high values for NOX
and Hg***
billion 2008$
7-percent
discount rate
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
.......................................................................................................................
3-percent
discount rate
4.69
5.41
5.96
4.36
4.99
2.85
1.45
12.4
15.4
17.5
16.4
23.1
41.3
51.1
2,517
3,808
4,174
4,622
6,102
9,807
25,042
3-percent
discount rate
5,710
8,647
9,455
10,428
14,252
23,392
59,779
* These values per ton represent the global negative externalities of CO2.
** Low Value corresponds to a value of $442 per ton of NOX emissions and $0.745 million per ton of Hg emissions.
*** High Value corresponds to a value of $4,540 per ton of NOX emissions and $33.3 million per ton of Hg emissions.
7. Other Factors
In determining whether a standard is
economically justified, the Secretary of
Energy may consider any other factors
that the Secretary deems to be relevant.
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(42 U.S.C. 6295(o)(2)(B)(i)(VII)) The
Secretary has decided that the LCC
impacts on identifiable groups of
consumers, such as senior citizens and
residents of multi-family housing who
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may be disproportionately affected by
any national energy conservation
standard level, is a relevant factor. The
impacts on the identified consumer
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65962
Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
subgroups are described in section V.B.1
above.
DOE also believes that uncertainties
associated with the heat pump water
heater market (e.g., product availability)
are relevant to consider. These
uncertainties are discussed in section
V.C below.
C. Proposed Standards
When considering proposed
standards, DOE recognizes that EPCA
specifies that any new or amended
energy conservation standard 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 to the greatest extent
practicable, in light of 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))
DOE considered the impacts of
standards at each trial standard level,
beginning with the maximum
technologically feasible level, to
determine whether each level was
economically justified. If the max-tech
level is not justified, DOE then
considers the next most efficient level
and undertakes the same evaluation
until it reached the highest level that is
both technologically feasible and
economically justified, and saves a
significant amount of energy.
To aid the reader as DOE discusses
the benefits and/or burdens of each trial
standard level, the tables in the
following sections present summaries of
the results of DOE’s quantitative
analysis at each TSL for each of the
three heating products based on the
methodology discussed above.
Additional quantitative results (e.g., the
cumulative NPV to natural gas
consumers of the economy-wide savings
in natural gas expenditures during the
forecast period due to the projected
decline in natural gas prices resulting
from amended standards on the three
types of heating products) are provided
in section V.B.3.
In addition to the quantitative results,
DOE also considers other burdens and
benefits that affect economic
justification. These include the LCC
impacts on identifiable subgroups of
consumers, such as seniors and
residents of multi-family housing, who
may be disproportionately affected by
any national energy conservation
standard level, and the uncertainties
associated with the heat pump water
heater market.
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. 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). There is evidence
that consumers undervalue future
energy savings as a result of (1) A lack
of information, (2) a lack of sufficient
savings to warrant delaying or altering
purchases (e.g. an inefficient ventilation
fan in a new building or the delayed
replacement of a water pump), (3)
inconsistent (e.g. excessive short-term)
weighting of future energy cost savings
relative to available returns on other
investments, (4) computational or other
difficulties associated with the
evaluation of relevant tradeoffs, and (5)
a divergence in incentives (e.g. renter
versus owner; builder v. purchaser).
Other literature indicates that with less
than perfect foresight and a high degree
of uncertainty about the future,
consumers may tradeoff these types of
investments at a higher than expected
rate between current consumption and
uncertain future energy cost savings.
While DOE is not prepared at present to
provide a fuller quantifiable framework
for this discussion, DOE seeks
comments on how to assess these
possibilities.
1. Water Heaters
Table V.59 presents a summary of the
impacts for each water heater TSL.
TABLE V.59—SUMMARY OF RESULTS FOR WATER HEATERS
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Category
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
National Energy Savings
(quads).
3% discount rate .............
7% discount rate .............
NPV of Consumer Benefits
(2008$ billion).
3% discount rate .............
7% discount rate .............
Industry Impacts
Gas-Fired and Electric
Storage.
Industry NPV (2008$
million).
Industry NPV (%
change).
Oil-Fired Storage.
Industry NPV (2008$
million).
Industry NPV (%
change).
Gas-Fired Instantaneous.
Industry NPV (2008$
million).
Industry NPV (%
change).
Cumulative Emissions Reduction.
1.26 ..............
1.88 ..............
2.28 ..............
2.60 ..............
3.74 ..............
10.44 ............
16.85
0.67 ..............
0.32 ..............
0.99 ..............
0.47 ..............
1.21 ..............
0.58 ..............
1.38 ..............
0.66 ..............
1.99 ..............
0.96 ..............
5.57 ..............
2.71 ..............
8.98
0.32
10.20 ............
3.69 ..............
12.71 ............
4.20 ..............
14.36 ............
4.53 ..............
15.64 ............
4.79 ..............
21.89 ............
6.64 ..............
41.52 ............
8.43 ..............
47.99
2.75
(4)–(12) ........
(5)–(31) ........
(5)–(35) ........
(3)–(79) ........
(21)–(130) ....
(2)–(306) ......
63–(538)
(0.5)–(1.5) ....
(0.6)–(3.6) ....
(0.6)–(4.2) ....
(0.4)–(9.4) ....
(2.5)–(15.4) ..
(0.2)–(36.3) ..
7.5-(63.8)
(0.2)–(0.3) ....
(0.2)–(0.3) ....
(0.2)–(0.4) ....
(0.2)–(0.4) ....
(0.2)–(0.4) ....
(0.2)–(0.4) ....
(1.3)–(3.5)
(1.9)–(3.9) ....
(1.8)–(3.6) ....
(2.0)–(4.3) ....
(2.0)–(4.3) ....
(2.0)–(4.3) ....
(2.0)–(4.3) ....
(14.8)–(39.9)
1.2–(1.8) .......
1.2–(1.8) .......
1.2–(1.8) .......
1.2–(1.8) .......
1.2–(1.8) .......
1.2–(1.8) .......
80.3–(65.9)
0.2–(0.3) .......
0.2–(0.3) .......
0.2–(0.3) .......
0.2–(0.3) .......
0.2–(0.3) .......
0.2–(0.3) .......
13.3–(10.9)
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TSL 7
65963
Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
TABLE V.59—SUMMARY OF RESULTS FOR WATER HEATERS—Continued
Category
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
CO2 (Mt) ..........................
NOX (kt) ...........................
Hg (t) ...............................
Value of Cumulative Emissions Reduction (2008$ million)‡.
CO2—3% discount rate ...
CO2—7% discount rate ...
NOX—3% discount rate ..
NOX—7% discount rate ..
Hg—3% discount rate .....
Hg—7% discount rate .....
Mean LCC Savings* (2008$).
Gas-Fired Storage ...........
Electric Storage ...............
Oil-Fired Storage .............
Gas-Fired Instantaneous
Median PBP (years).
Gas-Fired Storage ...........
Electric Storage ........
Oil-Fired Storage ......
Gas-Fired Instantaneous.
Distribution of Consumer LCC
Impacts
Gas-Fired Storage.
Net Cost (%) ............
No Impact (%) ..........
Net Benefit (%) .........
Electric Storage.
Net Cost (%) ............
No Impact (%) ..........
Net Benefit (%) .........
Oil-Fired Storage.
Net Cost (%) ............
No Impact (%) ..........
Net Benefit (%) .........
Gas-Fired Instantaneous.
Net Cost (%) ............
No Impact (%) ..........
Net Benefit (%) .........
Generation Capacity Change
(GW)†.
Employment Impacts
Total Potential Changes
in Domestic Production
Workers in 2015.
Gas-Fired and Electric Storage.
Oil-Fired Storage ......
Gas-Fired Instantaneous.
88.7 ..............
68.5 ..............
0.11 ..............
137 ...............
106 ...............
0.16 ..............
147 ...............
113 ...............
0.19 ..............
154 ...............
118 ...............
0.20 ..............
217 ...............
165 ...............
0.60 ..............
346 ...............
254 ...............
2.18 ..............
965
730
4.43
480–5,285 ....
211–2,317 ....
16–163 .........
7–76 .............
0.05–2.2 .......
0.03–1.2 .......
741–8,151 ....
325–3,575 ....
24–252 .........
11–118 .........
0.07–3.3 .......
0.04–1.8 .......
794–8,732 ....
348–3,832 ....
26–269 .........
12–126 .........
0.08–3.7 .......
0.05–2.1 .......
833–9,166 ....
366–4,024 ....
27–282 .........
13–132 .........
0.09–4.1 .......
0.05–2.2 .......
1,162–12,787
492–5,409 ....
37–377 .........
16–168 .........
0.28–12.53 ...
0.16–6.94 .....
1,824–20,066
749–8,235 ....
54.1–556 ......
23.0–236 ......
0.93–41.7 .....
0.49–21.7 .....
5,132–56,447
2,134–23,476
159–1,632
69–710
1.90–84.8
0.99–44.1
69 .................
16 .................
171 ...............
0 ...................
68 .................
23 .................
288 ...............
0 ...................
68 .................
32 .................
395 ...............
0 ...................
68 .................
39 .................
395 ...............
0 ...................
78 .................
96 .................
395 ...............
0 ...................
68 .................
224 ...............
395 ...............
0 ...................
(55)
273
655
(307)
1.4 ................
2.8 ................
0.7 ................
23.5 ..............
2.7 ................
3.0 ................
0.4 ................
23.5 ..............
2.7 ................
4.5 ................
0.5 ................
23.5 ..............
2.7 ................
5.8 ................
0.5 ................
23.5 ..............
3.0 ................
5.9 ................
0.5 ................
23.5 ..............
2.7 ................
8.3 ................
0.5 ................
23.5 ..............
14.1
8.2
1.4
39.5
9 ...................
22 .................
69 .................
15 .................
17 .................
68 .................
15 .................
17 .................
68 .................
15 .................
17 .................
68 .................
16 .................
16 .................
68 .................
15 .................
17 .................
68 .................
62
1
36
10 .................
32 .................
59 .................
11 .................
29 .................
60 .................
20 .................
14 .................
66 .................
25 .................
10 .................
65 .................
25 .................
10 .................
65 .................
45 .................
5 ...................
50 .................
45
1
54
0 ...................
69 .................
31 .................
0 ...................
52 .................
48 .................
0 ...................
45 .................
55 .................
0 ...................
45 .................
55 .................
0 ...................
45 .................
55 .................
0 ...................
45 .................
55 .................
0
7
93
11 .................
85 .................
4 ...................
(0.129) ..........
11 .................
85 .................
4 ...................
(0.195) ..........
11 .................
85 .................
4 ...................
(0.221) ..........
11 .................
85 .................
4 ...................
(0.242) ..........
11 .................
85 .................
4 ...................
(0.956) ..........
11 .................
85 .................
4 ...................
(2.59) ............
83
6
12
(5.28)
(3,690)–68 ....
(3,690)–152 ..
(3,690)–191 ..
(3,690)–287 ..
(3,690)–706 ..
(3,690)–4,078
(3,690)–6,133
(38)–(1) ........
Not Applicable *.
(38)–2 ...........
......................
(38)–(1) ........
......................
(38)–(1) ........
......................
(38)–(1) ........
......................
(38)–(1) ........
......................
(38)–9
3.32 ..............
4.38 ..............
6.70 ..............
8.49 ..............
17.82 ............
55.67 ............
68.11
Indirect domestic jobs
(thousands) †.
TSL 7
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Note: Parentheses indicate negative (-) values.
* For LCCs, a negative value means an increase in LCC by the amount indicated.
** The industry for gas-fired instantaneous water heaters is international.
† Changes in 2044
‡ Range of the economic value of CO reductions is based on estimates of the global benefit of reduced CO emissions.
2
2
DOE first considered TSL 7, which
represents the max-tech efficiency levels
for all four product classes. TSL 7
would save 16.85 quads of energy, an
amount DOE considers significant. TSL
7 would provide a NPV of consumer
benefit of $2.75 billion, using a discount
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20:45 Dec 10, 2009
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rate of 7 percent, and $48.0 billion,
using a discount rate of 3 percent.
The cumulative emissions reductions
at TSL 7 are 965 Mt of CO2, 730 kt of
NOX, and 4.43 t of Hg. The estimated
monetary value of the cumulative CO2
emissions reductions at TSL 7 is $2.13
billion to $23.48 billion, using a
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discount rate of 7 percent, and $5.13 to
$56.45 billion, using a discount rate of
3 percent. Total electricity generating
capacity in 2044 is estimated to
decrease by 5.28 gigawatts (GW) under
TSL 7.
At TSL 7, DOE projects that the
average LCC impact for consumers is a
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loss of $55 for gas-fired storage water
heaters, a gain of $273 for electric
storage water heaters, a gain of $655 for
oil-fired storage water heaters, and a
loss of $307 for gas-fired instantaneous
water heaters. The median payback
period is 14.1 years for gas-fired storage
water heaters, 8.2 years for electric
storage water heaters, 1.4 years for oilfired storage water heaters, and 39.5
years for gas-fired instantaneous water
heaters (which is substantially longer
than the mean lifetime of the product).
At TSL 7, the fraction of consumers
experiencing an LCC benefit is 36
percent for gas-fired storage water
heaters, 54 percent for electric storage
water heaters, 93 percent for oil-fired
storage water heaters, and 12 percent for
gas-fired instantaneous water heaters.
The fraction of consumers experiencing
an LCC cost is 62 percent for gas-fired
storage water heaters, 45 percent for
electric storage water heaters, 0 percent
for oil-fired storage water heaters, and
83 percent for gas-fired instantaneous
water heaters.
At TSL 7, the projected change in the
INPV is estimated to decrease up to
$538 million for gas-fired and electric
storage water heaters, a decrease of up
to $3.5 million for residential oil-fired
storage water heaters, and a decrease of
up to $66 million for gas-fired
instantaneous water waters, in 2008$.
For gas and electric storage water
heaters, the impacts are driven
primarily by the assumptions regarding
the ability for manufacturers to produce
products at these efficiency levels in the
volumes necessary to serve the entire
market. Manufacturers would need to
redesign almost all of their products at
TSL 7, which would force
manufacturers to incur significant
product and capital conversion costs.
Some loss in product utility may also
occur for units that are presently
installed in space-constrained
applications because condensing and
heat pump technologies would typically
cause water heaters to have a larger
footprint. At TSL 7, DOE recognizes the
risk of very large negative impacts if
manufacturers’ expectations about
reduced profit margins are realized. In
particular, if the high end of the range
of impacts is reached as DOE expects,
TSL 7 could result in a net loss of 63.8
percent in INPV for gas-fired and
electric storage water heaters, a net loss
of 39.9 percent in INPV for oil-fired
storage water heaters, and a net loss of
10.9 percent in INPV for gas-fired
instantaneous water heaters.
At TSL 7, the average LCC savings are
lower for all of the considered consumer
subgroups than for the full household
sample for electric and gas-fired storage
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water heaters. In the case of electric
storage water heaters, the multi-family
subgroup would experience an average
negative LCC savings of $357 (i.e., the
average LCC would increase), and threefourths of the households would
experience a net cost. For the other
subgroups, the fraction of households
that would experience a net cost is close
to or just above 50 percent, which is
slightly higher than for the full
household sample. The impact on the
multi-family subgroup is primarily due
to the lower hot water use per family
among these households.
For gas-fired storage water heaters at
TSL 7, condensing operation would be
required. DOE has several concerns
related to the condensing gas-fired
storage water heater market. At the time
of the NOPR analysis, there were no
condensing gas-fired storage water
heaters available to residential
consumers in the United States. DOE is
concerned about the ability of
manufacturers to convert all product
lines to manufacture condensing gasfired storage water heaters in the
volumes needed by the compliance date
of the standard, because the
manufacturers’ ability to afford the
necessary conversion costs is uncertain.
In addition, uncertainties exist about
whether manufacturers will be able to
train enough installers and servicers of
condensing gas-fired water heaters to
serve the relevant market by the
compliance date of the standard. As
with electric storage heat pump water
heaters, DOE is concerned that a typical
installer or repair person will not have
the knowledge required to troubleshoot
or repair condensing gas-fired storage
water heaters since they are more
complex than traditional gas-fired
storage water heaters. It is unclear
whether reliable installation and
servicing could be achieved by the
effective date for compliance with the
standard.
TSL 7 also includes an efficiency
level for electric storage water heaters
that will require the use of heat pump
technology. The substantial average
savings for customers estimated by
DOE’s analysis for TSL 7 are primarily
driven by the results for heat pump
water heaters. However, DOE has
concerns about issues with the current
heat pump water heater market that may
prevent heat pump technology from
being ready for full scale
implementation. DOE fully discusses
these concerns and seeks comments
from interested parties on a variety of
issues associated with heat pump water
heaters in its discussion of the benefits
and burdens of TSL 6, below.
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The Secretary tentatively concludes
that at TSL 7, the benefits of energy
savings, positive NPV of consumer
benefits, generating capacity reductions,
and emission reductions would be
outweighed by the economic burden on
a significant fraction of consumers due
to the large increases in first costs
associated with electric heat pump
water heaters and gas-fired condensing
water heaters, the disproportionate
impacts to consumers in multi-family
housing, the large capital conversion
costs that could result in a large
reduction in INPV for the
manufacturers, as well as the
uncertainty associated with providing
products at the max-tech level on a scale
necessary to serve the entire market.
Consequently, the Secretary has
tentatively concluded that TSL 7 is not
economically justified.
Next, DOE considered TSL 6. The
efficiency levels in TSL 6 include the
ENERGY STAR program level for
electric storage water heaters, which
requires heat pump water heaters. TSL
6 would save 10.4 quads of energy, an
amount DOE considers significant. TSL
6 would increase consumer NPV by $8.4
billion, using a discount rate of 7
percent, and increase the NPV by $41.5
billion, using a discount rate of 3
percent.
The cumulative emissions reductions
at TSL 6 are 346 Mt of CO2, 254 kt of
NOX, and 2.18 t of Hg. The estimated
monetary value of the cumulative CO2
emissions reductions at TSL 6 is $749
billion to $8.235 billion, using a
discount rate of 7 percent, and $1.824
billion to $20.066 billion, using a
discount rate of 3 percent. Total
generating capacity in 2044 is estimated
to decrease by 2.59 GW under TSL 6.
At TSL 6, DOE projects that the
average LCC impact is a gain of $68 for
gas-fired storage water heaters, a gain of
$224 for electric storage water heaters,
a gain of $395 for oil-fired storage water
heaters, and no change for gas-fired
instantaneous water heaters. The
median payback period is 2.7 years for
gas-fired storage water heaters, 8.3 years
for electric storage water heaters, 0.5
years for oil-fired storage water heaters,
and 23.5 years for gas-fired
instantaneous water heaters (which is
longer than the mean lifetime of the
product). At TSL 6, the fraction of
consumers experiencing an LCC benefit
is 68 percent for gas-fired storage water
heaters, 50 percent for electric storage
water heaters, 55 percent for oil-fired
storage water heaters, and 4 percent for
gas-fired instantaneous water heaters.
The fraction of consumers experiencing
an LCC cost is 15 percent for gas-fired
storage water heaters, 45 percent for
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electric storage water heaters, 0 percent
for oil-fired storage water heaters, and
11 percent for gas-fired instantaneous
water heaters.
At TSL 6, the projected change in
INPV ranges from a decrease of up to
$305.8 million for gas-fired and electric
storage water heaters, a decrease of up
to $0.4 million for oil-fired storage water
heaters, and a decrease of up to $1.8
million for gas-fired instantaneous water
heaters, in 2008$. The negative impacts
on INPV are driven largely by the
required efficiencies for electric storage
water heaters which effectively require
heat pump technology. The oil-fired
storage water heater and gas-fired
instantaneous water heater efficiencies
do not require substantial changes to the
existing operations for some
manufacturers. The significant changes
for electric storage water heaters help to
drive the INPVs negative, especially if
profitability is impacted after the
compliance date of the amended energy
conservation standard. In particular, if
the high end of the range of impacts is
reached as DOE expects, TSL 6 could
result in a net loss of 36.3 percent in
INPV for gas-fired and electric storage
water heaters, a net loss of 4.3 percent
in INPV for oil-fired storage water
heaters, and a net loss of 0.3 percent in
INPV for gas-fired instantaneous water
heaters.
TSL 6 includes efficiency levels for
electric storage water heaters that are
currently only achievable through the
use of advanced heat pump
technologies. DOE’s analysis indicates
that dramatic reductions in energy use
and substantial economic savings are
possible for electric water heaters with
the use of these technologies. The
average savings for electric water heater
customers estimated by DOE’s analysis
for TSL 6 are primarily driven by the
results for heat pump water heaters.
While DOE finds the potential energy
savings resulting from a national heat
pump water heater standard very
favorable, DOE has some concerns
regarding the manufacturability and the
market for heat pump water heaters,
which are further discussed below.
Heat pump technologies are currently
used in space heating and cooling, and
other refrigeration-cycle products,
indicating that this technology is a
viable design option. The use of heat
pump water heaters adds dramatically
to the MSP estimates, increasing the
MSP more than $400 over the baseline
electric storage water heater. In part due
to this change, the total installed cost to
the consumer increases by an average of
$900 for heat pump water heaters
compared to traditional electric storage
water heaters that use electric resistance
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20:45 Dec 10, 2009
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heating elements. Even though there are
potential benefits of adopting an
amended energy conservation standard
requiring heat pump technologies, DOE
is concerned about the uncertainties
currently experienced in the heat pump
water heater market.
Although most manufacturers are in
the process of developing a heat pump
water heater to offer to consumers in
response to the ENERGY STAR program
or have recently began to offer a heat
pump water heater model for sale, heat
pump water heaters were not offered for
sale at the time DOE’s analysis was
developed. DOE’s shipments model
projects that by 2015 heat pump water
heaters will achieve approximately five
percent market share. The manufacturer
impacts are driven primarily by the
assumptions regarding the ability of
manufacturers to produce heat pump
water heaters in the full range of rated
storage volumes in the quantities
necessary to serve the entire market.
Though most electric storage water
heater manufacturers indicated that they
are in the process of developing heat
pump water heaters, all manufacturers
believe that an efficiency level that
requires heat pump water heater
technology is not appropriate as an
amended energy conservation standard.
Several manufacturers expect that they
will have to buy the heat pump modules
from outside vendors because most
water heater manufacturers have no
experience manufacturing heat pumps
and have limited space in their facilities
to produce heat pump systems.
Manufacturers stated that they would
consider moving all or part of their
existing production capacity abroad if
the energy conservation standard is set
at TSL 6 because many manufacturers
expect to have to redesign their facilities
completely to accommodate a minimum
energy conservation standard requiring
heat pump water heaters. DOE is
concerned about the capability of
manufacturers to convert all product
lines to manufacture heat pump water
heaters in the volumes needed by the
compliance date of the standard,
because producing exclusively heat
pump water heaters will require $119
million in conversion costs plus an
additional $256 million in working
capital for a $375 million cash
requirement. In addition, water heater
manufacturers would be dependent
upon the ability of heat pump
component manufacturers (e.g.,
compressor manufacturers) to ramp up
production to support the new market
by the compliance date of the amended
standard. DOE invites comments on the
viability for high-volume production of
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65965
heat pump water heaters in the full
range of rated storage volumes and also
requests information or data that would
allow an assessment of such viability to
be conducted. (See Issue 11 under
‘‘Issues on Which DOE Seeks Comment’’
in section VII.E of this NOPR.)
DOE also notes that the service
industry has very little experience with
integrated heat pump water heater
designs because heat pump water
heaters have only been available in the
U.S. market in the past for short periods
of time, and have only recently become
available to the U.S. market once again.
DOE is concerned that a typical installer
or repair person would not have the
requisite knowledge to troubleshoot or
repair heat pump water heaters because
they are more complex than traditional
electric storage water heaters. It is
unclear whether reliable installation
and servicing could be achieved on the
scale needed by the compliance date of
the amended standard.
In addition, although DOE’s analysis
reveals that heat pump water heaters are
capable of being installed in all of the
types of installations currently serviced
by the residential electric storage water
heating market, DOE found that in
certain situations (especially indoor
locations) installations could be very
costly for consumers, requiring them to
alter their existing space to
accommodate a heat pump water heater.
DOE estimates 30 to 40 percent of
installations would require such
building modifications. In part for this
reason, DOE estimated that 12 percent
of electric storage water heater
consumers would experience an
increase of more than $500 in their LCC
compared to the base case.
Another concern DOE has regarding
heat pump water heaters is the impact
on consumer utility in the instances
when electric storage water heaters are
installed in conditioned indoor spaces.
DOE estimates that 39 percent of electric
storage water heaters are installed in
conditioned spaces. In these cases, the
cold air given off by the heat pump
module may negatively impact
consumer comfort due to uneven
heating and cooling.
DOE strongly considered TSL 6 as the
proposed standard level for residential
water heaters. DOE is concerned,
however, about the ability for
manufacturers to ramp up production in
time to meet the demand by the
compliance date of amended standards,
the potential large increases in total
installed cost to certain consumers, the
ability for the service industry to gain
the knowledge and experience
necessary to provide reliable service to
consumers, the potential impacts on
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multi-family households, and the
potential impacts on the space
conditioning of the residence. DOE
seeks comments and data from
interested parties that will allow DOE to
further bring clarity to the issues
surrounding heat pump water heaters,
and determine how the issues discussed
in the paragraphs above could be
adequately addressed prior to the
compliance date of an amended national
energy conservation standard for water
heaters that would effectively require
the use of such technology. (See Issue
16 under ‘‘Issues on Which DOE Seeks
Comment’’ in section VII.E of this
NOPR.) For today’s proposed rule, the
Secretary tentatively concludes that at
TSL 6, the benefits of energy savings,
generating capacity reductions, and
emission reductions would be
outweighed by the negative economic
impacts on those consumers that would
have to make structural changes to
accommodate the larger footprint of the
heat pump water heaters, the economic
burden on a large fraction of consumers
due to the large increases in first costs
associated with heat pump water
heaters, the disproportionate impacts to
consumers in multi-family housing and
others with comparatively low usage
rates, the large capital conversion costs
that could result in a large reduction in
INPV for the manufacturers, and the
uncertainties associated with the heat
pump water heater market. DOE is
particularly concerned about product
availability for the heat pump water
heater market since it is unclear
whether manufacturers would be able to
produce equipment in the volumes
necessary to serve the entire market.
DOE will revisit this decision and
strongly reconsider adoption of TSL 6 in
the final rule in light of any comments
and data submitted by interested
parties.
Next, DOE considered TSL 5, in
which DOE paired efficiency levels that
would effectively require different
technologies for large-volume and
small-volume gas-fired and electric
storage water heaters in an effort to
promote advance technology
penetration into the market and
potentially save additional energy.
Specifically, TSL 5 would effectively
require heat pump technology for
electric storage water heaters greater
than 55 gallons and condensing
technology for gas-fired storage water
heaters greater than 55 gallons.
TSL 5 would save 3.7 quads of energy,
an amount DOE considers significant.
Under TSL 5, the NPV of consumer
benefit would be $6.64 billion, using a
discount rate of 7 percent, and $21.89
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billion, using a discount rate of 3
percent.
The cumulative emissions reductions
at TSL 5 are 217 Mt of CO2, 165 kt of
NOX, and 0.60 t of Hg. The estimated
monetary value of the cumulative CO2
emissions reductions at TSL 5 is $0.492
to $5.409 billion, using a discount rate
of 7 percent, and $1.162 to $12.787
billion, using a discount rate of 3
percent. Total generating capacity in
2044 is estimated to decrease by 0.96
GW under TSL 5.
At TSL 5, DOE projects that the
average LCC impact is a gain (consumer
cost savings) of $78 for gas-fired storage
water heaters, a gain of $96 for electric
storage water heaters, a gain of $395 for
oil-fired storage water heaters, and no
change for gas-fired instantaneous water
heaters. The median payback period is
3.0 years for gas-fired storage water
heaters, 5.9 years for electric storage
water heaters, 0.5 years for oil-fired
storage water heaters, and 23.5 years for
gas-fired instantaneous water heaters
(which is longer than the mean lifetime
of the product). At TSL 5, the fraction
of consumers experiencing an LCC
benefit is 68 percent for gas-fired storage
water heaters, 65 percent for electric
storage water heaters, 55 percent for oilfired storage water heaters, and 4
percent for gas-fired instantaneous
water heaters. The fraction of consumers
experiencing an LCC cost is 16 percent
for gas-fired storage water heaters, 25
percent for electric storage water
heaters, 0 percent for oil-fired storage
water heaters, and 11 percent for gasfired instantaneous water heaters.
At TSL 5, the projected change in
INPV ranges from a decrease of up to
$129.9 million for gas-fired and electric
storage water heaters, a decrease of up
to $0.4 million for oil-fired storage water
heaters, and a decrease of up to $1.8
million for gas-fired instantaneous water
heaters, in 2008$. The negative impacts
on INPV are driven largely by the
required efficiencies for gas-fired and
electric storage water heaters with rated
storage volumes above 55 gallons. TSL
5 would effectively require heat pump
technology and condensing technology
for the electric and gas-fired storage
water heaters at these volume sizes. The
efficiency requirements at TSL 5 for
electric storage water heater with a rated
volume less than 55 also result in
negative impacts because such large
increases in insulation also require
manufacturers to implement changes to
their existing equipment. The oil-fired
storage water heater and gas-fired
instantaneous water heater efficiencies
at TSL 5 do not require substantial
changes to the existing operations for
some manufacturers. The significant
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changes gas-fired and electric storage
water heaters with rated storage
volumes greater than 55 gallons help to
drive the INPVs negative, especially if
profitability is impacted after the
compliance date of the amended energy
conservation standard. In particular, if
the high end of the range of impacts is
reached as DOE expects, TSL 5 could
result in a net loss of 15.4 percent in
INPV for gas-fired and electric storage
water heaters, a net loss of 4.3 percent
in INPV for oil-fired storage water
heaters, and a net loss of 0.3 percent in
INPV for gas-fired instantaneous water
heaters.
DOE believes TSL 5 would provide an
effective mechanism for increasing the
market penetration for advancedtechnology water heaters. Given DOE’s
concerns with TSL 6 (which includes a
national heat pump water heater
standard for electric storage water
heaters across the entire range of rated
storage volumes) as described above,
DOE also strongly considered proposing
TSL 5. TSL 5 results in positive NPV of
consumer benefit for both electric and
gas-fired storage water heaters, while
also providing additional energy and
carbon savings.
Using DOE’s shipments model and
market assessment, DOE estimated
approximately 4 percent of gas-fired
storage water heater shipments and 11
percent of models would fall into the
large-volume water heater category
using the TSL 5 division (i.e., large
water heaters with storage volumes
above 55 gallons). Similarly, DOE
estimated approximately 9 percent of
electric storage water heater shipments
and 27 percent of models would fall
into the large-volume water heater
category using the TSL 5 division.
Compared to TSL 6, TSL 5 effectively
requires heat pump technology for a
relatively small fraction of the electric
storage water heater market, reduces the
number of installations that would
necessitate significant building
modifications due to the size of heat
pump water heaters, reduces the
number of installations that have space
conditioning impacts from cool air
produced by the heat pump water heater
operation, results in higher average
savings and lower median payback
periods, and reduces the negative
impacts on consumer subgroups. For
gas-fired storage water heaters,
compared to a national condensing
standard level (TSL 7), TSL 5 requires
condensing technology for a relatively
small fraction of the gas storage water
heater market, reduces the number of
installations that require significant
building modifications due to the size of
condensing gas water heaters, and
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results in higher average LCC savings
and lower median payback period.
Even though DOE has identified a
number of benefits associated with TSL
5, DOE is aware that there are multiple
issues associated with promulgating an
amended energy conservation standard
that affects only a subset of the products
on the market. Potential issues with TSL
5 affecting both heat pump water
heaters and condensing gas-fired water
heaters include: (1) Consumer
acceptance; (2) training; (3) product
substitution; (4) engineering resource
constraints; (5) product discontinuation;
and (6) manufacturing issues.
First, consumers may elect not to buy
the larger volume water heaters for a
number of reasons, including increased
first cost, being unfamiliar with the
advanced technologies being used, and
installation size constraints. Both heat
pump and condensing water heaters are
significantly more expensive than
baseline water heaters of the same
nominal capacity and take up more
space per nominal gallon of capacity. As
a result, consumers may buy multiple
water heaters that are under the capacity
limit and use them in parallel to achieve
the same nominal capacity, although at
a higher standby loss.
Furthermore, the current water heater
service and installation infrastructure
has little to no experience installing and
servicing these advanced-technology
storage water heaters, leading to
possible reluctance of contractors to
install these products. To minimize unit
damage and warranty claims and to
improve market acceptance,
manufacturers would likely have to
expend significant additional resources
to hire training staff to tour the country
and to provide technical support at
headquarters. Additionally, field
technicians likely would need
additional licenses and test equipment
to be able to service heat pump water
heaters properly (for example, to recover
refrigerant). These additional
requirements would likely increase
installation and service costs beyond
current levels, since consumers will
have fewer servicers/installers to choose
from and the products have become
more complex.
Due to the price discrepancy between
the cost of commercial equipment (not
covered by the heat pump and
condensing requirement) and residential
products of the same capacity, the use
of commercially-classified storage water
heater equipment in residential
applications would likely significantly
expand beyond current levels under
TSL 5. Such substitutions have health
and safety considerations such as the
typical lack of FVIR protection and the
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higher allowable set-point temperatures
for commercial equipment.
Manufacturers would likely face
constraints regarding the abilities of
their engineering teams to develop
multiple water heater families, as most
engineering departments have limited
experience with either advanced
technology. At a minimum, condensing
gas-fired products would require
manufacturers to convert existing
commercial equipment lines to
residential use. However, multiple
manufacturers are expected to have to
develop completely new platforms in
order to remain cost-competitive.
In light of the above, manufacturers
could decide that the demand for
residential heat pump and condensing
gas water heaters would likely drop to
a point where product conversion and
capital costs required to modify their
operations are not justified. As a result,
some manufacturers would likely no
longer manufacture residential storage
water heaters at rated storage volumes
above the division point (i.e., 56 gallons
and above). Even if a manufacturer were
to offer products, development and
capital costs make it likely that
consumers would have fewer product
families to choose from than presently
exist. Mass-manufacturing facilities
visited by DOE were typically finetuned for units with similar assembly
processes and cannot accommodate
units with a wide scope of assembly
requirements. Units that fall outside
these standardized (high-volume)
production settings would likely have to
be assembled on a separate line in a new
facility adjacent to current
manufacturing space. The costs to
retrofit a manufacturing plant to allow
production of these units are high and
the industry reaction is uncertain. DOE
seeks comments about whether
manufacturers would upgrade just one
of their facilities (and produce all heat
pump and/or condensing units there) or
would upgrade multiple facilities to
minimize shipping costs and
distribution costs. Additionally,
manufacturers could continue the trend
to relocate to new facilities or expand
existing facilities abroad.
DOE strongly considered TSL 5 and
believes it would provide additional
energy and carbon savings, while
mitigating some of the issues associated
with a national heat pump water heater
standard. However, DOE has identified
a number of potential issues with TSL
5 related to proposing standards that
effectively require different technologies
for different subsets of products. For
today’s proposed rule, the Secretary
tentatively concludes that at TSL 5, the
benefits of energy savings, generating
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65967
capacity reductions, economic savings
for most consumers, and the emission
reductions would be outweighed by the
large capital conversion costs that could
result in a large reduction in INPV for
the manufacturers, the uncertainties
associated with the rapid introduction
of new product technologies, the large
increases in first costs, especially for
those consumers that would have to
make structural changes, and the
uncertainties associated with a
promulgation of an amended energy
conservation standards that only affects
a subset of the market. DOE seeks
comments and data from interested
parties that will assist DOE in bringing
further clarity to some of the issues
surrounding the product division used
in the two slope energy-efficiency
equations, promulgation of different
standards for a subset of products, the
heat pump water heater market, the
condensing water heater market, as well
as help DOE determine how these issues
can be adequately addressed prior to the
compliance date of an amended energy
conservation standard for residential
water heaters. (See Issue 17 under
‘‘Issues on Which DOE Seeks Comment’’
in section VII.E of this NOPR.) DOE will
revisit this decision and strongly
consider adoption of TSL 5 in the final
rule in light of any comments and data
submitted by interested parties.
Next, DOE considered TSL 4. TSL 4
would save 2.6 quads of energy, an
amount DOE considers significant.
Under TSL 4, the NPV of consumer
benefit would be $4.8 billion, using a
discount rate of 7 percent, and $15.6
billion, using a discount rate of 3
percent.
The cumulative emissions reductions
at TSL 4 are 154 Mt of CO2, 118 kt of
NOX, and 0.2 t of Hg. The estimated
monetary value of the cumulative CO2
emissions reductions at TSL 4 is $0.366
to $4.024 billion, using a discount rate
of 7 percent, and $0.833 to $9.166
billion, using a discount rate of 3
percent. Total generating capacity in
2044 is estimated to decrease by 0.24
GW under TSL 4.
At TSL 4, DOE projects that the
average LCC impact is a gain of $68 for
gas-fired storage water heaters, a gain of
$39 for electric storage water heaters, a
gain of $395 for oil-fired storage water
heaters, and no change for gas-fired
instantaneous water heaters. The
median payback period is 2.7 years for
gas-fired storage water heaters, 5.8 years
for electric storage water heaters, 0.5
years for oil-fired storage water heaters,
and 23.5 years for gas-fired
instantaneous water heaters (which is
longer than the mean lifetime of the
product). At TSL 4, the fraction of
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consumers experiencing an LCC benefit
is 68 percent for gas-fired storage water
heaters, 65 percent for electric storage
water heaters, 55 percent for oil-fired
storage water heaters, and 4 percent for
gas-fired instantaneous water heaters.
The fraction of consumers experiencing
an LCC cost is 15 percent for gas-fired
storage water heaters, 25 percent for
electric storage water heaters, 0 percent
for oil-fired storage water heaters, and
11 percent for gas-fired instantaneous
water heaters. For gas-fired
instantaneous water heaters, 85 percent
of consumers would not be impacted at
TSL 4 because DOE projects that they
would purchase an appliance of equal
or higher efficiency than the TSL 4
level.
At TSL 4, the projected change in
INPV ranges from a decrease of up to
$79 million for gas-fired and electric
storage water heaters, a decrease of up
to $0.4 million for oil-fired storage water
heaters, and a decrease of up to $1.8
million for gas-fired instantaneous water
heaters, in 2008$. The impacts on
manufacturers are less significant at
TSL4 because the technology used at
TSL 4 does not greatly differ from
baseline models for gas-fired, electric,
and oil-fired storage water heaters. In
addition, most manufacturers of gasfired instantaneous water heaters offer
products that meet or exceed the
efficiencies required at TSL 4. If the
high end of the range of impacts is
reached as DOE expects, TSL 4 could
result in a net loss of 9.4 percent in
INPV for gas-fired and electric storage
water heaters, a net loss of 4.3 percent
in INPV for oil-fired storage water
heaters, and a net loss of 0.3 percent in
INPV for gas-fired instantaneous water
heaters.
After considering the analysis,
comments on the January 13, 2009,
notice and the preliminary TSD, and the
benefits and burdens of TSL 4, the
Secretary tentatively concludes that this
TSL will offer the maximum
improvement in efficiency that is
technologically feasible and
economically justified, and will result
in significant conservation of energy.
Further, benefits from carbon dioxide
reductions (at a central value of $20)
would increase NPV by between $366
million and $4,024 million (2008$) at a
7% discount rate and between $833
million and $9,166 million at a 3%
discount rate. These benefits from
carbon dioxide emission reductions,
when considered in conjunction with
the consumer savings NPV and other
factors described above support DOE’s
tentative conclusion that trial standard
level 4 is economically justified.
Therefore, the Department today
proposes to adopt TSL 4 as amended
energy conservation standards for water
heaters as shown in Table V.60.
TABLE V.60—PROPOSED MINIMUM ENERGY FACTOR REQUIREMENTS FOR RESIDENTIAL WATER HEATERS (TSL 4)
Product class
Energy factor requirement
Gas-fired Storage .................
For tanks with a Rated Storage Volume at or below 60
gallons:.
EF = 0.675 ¥ (0.0012 × Rated Storage Volume in gallons).
For tanks with a Rated Storage Volume at or below 80
gallons:.
EF = 0.96 ¥ (.0003 × Rated Storage Volume in gallons).
Electric Storage ....................
galgalgalgal-
EF = 0.68 ¥ (.0019 × Rated Storage Volume in gallons)
EF = 0.82 ¥ (.0019 × Rated Storage Volume in gallons)
Oil-fired Storage ...................
Gas-fired Instantaneous .......
DOE also calculated the annualized
values for certain benefits and costs
under the considered TSLs. The
annualized values refer to consumer
operating cost savings, consumer
incremental product and installation
costs, the quantity of emissions
reductions for CO2, NOX, and Hg, and
the monetary value of CO2 emissions
reductions (using a value of $20/t CO2,
which is in the middle of the values
considered by DOE for valuing the
potential global benefits resulting from
reduced CO2 emissions).
DOE used a two-step calculation
process to convert the time-series of
costs and benefits into annualized
values. First, DOE calculated a present
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
For tanks with a Rated Storage Volume above 60
lons:
EF = 0.717 ¥(0.0019 × Rated Storage Volume in
lons)
For tanks with a Rated Storage Volume above 80
lons:
EF = 1.088 ¥ (.0019 × Rated Storage Volume in
lons)
value for the time-series of costs and
benefits using a discount rate of either
three or seven percent. From the present
value, DOE then calculated the fixed
annual payment over the analysis time
period (2015 to 2045 for water heaters)
that yielded 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 are a steady stream of
payments.
Table V.61 presents the annualized
values for each TSL considered for
water heaters. The tables also present
the annualized net benefit that results
from summing the two monetary
benefits and subtracting the consumer
incremental product and installation
costs. Although summing the value of
operating savings with the value of CO2
reductions provides a valuable
perspective, please note the following.
The operating cost savings are domestic
U.S. consumer monetary savings found
in market transactions while the CO2
value is based on an estimate of
imputed marginal SCC, which is meant
to reflect the global benefits of CO2
reductions. In addition, the SCC value
considers a longer time frame than the
period considered for operating cost
savings.
TABLE V.61—ANNUALIZED BENEFITS AND COSTS FOR WATER HEATERS BY TRIAL STANDARD LEVEL
TSL
Category
Primary estimate
(AEO reference case)
Unit
7%
3%
Low estimate
(AEO low growth case)
7%
3%
Benefits
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(high growth case)
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65969
TABLE V.61—ANNUALIZED BENEFITS AND COSTS FOR WATER HEATERS BY TRIAL STANDARD LEVEL—Continued
TSL
Category
Primary estimate
(AEO reference case)
Unit
Low estimate
(AEO low growth case)
High estimate
(high growth case)
7%
1 ........
Monetized Operating
Cost Savings.
Quantified Emissions Reductions.
Monetized Avoided CO2
Value (at $19/t).
3%
7%
3%
7%
3%
Million 2008$ ...................
709.5 ........
885.3 .......
663.7 .......
824.2 .......
755.3 .......
946.6
CO2 (Mt) ..........................
2.63 .........
2.83 ..........
3.04 .........
3.01 ..........
0.52 ..........
0.77
NOX (kt) ..........................
Hg (t) ...............................
Million 2008$ ...................
2.04 .........
0.005 ........
90.4 .........
2.19 ..........
0.004 .......
108.0 ........
2.38 ..........
(0.002) .....
105.1 .......
2.35 .........
(0.006) .....
126.5 .......
0.47 ..........
0.005 ........
17.6 ..........
0.67
0.007
30.8
277.2 .......
265.3 .......
308.7 .......
299.4
491.6 .......
685.4 ........
464.3 .......
677.9
Costs
Monetized Incremental
Product and Installation
Costs.
Million 2008$ ...................
292.9 ........
282.3 .......
Net Benefits
Monetized Value .............
Million 2008$ ...................
507.0 .......
2 ........
711.0 .......
Benefits
Monetized Operating
Cost Savings.
Quantified Emissions Reductions.
Monetized Avoided CO2
Value (at $19/t).
Million 2008$ ...................
1,051.1 ....
1,309.8 .....
984.4 .......
1,220.4 .....
1,117.9 ....
1,399.4
CO2 (Mt) ..........................
4.07 .........
4.37 ..........
4.68 .........
4.63 ..........
0.85 ..........
1.24
NOX (kt) ..........................
Hg (t) ...............................
Million 2008$ ...................
3.16 .........
0.007 ........
139.6 .......
3.38 ..........
0.006 .......
166.5 .......
3.66 ..........
(0.003) .....
161.9 .......
3.61 .........
(0.009) .....
194.6 ........
0.77 ..........
0.008 ........
28.9 .........
1.07
0.011
49.2
545.2 .......
524.1 .......
607.5 .......
591.9
601.1 .......
890.8 ........
539.4 .......
856.8
Costs
Monetized Incremental
Product and Installation
Costs.
Million 2008$ ...................
576.2 ........
557.9 .......
Net Benefits
Monetized Value .............
Million 2008$ ...................
614.5 .......
3 ........
918.5 .......
Benefits
Monetized Operating
Cost Savings.
Quantified Emissions Reductions.
Monetized Avoided CO2
Value (at $19/t).
Million 2008$ ...................
1,297.3 ....
1,610.6 .....
1,210.0 .....
1,496.1 ....
1,384.7 .....
1,725.0
CO2 (Mt) ..........................
4.36 .........
4.68 ..........
5.05 .........
5.00 ..........
0.72 ..........
1.13
NOX (kt) ..........................
Hg (t) ...............................
Million 2008$ ...................
3.38 .........
0.008 ........
149.6 .......
3.62 ..........
0.007 .......
178.4 .......
3.95 ..........
(0.003) .....
175.0 .......
3.90 .........
(0.010) .....
210.3 ........
0.67 ..........
0.009 ........
24.1 .........
0.99
0.012
45.2
742.9 .......
715.3 .......
828.0 .......
807.9
642.0 .......
991.2 .......
580.8 .......
962.4
Costs
Monetized Incremental
Product and Installation
Costs.
Million 2008$ ...................
785.3 ........
761.4 .......
Net Benefits
Monetized Value .............
Million 2008$ ...................
661.7 .......
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
4 ........
1,027.7 .....
Benefits
Monetized Operating
Cost Savings.
Quantified Emissions Reductions.
Monetized Avoided CO2
Value (at $19/t).
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22:35 Dec 10, 2009
Million 2008$ ...................
1,487.1 ....
1,842.4 .....
1,383.7 .....
1,708.4 ....
1,590.5 .....
1,976.2
CO2 (Mt) ..........................
4.58 .........
4.92 ..........
5.34 .........
5.28 ..........
0.61 ..........
1.04
NOX (kt) ..........................
Hg (t) ...............................
Million 2008$ ...................
3.54 .........
0.009 ........
157.1 .......
3.79 ..........
0.008 .......
187.3 .......
4.17 ..........
(0.003) .....
184.8 .......
4.11 .........
(0.011) .....
222.1 ........
0.58 ..........
0.010 ........
20.2 .........
0.92
0.013
41.9
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TABLE V.61—ANNUALIZED BENEFITS AND COSTS FOR WATER HEATERS BY TRIAL STANDARD LEVEL—Continued
TSL
Category
Primary estimate
(AEO reference case)
Unit
7%
Low estimate
(AEO low growth case)
High estimate
(high growth case)
3%
7%
3%
7%
3%
917.3 .......
894.4 .......
861.7 .......
997.0 .......
973.4
674.1 .......
1,068.9 ....
613.7 ........
1,044.7
Costs
Monetized Incremental
Product and Installation
Costs.
Million 2008$ ...................
945.5 ........
Net Benefits
Monetized Value .............
Million 2008$ ...................
698.8 .......
5 ........
1,112.4 .....
Benefits
Monetized Operating
Cost Savings.
Quantified Emissions Reductions.
Monetized Avoided CO2
Value (at $19/t).
Million 2008$ ...................
2,163.1 ....
2,670.6 .....
2,005.0 .....
2,469.3 ....
2,320.8 .....
2,871.2
CO2 (Mt) ..........................
6.18 .........
6.83 ..........
14.38 .......
14.84 .......
3.11 ..........
3.56
NOX (kt) ..........................
Hg (t) ...............................
Million 2008$ ...................
4.72 .........
0.023 ........
211.2 .......
5.20 ..........
0.022 .......
261.2 .......
11.09 .......
0.038 .......
318.5 .......
11.41 .......
0.030 .......
383.1 ........
2.43 ..........
0.011 .......
26.2 .........
2.78
0.017
52.1
1,336.7 ....
1,292.6 .....
1,490.2 ....
1,460.4
668.3 .......
1176.7 ......
830.6 .......
1410.8
Costs
Monetized Incremental
Product and Installation
Costs.
Million 2008$ ...................
1,413.1 .....
1,376.1 .....
Net Benefits
Monetized Value .............
Million 2008$ ...................
961.2 .......
6 ........
1555.7 ......
Benefits
Monetized Operating
Cost Savings.
Quantified Emissions Reductions.
Monetized Avoided CO2
Value (at $19/t).
Million 2008$ ...................
6,331.1 ....
7,745.0 .....
5,801.0 .....
7,097.1 ....
6,857.9 .....
8,387.1
CO2 (Mt) ..........................
9.49 .........
10.72 .......
15.61 ........
16.89 .......
(2.13) .......
(1.50)
NOX (kt) ..........................
Hg (t) ...............................
Million 2008$ ...................
7.02 .........
0.077 ........
321.6 .......
7.90 ..........
0.075 .......
410.0 .......
11.90 .......
0.038 .......
537.9 .......
12.82 .......
0.036 .......
646.5 ........
(1.58) .......
0.004 .......
(86.7) .......
(1.08)
0.012
(62.2)
5,112.0 ....
4,992.4 .....
5,700.5 ....
5,641.7
689.0 .......
2,104.7 .....
1,157.4 ....
2,745.4
Costs
Monetized Incremental
Product and Installation
Costs.
Million 2008$ ...................
5,405.0 .....
5,315.6 .....
Net Benefits
Monetized Value .............
Million 2008$ ...................
1,247.7 ....
7 ........
Benefits
Monetized Operating
Cost Savings.
Quantified Emissions Reductions.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
2,839.3 .....
Monetized Avoided CO2
Value (at $19/t).
Million 2008$ ...................
9,837.9 ....
12,187.1 ...
9,105.6 ....
11,255.5 ..
10,568.4 ...
13,115.0
CO2 (Mt) ..........................
26.82 .......
30.05 .......
39.27 .......
39.00 .......
3.17 ..........
5.19
NOX (kt) ..........................
Hg (t) ...............................
Million 2008$ ...................
20.41 .......
0.157 ........
916.6 .......
22.79 .......
0.153 .......
1,153.3 .....
30.34 .......
0.078 .......
1,357.0 ....
29.99 ........
0.056 .......
1,634.6 .....
2.91 .........
0.007 .......
85.6 .........
4.51
0.024
192.1
9,010.5 ....
8,779.1 .....
10,048.9 ..
9,923.2
Costs
Monetized Incremental
Product and Installation
Costs.
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Million 2008$ ...................
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TABLE V.61—ANNUALIZED BENEFITS AND COSTS FOR WATER HEATERS BY TRIAL STANDARD LEVEL—Continued
TSL
Category
Primary estimate
(AEO reference case)
Unit
7%
Low estimate
(AEO low growth case)
High estimate
(high growth case)
3%
7%
3%
7%
3,991.8 .....
1,452.1 .....
4,110.9 ....
605.1 .......
3%
Net Benefits
Monetized Value .............
Million 2008$ ...................
1,227.2 ....
3,383.9
2. Direct Heating Equipment
Table V.62 presents a summary of the
impacts for each TSL considered for
DHE.
TABLE V.62—SUMMARY OF RESULTS FOR DIRECT HEATING EQUIPMENT
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Category
TSL 1
National Energy Savings (quads) ............
3% discount rate ...............................
7% discount rate ...............................
NPV of Consumer Benefits (2008$ billion):
3% discount rate ...............................
7% discount rate ...............................
Industry Impacts:
Traditional Direct Heating Equipment:
Industry NPV (2008$ million) ....
Industry NPV (% change) ..........
Gas Hearth Direct Heating Equipment:
Industry NPV (2008$ million) ....
Industry NPV (% change) ..........
Cumulative Emissions Reduction*:
CO2 (Mt) ............................................
NOX (kt) ............................................
Value of Cumulative Emissions Reduction (2008$ million)‡:
CO2—3% discount rate ....................
CO2—7% discount rate ....................
NOX—3% discount rate ....................
NOX—7% discount rate ....................
Mean LCC Savings** (2008$):
Gas Wall Fan ....................................
Gas Wall Gravity ...............................
Gas Floor ..........................................
Gas Room .........................................
Gas Hearth .......................................
Median PBP (years):
Gas Wall Fan ....................................
Gas Wall Gravity ...............................
Gas Floor ..........................................
Gas Room .........................................
Gas Hearth .......................................
Distribution of Consumer LCC Impacts
Gas Wall Fan:
Net Cost (%) ..............................
No Impact (%) ...........................
Net Benefit (%) ..........................
Gas Wall Gravity:
Net Cost (%) ..............................
No Impact (%) ...........................
Net Benefit (%) ..........................
Gas Floor:
Net Cost (%) ..............................
No Impact (%) ...........................
Net Benefit (%) ..........................
Gas Room:
Net Cost (%) ..............................
No Impact (%) ...........................
Net Benefit (%) ..........................
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TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
0.15
0.09
0.04
0.17
0.10
0.05
0.22
0.12
0.06
0.39
0.22
0.11
0.44
0.24
0.12
1.08
0.61
0.31
1.68
0.71
1.87
0.79
2.22
0.91
(0.33)
(0.89)
(0.26)
(0.93)
(2.63)
(3.54)
(0.4)–(1.6)
(2.3)–(9.1)
(0.6)–(3.1)
(3.4)–(17.2)
(1.1)–(6.0)
(5.9)–(33.5)
(1.3)–(7.6)
(7.2)–(42.1)
(1.8)–(8.0)
(10.0)–(44.8)
(2.2)–(10.8)
(12.3)–(60.0)
(0.2)–(0.9)
(0.2)–(1.1)
(0.2)–(0.9)
(0.2)–(1.1)
(0.2)–(0.9)
(0.2)–(1.1)
2.4–(14.8)
2.8–(17.1)
2.4–(14.8)
2.8–(17.1)
10.2–(55.1)
11.8–(63.8)
6.3
5.8
7.0
6.4
8.5
7.7
16.7
15.2
18.5
16.9
43.0
39.6
34.3–377
16.2–178
1.4–14.5
0.7–7.3
38.1–419
18.0–198
1.6–16.1
0.8–8.0
46.2–508
21.8–240
1.9–19.4
0.9–9.7
90.5–996
42.9–472
3.7–38.3
1.9–19.2
100–1,101
47.4–521
4.1–42.5
2.1–21.3
233–2,564
111–1,216
9.7–99.4
4.9–50.0
73
25
13
42
96
90
83
13
96
96
104
192
13
143
96
135
192
13
143
(70)
73
68
13
646
(70)
135
68
13
646
(253)
3.1
8.1
14.7
8.1
0.0
3.9
6.5
14.7
4.9
0.0
6.0
8.3
14.7
5.3
0.0
9.8
8.3
14.7
5.3
25.9
3.1
13.0
14.7
7.0
25.9
9.8
13.0
14.7
7.0
37.5
3
59
38
5
55
41
30
14
56
44
5
52
3
59
38
44
5
52
12
70
18
19
40
41
39
0
61
39
0
61
59
0
41
59
0
41
25
57
18
25
57
18
25
57
18
25
57
18
25
57
18
25
57
18
19
50
31
19
25
56
20
25
55
20
25
55
26
25
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26
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TABLE V.62—SUMMARY OF RESULTS FOR DIRECT HEATING EQUIPMENT—Continued
Category
TSL 1
Gas Hearth:
Net Cost (%) ..............................
No Impact (%) ...........................
Net Benefit (%) ..........................
Generation Capacity Change (GW)*** ....
Employment Impacts:
Total Potential Changes in Domestic
Production Workers in 2013:
Traditional
Direct
Heating
Equipment ..............................
Gas Hearth Direct Heating
Equipment ..............................
Indirect domestic jobs (thousands)***
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
9
51
40
+0.023
9
51
40
+0.025
9
51
40
+0.031
69
13
17
+0.045
69
13
17
+0.049
81
0
19
+0.119
(300)–5
(300)–30
(300)–44
(300)–50
(300)–48
(300)–61
(1,243)–7
0.16
(1,243)–7
0.18
(1,243)–7
0.23
(1,243)–516
0.08
(1,243)–516
0.09
(1,243)–846
0.24
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Parentheses indicate negative (¥) values.
* Hg emissions increase slightly (0.01 to 0.02 t) for the considered TSLs.
** For LCCs, a negative value means an increase in LCC by the amount indicated.
*** Changes in 2042.
‡ Range of the economic value of CO reductions is based on estimates of the global benefit of reduced CO emissions.
2
2
DOE first considered TSL 6, the maxtech level. TSL 6 would save 1.08 quads
of energy, an amount DOE considers
significant. TSL 6 would decrease
consumer NPV by $3.54 billion, using a
discount rate of 7 percent, and by $2.63
billion, using a discount rate of 3
percent.
The emissions reductions at TSL 6 are
43.0 Mt of CO2 and 39.6 kt of NOX. The
estimated monetary value of the
cumulative CO2 emissions reductions at
TSL 6 is $111 to $1,216 million, using
a discount rate of 7 percent, and $233
to $2,564 million, using a discount rate
of 3 percent. Total generating capacity
in 2044 is estimated to increase slightly
under TSL 6.
At TSL 6, DOE projects that the
average LCC impact for consumers is a
gain of $135 for gas wall fan DHE, $68
for gas wall gravity DHE, $13 for gas
floor DHE, $646 for gas room DHE and
a loss of $253 for gas hearth DHE. The
median payback period is 9.8 years for
gas wall fan DHE, 13.0 years for gas wall
gravity DHE, 14.7 years for gas floor
DHE, 7.0 years for gas room DHE and
37.5 for gas hearth DHE (which is
significantly longer than the mean
lifetime of the product). At TSL 6, the
fraction of consumers experiencing an
LCC benefit is 52 percent for gas wall
fan DHE, 41 percent for gas wall gravity
DHE, 18 percent for gas floor DHE, 49
percent for gas room DHE and 19
percent for gas hearth DHE. The fraction
of consumers experiencing an LCC cost
is 44 percent for gas wall fan DHE, 59
percent for gas wall gravity DHE, 25
percent for gas floor DHE, 26 percent for
gas room DHE and 81 percent for gas
hearth DHE.
At TSL 6, the projected change in
INPV ranges from a decrease of up to
$10.8 million for traditional DHE and a
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decrease of up to $55.1 million for gas
hearth DHE, in 2008$. Very few
manufacturers offer products at the
max-tech level for both traditional and
gas hearth DHE. At TSL 6, almost every
manufacturer would face substantial
product and capital conversion costs to
completely redesign most of their
current products and existing
production facilities. In addition, higher
component costs could significantly
harm profitability. If the high end of the
range of impacts is reached as DOE
expects, TSL 6 could result in a net loss
of 60.0 percent in INPV for traditional
DHE and a net loss of 63.8 percent in
INPV for gas hearth DHE. In addition to
the large, negative impacts on INPV at
TSL 6, the required capital and product
conversion costs could cause material
harm to a significant number of small
businesses in both the traditional and
gas hearth DHE market. The conversion
costs could cause many of these small
businesses to exit the market.
The Secretary tentatively concludes
that at TSL 6, the benefits of energy
savings, generating capacity reductions,
and emission reductions would be
outweighed by the negative impacts on
consumer NPV, the economic burden on
some consumers, the large capital
conversion costs that could result in a
large reduction in INPV for the
manufacturers, and the potential
impacts on a significant number of
small businesses. Consequently, the
Secretary has tentatively concluded that
TSL 6 is not economically justified.
Next, DOE considered TSL 5. TSL 5
would save 0.44 quads of energy, an
amount DOE considers significant. TSL
5 would decrease consumer NPV by
$0.93 billion, using a discount rate of 7
percent, and by $0.26 billion, using a
discount rate of 3 percent.
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The emissions reductions at TSL 5 are
18.5 Mt of CO2 and 16.9 kt of NOX. The
estimated monetary value of the
cumulative CO2 emissions reductions at
TSL 5 is $47.4 to $521 million, using a
discount rate of 7 percent, and $100 to
$1,101 million, using a discount rate of
3 percent. Total generating capacity in
2044 is estimated to increase slightly
under TSL 5.
At TSL 5, DOE projects that the
average LCC impact for consumers is a
gain of $73 for gas wall fan DHE, $68 for
gas wall gravity DHE, $13 for gas floor
DHE, $646 for gas room DHE and a loss
of $70 for gas hearth DHE. The median
payback period is 3.1 years for gas wall
fan DHE, 13.0 years for gas wall gravity
DHE, 14.7 years for gas floor DHE, 7.0
years for gas room DHE, and 25.9 for gas
hearth DHE. At TSL 5, the fraction of
consumers experiencing an LCC benefit
is 38 percent for gas wall fan DHE, 41
percent for gas wall gravity DHE, 18
percent for gas floor DHE, 49 percent for
gas room DHE, and 17 percent for gas
hearth DHE. The fraction of consumers
experiencing an LCC cost is 3 percent
for gas wall fan DHE, 59 percent for gas
wall gravity DHE, 25 percent for gas
floor DHE, 26 percent for gas room DHE,
and 69 percent for gas room DHE.
At TSL 5, the projected change in
INPV ranges from a decrease of up to $8
million for traditional DHE and a
decrease of up to $15 million for gas
hearth DHE, in 2008$. While some
manufacturers offer a limited number of
products at TSL 5, most of the current
products would have to be redesigned to
meet the required efficiencies at TSL 5.
In addition, higher component costs for
both traditional and gas hearth DHE
could significantly harm profitability. If
the high end of the range of impacts is
reached as DOE expects, TSL 5 could
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Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
result in a net loss of 44.8 percent in
INPV for traditional DHE and a net loss
of 17.1 percent in INPV for gas hearth
DHE. In addition to the large, negative
impacts on INPV at TSL 5, the required
capital and product conversion costs
could cause material harm to a
significant number of small businesses
in both the traditional and gas hearth
DHE market. These manufacturers could
be forced to discontinue many of their
existing product lines and, possibly, exit
the market altogether.
The Secretary tentatively concludes
that at trial standard level 5, the benefits
of energy savings, generating capacity
reductions, and emission reductions
would be outweighed by the negative
impacts on consumer NPV, the
economic burden on some consumers,
the large capital conversion costs that
could result in a large reduction in INPV
for the manufacturers, and the potential
for small businesses to have to reduce
or discontinue a significant number of
their product lines. Consequently, the
Secretary has tentatively concluded that
trial standard level 5 is not
economically justified.
Next, DOE considered TSL 4. TSL 4
would save 0.39 quads of energy, an
amount DOE considers significant. TSL
4 would provide a NPV of consumer
benefit of $0.89 billion, using a discount
rate of 7 percent, and $0.33 billion,
using a discount rate of 3 percent.
The emissions reductions at TSL 4 are
16.7 Mt of CO2 and 15.2 kt of NOX. The
estimated monetary value of the
cumulative CO2 emissions reductions at
TSL 4 is $42.9 to $472 million, using a
discount rate of 7 percent, and $90.5 to
$996 million, using a discount rate of 3
percent. Total generating capacity in
2044 is estimated to increase slightly
under TSL 4.
At TSL 4, DOE projects that the
average LCC impact for consumers is a
gain of $73 for gas wall fan DHE, $68 for
gas wall gravity DHE, $13 for gas floor
DHE, $646 for gas room DHE, and a loss
of $70 for gas hearth DHE. The median
payback period is 9.8 years for gas wall
fan DHE, 8.3 years for gas wall gravity
DHE, 14.7 years for gas floor DHE, 5.3
years for gas room DHE and 25.9 years
for gas hearth DHE (which is
significantly beyond the mean lifetime
of the equipment). At TSL 4, the fraction
of consumers experiencing an LCC
benefit is 52 percent for gas wall fan
DHE, 61 percent for gas wall gravity
DHE, 18 percent for gas floor DHE, 55
percent for gas room DHE, and 17
percent for gas hearth DHE. The fraction
of consumers experiencing an LCC cost
is 44 percent for gas wall fan DHE, 39
percent for gas wall gravity DHE, 25
percent for gas floor DHE, 20 percent for
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gas room DHE and 69 percent for gas
hearth DHE.
At TSL 4, the projected change in
INPV ranges from a decrease of up to $8
million for traditional DHE and decrease
of up to $15 million for gas hearth DHE.
While some manufacturers offer a
limited number of products at TSL 4,
most of the current products would
have to be redesigned to meet the
required efficiencies at TSL 4. In
addition, higher component costs for
both traditional and gas hearth DHE
could significantly harm profitability. If
the high end of the range of impacts is
reached as DOE expects, TSL 4 could
result in a net loss of 42.1 percent in
INPV for traditional DHE and a net loss
of 17.1 percent in INPV for gas hearth
DHE. In addition to the large, negative
impacts on INPV at TSL 4, the required
capital and product conversion costs
could cause material harm to a
significant number of small businesses
in both the traditional and gas hearth
DHE market. These manufacturers could
be forced to reduce their product
offerings to remain competitive.
The Secretary tentatively concludes
that at trial standard level 4, the benefits
of energy savings, generating capacity
reductions, and emission reductions
would be outweighed by the negative
impacts on consumer NPV, the
economic burden on some consumers,
the large capital conversion costs that
could result in a large reduction in INPV
for the manufacturers, and the potential
for small businesses of DHE to reduce
their product offerings. Consequently,
the Secretary has tentatively concluded
that trial standard level 4 is not
economically justified.
Next, DOE considered TSL 3. TSL 3
would save 0.22 quads of energy, an
amount DOE considers significant. TSL
3 would provide a NPV of consumer
benefit of $0.91 billion, using a discount
rate of 7 percent, and $2.22 billion,
using a discount rate of 3 percent.
The emissions reductions at TSL 3 are
8.5 Mt of CO2 and 7.7 kt of NOX. The
estimated monetary value of the
cumulative CO2 emissions reductions at
TSL 3 is $21.8 to $240 million, using a
discount rate of 7 percent, and $46.2 to
$508 million, using a discount rate of 3
percent. Total electric generating
capacity in 2044 is estimated to increase
slightly under TSL 3.
At TSL 3, DOE projects that the
average LCC impact for consumers is a
gain of $104 for gas wall fan DHE, $192
for gas wall gravity DHE, $13 for gas
floor DHE, $143 for gas room DHE, and
$96 for gas hearth DHE. The median
payback period is 6.0 years for gas wall
fan DHE, 8.3 years for gas wall gravity
DHE, 14.7 years for gas floor DHE, 5.3
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65973
years for gas room DHE, and 0.0 years
for gas hearth DHE. At TSL 3, the
fraction of consumers experiencing an
LCC benefit is 56 percent for gas wall
fan DHE, 61 percent for gas wall gravity
DHE, 18 percent for gas floor DHE, 55
percent for gas room DHE, and 40
percent for gas hearth DHE. The fraction
of consumers experiencing an LCC cost
is 30 percent for gas wall fan DHE, 39
percent for gas wall gravity DHE, 25
percent for gas floor DHE, 20 percent for
gas room DHE, and 9 percent for gas
hearth DHE.
At TSL 3, the projected change in
INPV ranges from a decrease of up to $6
million for traditional DHE and decrease
of up to $1 million for gas hearth DHE.
Most traditional direct heating
manufacturers have existing products
that meet the efficiencies required at
TSL 3 in three out of four product
categories. The impacts on gas hearth
manufacturers are less significant at TSL
3 because manufacturers offer a wide
range of product lines that meet the
required efficiencies at TSL 3 and most
products that do not meet TSL 3 could
be upgraded with inexpensive
purchased parts and fairly small
conversion costs. If the high end of the
range of impacts is reached, TSL 3 could
result in a net loss of 33.5 percent in
INPV for traditional DHE and a net loss
of 1.1 percent in INPV for gas hearth
DHE. In addition, the required capital
and product conversion costs faced by
small businesses decrease, mitigating
the potential harm to a significant
number of small businesses.
After considering the analysis,
comments on the January 13, 2009,
notice and the preliminary TSD, and the
benefits and burdens of TSL 3, the
Secretary tentatively concludes that this
trial standard level will offer the
maximum improvement in efficiency
that is technologically feasible and
economically justified, and will result
in significant conservation of energy.
Further, benefits from carbon dioxide
reductions (at a central value of $20)
would increase NPV by between $21.8
million and $240 million (2008$) at a
7% discount rate and between $46.2
million and $508 million at a 3%
discount rate. These benefits from
carbon dioxide emission reductions,
when considered in conjunction with
the consumer savings NPV and other
factors described above support DOE’s
tentative conclusion that trial standard
level 3 is economically justified.
Therefore, the Department today
proposes to adopt the energy
conservation standards for DHE at TSL
3, as shown in Table V.63.
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Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
TABLE V.63—PROPOSED MINIMUM AFUE REQUIREMENTS FOR DIRECT HEATING EQUIPMENT (TSL 3)
Annual fuel
utilization efficiency
%
Direct heating equipment design type
Product class input capacity range
Btu/h
Gas wall fan ..............................................
up to 42,000 .................................................................................................................
over 42,000 ..................................................................................................................
up to 27,000 .................................................................................................................
over 27,000 and up to 46,000 .....................................................................................
over 46,000 ..................................................................................................................
up to 37,000 .................................................................................................................
over 37,000 ..................................................................................................................
up to 20,000 .................................................................................................................
over 20,000 and up to 27,000 .....................................................................................
over 27,000 and up to 46,000 .....................................................................................
over 46,000 ..................................................................................................................
up to 20,000 .................................................................................................................
over 20,000 and up to 27,000 .....................................................................................
over 27,000 and up to 46,000 .....................................................................................
over 46,000 ..................................................................................................................
Gas wall gravity ........................................
Gas floor ...................................................
Gas room ..................................................
Gas hearth ................................................
DOE also calculated the annualized
values for certain benefits and costs
under the considered TSLs. The
annualized values refer to consumer
operating cost savings, consumer
incremental product and installation
costs, the quantity of emissions
reductions for CO2, NOX, and Hg, and
the monetary value of CO2 emissions
reductions (using a value of $20/t CO2,
which is in the middle of the values
considered by DOE for valuing the
potential global benefits resulting from
reduced CO2 emissions).
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 for the time-series of costs and
benefits using a discount rate of either
three or seven percent. From the present
value, DOE then calculated the fixed
annual payment over the analysis time
period (2013 to 2043 for DHE) that
76
77
70
71
72
57
58
62
67
68
69
61
66
67
68
yielded 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 are a steady stream of
payments. Table V.64 presents the
annualized values for each TSL
considered for DHE.
TABLE V.64—ANNUALIZED BENEFITS AND COSTS FOR DIRECT HEATING EQUIPMENT BY TRIAL STANDARD LEVEL
TSL
Category
Primary Estimate
(AEO reference case)
Unit
7%
Low Estimate
(AEO low growth case)
3%
High Estimate
(AEO high growth case)
7%
3%
7%
3%
93.5
115.5
100.7
125.0
Benefits
1 ........
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
97.7
121.1
CO2 (Mt) ....................
0.18
0.20
0.32
0.34
0.10
0.11
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
0.16
(0.000)
6.1
0.18
(0.000)
7.2
0.27
(0.000)
0.5
0.28
(0.001)
0.5
0.10
(0.000)
15.4
0.12
(0.000)
29.0
28.1
27.4
28.1
27.4
65.8
88.7
88.0
126.5
104.1
128.9
112.2
139.3
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
28.1
27.4
Net Benefits
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Monetized Value .......
Million 2008$ .............
75.7
100.9
Benefits
2 ........
Monetized .................
Operating Cost Savings.
Quantified Emissions
Reductions.
Million 2008$ .............
108.8
135.0
22:35 Dec 10, 2009
0.20
0.22
0.35
0.37
0.11
0.12
NOX (kt) ....................
Hg (t) .........................
VerDate Nov<24>2008
CO2 (Mt) ....................
0.18
(0.000)
0.20
(0.000)
0.30
(0.000)
0.32
(0.001)
0.11
(0.000)
0.13
(0.000)
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65975
TABLE V.64—ANNUALIZED BENEFITS AND COSTS FOR DIRECT HEATING EQUIPMENT BY TRIAL STANDARD LEVEL—
Continued
TSL
Category
Primary Estimate
(AEO reference case)
Unit
7%
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
Low Estimate
(AEO low growth case)
3%
6.7
7%
8.1
3%
High Estimate
(AEO high growth case)
7%
3%
0.8
0.9
25.3
46.4
31.3
30.5
31.3
30.5
73.6
99.3
106.1
155.2
126.4
156.9
136.2
169.6
Costs
Monetized .................
Incremental Product
and Installation
Costs.
Million 2008$ .............
31.3
30.5
Net Benefits
Monetized Value .......
Million 2008$ .............
84.2
112.6
Benefits
3 ........
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
132.2
164.4
CO2 (Mt) ....................
0.24
0.27
0.43
0.46
0.13
0.14
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
0.22
(0.000)
8.2
0.24
(0.001)
9.8
0.36
(0.000)
2.5
0.38
(0.001)
2.9
0.14
(0.000)
21.0
0.15
(0.000)
42.6
41.8
40.6
41.8
40.6
87.1
119.2
115.4
171.6
239.6
297.0
257.9
320.7
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
41.8
40.6
Net Benefits
Monetized Value .......
Million 2008$ .............
98.5
133.5
Benefits
4 ........
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
250.4
310.9
CO2 (Mt) ....................
0.48
0.52
0.85
0.89
0.32
0.36
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
0.43
0.001
16.1
0.48
0.000
19.2
0.71
(0.003)
3.0
0.75
(0.004)
3.5
0.32
(0.000)
17.7
0.36
0.000
39.5
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
337.8
329.1
337.8
329.1
337.8
329.1
(95.2)
(28.6)
(62.2)
31.1
267.3
331.8
287.7
358.3
Net Benefits
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Monetized Value .......
Million 2008$ .............
(71.3)
1.0
Benefits
5 ........
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Million 2008$ .............
279.4
347.3
22:35 Dec 10, 2009
0.53
0.58
0.93
0.99
0.35
0.40
NOX (kt) ....................
Hg (t) .........................
VerDate Nov<24>2008
CO2 (Mt) ....................
0.48
0.001
0.53
0.000
0.79
(0.003)
0.83
(0.004)
0.35
(0.000)
0.40
0.000
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TABLE V.64—ANNUALIZED BENEFITS AND COSTS FOR DIRECT HEATING EQUIPMENT BY TRIAL STANDARD LEVEL—
Continued
TSL
Category
Primary Estimate
(AEO reference case)
Unit
7%
Monetized Avoided
CO2 Value (at $19/
t).
3%
17.8
Million 2008$ .............
Low Estimate
(AEO low growth case)
7%
21.2
3%
High Estimate
(AEO high growth case)
7%
3%
4.1
4.7
65.3
152.0
371.6
361.8
371.6
361.8
(100.1)
(25.3)
(18.6)
148.5
656.6
811.8
707.9
878.5
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
371.6
361.8
Net Benefits
Monetized Value .......
Million 2008$ .............
(74.5)
6.7
Benefits
6 ........
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
686.8
850.9
CO2 (Mt) ....................
1.24
1.35
2.21
2.33
0.81
0.92
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
1.13
0.001
41.5
1.23
0.001
49.4
1.87
(0.007)
8.6
1.98
(0.011)
10.0
0.82
(0.000)
74.7
0.93
0.000
181.1
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
1,036.2
997.3
1,036.2
997.3
1,036.2
997.3
(371.0)
(175.6)
(253.5)
62.3
Net Benefits
Monetized Value .......
Million 2008$ .............
3. Pool Heaters
Table V.65 presents a summary of the
energy savings and economic impacts
(307.9)
(97.0)
for each TSL considered for pool
heaters.
TABLE V.65—SUMMARY OF RESULTS FOR POOL HEATERS
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Category
TSL 1
National Energy Savings (quads) ............
3% discount rate ...............................
7% discount rate ...............................
NPV of Consumer Benefits (2008$ billion):
3% discount rate ...............................
7% discount rate ...............................
Industry Impacts:
Industry NPV (2008$ million) ............
Industry NPV (% change) .................
Cumulative Emissions Reduction*:
CO2 (Mt) ............................................
NOX (kt) ............................................
Value of Cumulative Emissions Reduction (2008$ million) ‡:
CO2—3% discount rate ....................
CO2—7% discount rate ....................
NOX—3% discount rate ....................
NOX—7% discount rate ....................
Mean LCC Savings** (2008$) .................
Median PBP (years) .................................
Distribution of Consumer LCC Impacts:
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TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
0.02
0.01
0.00
0.03
0.02
0.01
0.08
0.05
0.03
0.10
0.06
0.03
0.13
0.08
0.04
0.28
0.16
0.09
0.16
0.08
0.18
0.07
0.40
0.14
0.25
0.03
(1.97)
(1.27)
(4.51)
(2.94)
0.1–(0.2)
0.1–(0.3)
0.4–(1.0)
0.7–(1.7)
(0.2)–(5.6)
(0.4)–(9.1)
0.5–(7.5)
0.9–(12.1)
3.1–(19.5)
5.0–(31.8)
12.9–(44.5)
21.0–(72.6)
0.61
0.55
1.05
0.94
3.31
2.98
4.21
3.74
5.74
5.10
12.12
10.77
3.3 to 36
1.6 to 18
0.1 to 1.4
0.1 to 0.7
24
2.5
5.7 to 63
2.8 to 31
0.2 to 2.4
0.1 to 1.3
18
7.4
18 to 197
8.9 to 97
0.7 to 7.7
0.4 to 4.0
39
10.6
23 to 251
11 to 123
0.9 to 9.7
0.5 to 5.0
(13)
13.0
31 to 342
15 to 168
1.3 to 13.2
0.7 to 6.9
(555)
28.6
66 to 723
33 to 354
2.7 to 27.8
1.4 to 14.5
(1,323)
28.1
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65977
TABLE V.65—SUMMARY OF RESULTS FOR POOL HEATERS—Continued
Category
TSL 1
Net Cost (%) .....................................
No Impact (%) ...................................
Net Benefit (%) .................................
Generation Capacity Change (GW)*** ....
Employment Impacts:
Total Potential Changes in Domestic
Production Workers in 2013 .........
Indirect domestic jobs (thousands)***
TSL 2
TSL 3
TSL 4
TSL 5
TSL 6
6
64
30
+ 0.002
31
46
22
+ 0.004
52
24
24
+ 0.011
59
22
20
+ 0.012
90
6
5
+ 0.016
96
1
3
+ 0.034
(644)–13
3.32
(644)–34
4.38
(644)–66
6.70
(644)–93
8.49
(644)–163
50.59
(644)–331
14.82
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Parentheses indicate negative (¥) values.
* The impacts for Hg emissions are negligible (less than 0.01 ton).
** For LCCs, a negative value means an increase in LCC by the amount indicated.
*** Changes in 2042.
‡ Range of the economic value of CO reductions is based on estimates of the global benefit of reduced CO emissions.
2
2
DOE first considered TSL 6, the maxtech level. TSL 6 would save 0.28 quads
of energy, an amount DOE considers
significant. TSL 6 would decrease
consumer NPV by $2.9 billion, using a
discount rate of 7 percent, and by $4.5
billion, using a discount rate of 3
percent.
The emissions reductions at TSL 6 are
12.1 Mt of CO2 and 10.8 kt of NOX. The
estimated monetary value of the
cumulative CO2 emissions reductions at
TSL 6 is $33 million to $354 million,
using a discount rate of 7 percent, and
$66 million to $723 million, using a
discount rate of 3 percent. Total
generating capacity in 2044 is estimated
to increase slightly under TSL 6.
At TSL 6, DOE projects that the
average LCC impact for consumers is a
loss of $1,323. The median payback
period is 28.1 years (which is
substantially longer than the mean
lifetime of the product). At TSL 6, the
fraction of consumers experiencing an
LCC benefit is 3 percent. The fraction of
consumers experiencing an LCC cost is
96 percent.
At TSL 6, the projected change in
INPV to decrease by up to $44.5 million
for gas-fired pool heaters. Currently, gasfired pool heaters that meet the
efficiencies required by TSL 6 are
manufactured in extremely low volumes
by a limited number of manufacturers.
The significant impacts on
manufacturers arise from the large costs
to develop or increase the production of
fully condensing products. In addition,
manufacturers are significantly harmed
if profitability is negatively impacted to
keep consumers in the market for a
luxury item that is significantly more
expensive than most products currently
sold. If the high end of the range of
impacts is reached as DOE expects, TSL
6 could result in a net loss of 72.6
percent in INPV for gas-fired pool
heaters.
The Secretary tentatively concludes
that at TSL 6, the benefits of energy
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savings and emission reductions would
be outweighed by the negative economic
impacts to the Nation, the economic
burden on some consumers (as
indicated by the large increase in total
installed cost), and the large capital
conversion costs that could result in a
large reduction in INPV for the
manufacturers. Consequently, the
Secretary has tentatively concluded that
TSL 6 is not economically justified.
Next, DOE considered TSL 5. TSL 5
would save 0.13 quads of energy, an
amount DOE considers significant. TSL
5 would decrease consumer NPV by
$1.3 billion, using a discount rate of 7
percent, and by $2.0 billion, using a
discount rate of 3 percent.
The emissions reductions at TSL 5 are
5.7 Mt of CO2 and 5.1 kt of NOX. The
estimated monetary value of the
cumulative CO2 emissions reductions at
TSL 5 is $15 million to $168 million,
using a discount rate of 7 percent, and
$31 million to $342 million, using a
discount rate of 3 percent. Total
generating capacity in 2044 is estimated
to increase slightly under TSL 5.
At TSL 5, DOE projects that the
average LCC impact for consumers is a
loss of $555. The median payback
period is 28.6 years (which is
substantially longer than the mean
lifetime of the product). At TSL 5, the
fraction of consumers experiencing an
LCC benefit is 5 percent. The fraction of
consumers experiencing an LCC cost is
90 percent.
At TSL 5, the projected change in
INPV to decrease by up to $19.5 million
for gas-fired pool heaters. Currently, gasfired pool heaters that meet the
efficiencies required by TSL 5 are
manufactured in extremely low volumes
by a limited number of manufacturers,
as with TSL 6. The significant adverse
impacts on manufacturers arise from the
large costs to develop or increase the
production of products with multiple
efficiency improvements. In addition,
the potential for manufacturers to be
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significantly harmed increases if
consumers purchasing decisions are
impacted and shipments decline due to
the large increases in first cost for a
luxury item. If the high end of the range
of impacts is reached as DOE expects,
TSL 5 could result in a net loss of 31.8
percent in INPV for gas-fired pool
heaters.
The Secretary tentatively concludes
that at TSL 5, the benefits of energy
savings and emission reductions would
be outweighed by the negative economic
impacts to the Nation, the economic
burden on some consumers (as
indicated by the large increase in total
installed cost), and the large capital
conversion costs that could result in a
large reduction in INPV for the
manufacturers. Consequently, the
Secretary has tentatively concluded that
TSL 5 is not economically justified.
Next, DOE considered TSL 4. TSL 4
would save 0.10 quads of energy, an
amount DOE considers significant. TSL
4 would increase consumer NPV by
$0.03 billion, using a discount rate of 7
percent, and by $0.25 billion, using a
discount rate of 3 percent.
The cumulative emissions reductions
at TSL 4 are 4.2 Mt of CO2 and 3.7 kt
of NOX. The estimated monetary value
of the cumulative CO2 emissions
reductions at TSL 4 is $11 million to
$123 million, using a discount rate of 7
percent, and $23 million to $251
million, using a discount rate of 3
percent. Total generating capacity in
2044 is estimated to increase slightly
under TSL 4.
At TSL 4, the estimated increase in
the installed cost is $335. Because this
increase is substantially balanced by a
decrease in operating costs, DOE
projects that the average LCC impact for
consumers is a loss of $13 (note that this
quantity represents only 0.2 percent of
the average total LCC). The median
payback period is 13.0 years, compared
to a typical product life of 8 years. At
TSL 4, the fraction of consumers
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experiencing an LCC benefit is 20
percent. The fraction of consumers
experiencing a net increase in LCC
(mainly due to having low pool heater
operation) is 59 percent. Of these
consumers, the average net increase in
LCC would be about $172, which is
about 3 percent of the average LCC for
these consumers.
At TSL 4, DOE projects that INPV
decreases by up to $7.5 million for gasfired pool heaters. At TSL 4,
manufacturers believe that profitability
could be harmed in order to keep
consumers in the market for a luxury
item that is more expensive than the
most common products currently sold.
If the high end of the range of impacts
is reached as DOE expects, TSL 4 could
result in a net loss of 12.1 percent in
INPV for gas-fired pool heaters.
After considering the analysis,
comments on the January 13, 2009,
notice and the preliminary TSD, and the
benefits and burdens of TSL 4, the
Secretary tentatively concludes that this
trial standard level will offer the
maximum improvement in efficiency
that is technologically feasible and
economically justified, and will result
in significant conservation of energy.
Further, benefits from carbon dioxide
reductions (at a central value of $20)
would increase NPV by between $11
million and $123 million (2008$) at a
7% discount rate and between $23
million and $251 million at a 3%
discount rate. These benefits from
carbon dioxide emission reductions,
when considered in conjunction with
the consumer savings NPV and other
factors described above support DOE’s
tentative conclusion that trial standard
level 4 is economically justified.
Therefore, the Department today
proposes to adopt the energy
conservation standards for pool heaters
at TSL 4, which requires a thermal
efficiency of 84 percent for gas-fired
pool heaters as shown in Table V.66. As
discussed above, approximately 59
percent of consumers with pool heaters
would experience a life cycle cost from
the proposed standard for pool heaters,
TSL 4. Further, DOE estimates that onequarter of these consumers would
experience LCC of less than 2%.
Although most consumers would
experience some savings or very small
increases in life cycle costs, DOE is
seeking comment regarding the
appropriateness of proposing TSL 4 for
pool heaters since this efficiency level
would increase life-cycle costs for most
consumers. DOE also seeks comment on
its consideration of TSL 3 as an
alternative for the final standard level
for pool heaters. (See Issue 18 under
‘‘Issues on Which DOE Seeks Comment’’
in section VII.E of this NOPR.)
TABLE V.66—PROPOSED MINIMUM
THERMAL EFFICIENCY REQUIREMENTS FOR POOL HEATERS (TSL 4)
Product class
Thermal
efficiency
%
Gas-fired Pool Heaters .............
DOE also calculated the annualized
values for certain benefits and costs
under the considered pool heater TSLs.
The annualized values refer to
consumer operating cost savings,
consumer incremental product and
installation costs, the quantity of
emissions reductions of CO2, NOX, and
Hg, and the monetary value of CO2
emissions reductions (using a value of
$20/t CO2, which is in the middle of the
values considered by DOE for valuing
the potential global benefits resulting
from reduced CO2 emissions).
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 for the time-series of costs and
benefits using a discount rate of either
three or seven percent. From the present
value, DOE then calculated the fixed
annual payment over the analysis time
period (2013 to 2043 for pool heaters)
that yielded 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 costs and benefits
from which the annualized values were
determined are a steady stream of
payments. Table V.67 presents the
annualized values for each TSL
considered for pool heaters.
84
TABLE V.67—ANNUALIZED BENEFITS AND COSTS FOR POOL HEATERS BY TRIAL STANDARD LEVEL
Primary estimate
(AEO reference case)
TSL
Category
Unit
7%
Low estimate
(AEO low growth
case)
High estimate
(AEO high growth
case)
3%
7%
3%
7%
3%
Benefits
1 ................................
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
9.52
10.93
9.10
10.43
9.80
11.26
CO2 (Mt) ....................
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
0.02
0.017
0.000
0.61
0.02
0.018
0.000
0.70
0.02
0.021
(0.000)
0.82
0.03
0.022
(0.000)
0.94
0.01
0.013
(0.000)
0.47
0.01
0.014
0.000
0.54
1.98
2.06
1.98
2.06
1.98
7.86
9.39
8.21
9.82
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
2.06
Net Benefits
Monetized Value .......
Million 2008$ .............
8.07
9.65
Benefits
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TABLE V.67—ANNUALIZED BENEFITS AND COSTS FOR POOL HEATERS BY TRIAL STANDARD LEVEL—Continued
Primary estimate
(AEO reference case)
TSL
Category
Unit
Low estimate
(AEO low growth
case)
High estimate
(AEO high growth
case)
7%
2 ................................
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
3%
7%
3%
7%
3%
Million 2008$ .............
16.35
18.78
15.64
17.92
16.83
19.35
CO2 (Mt) ....................
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
0.03
0.029
0.000
1.06
0.03
0.030
0.000
1.20
0.04
0.036
(0.000)
1.40
0.04
0.038
(0.000)
1.62
0.02
0.023
(0.000)
0.80
0.03
0.024
0.000
0.93
8.66
8.98
8.66
8.98
8.66
8.06
10.88
8.65
11.62
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
8.98
Net Benefits
Monetized Value .......
Million 2008$ .............
8.42
11.33
Benefits
3 ................................
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
50.33
57.83
48.16
55.20
51.79
59.57
CO2 (Mt) ....................
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
0.10
0.091
0.000
3.33
0.11
0.095
0.000
3.80
0.13
0.113
(0.000)
4.42
0.14
0.120
(0.001)
5.10
0.08
0.072
(0.000)
2.55
0.08
0.077
0.000
2.93
35.38
36.72
35.38
36.72
35.38
15.86
24.92
17.62
27.12
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
36.72
Net Benefits
Monetized Value .......
Million 2008$ .............
16.94
26.25
Benefits
4 ................................
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
59.88
68.79
57.29
65.66
61.62
70.86
CO2 (Mt) ....................
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
0.13
0.112
0.000
4.20
0.13
0.119
0.000
4.84
0.16
0.134
(0.000)
5.24
0.17
0.143
(0.001)
6.08
0.09
0.085
(0.000)
3.01
0.10
0.091
0.000
3.47
54.59
56.66
54.59
56.66
54.59
5.88
17.15
7.97
19.74
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
56.66
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Net Benefits
Monetized Value .......
Million 2008$ .............
7.41
19.04
Benefits
5 ................................
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Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
22:35 Dec 10, 2009
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Million 2008$ .............
82.08
94.30
78.54
90.00
84.48
97.14
CO2 (Mt) ....................
NOX (kt) ....................
Hg (t) .........................
0.17
0.153
0.000
0.18
0.162
0.000
0.21
0.183
(0.000)
0.23
0.195
(0.001)
0.12
0.116
(0.000)
0.13
0.124
0.000
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TABLE V.67—ANNUALIZED BENEFITS AND COSTS FOR POOL HEATERS BY TRIAL STANDARD LEVEL—Continued
Primary estimate
(AEO reference case)
TSL
Category
Unit
Low estimate
(AEO low growth
case)
High estimate
(AEO high growth
case)
7%
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
3%
7%
3%
7%
3%
5.72
6.58
7.15
8.25
4.11
4.73
204.15
207.11
204.15
207.11
204.15
(121.42)
(105.90)
(118.52)
(102.28)
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
207.11
Net Benefits
Monetized Value .......
Million 2008$ .............
(119.31)
(103.27)
Benefits
6 ................................
Monetized Operating
Cost Savings.
Quantified Emissions
Reductions.
Monetized Avoided
CO2 Value (at $19/
t).
Million 2008$ .............
174.79
200.78
167.22
191.59
179.91
206.84
CO2 (Mt) ....................
NOX (kt) ....................
Hg (t) .........................
Million 2008$ .............
0.37
0.324
0.000
12.04
0.39
0.343
0.000
13.94
0.45
0.388
(0.001)
15.10
0.48
0.411
(0.002)
17.45
0.26
0.244
(0.000)
8.65
0.27
0.261
0.000
9.98
452.23
464.57
452.23
464.57
452.23
(282.25)
(243.19)
(276.01)
(235.41)
Costs
Monetized Incremental Product and
Installation Costs.
Million 2008$ .............
464.57
Net Benefits
Monetized Value .......
VI. Procedural Issues and Regulatory
Review
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
A. Review Under Executive Order 12866
Section 1(b)(1) of Executive Order
12866, ‘‘Regulatory Planning and
Review,’’ 58 FR 51735 (Oct. 4, 1993),
requires each agency to identify in
writing the market failure or other
problem that it intends to address, and
that warrants agency action (including
where applicable, the failure of private
markets or public institutions), as well
as assess the significance of that
problem, to enable assessment of
whether any new regulation is
warranted. The problems that today’s
proposed 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
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Million 2008$ .............
(277.74)
(237.52)
gathering information and effecting
exchanges of goods and services).
(3) There are external benefits
resulting from improved energy
efficiency of heating products 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 a
‘‘significant regulatory action’’ under
section 3(f)(1) of Executive Order 12866.
Accordingly, section 6(a)(3) of the
Executive Order requires that DOE
prepare a regulatory impact analysis
(RIA) on today’s proposed rule and that
the Office of Information and Regulatory
Affairs (OIRA) in the OMB review this
proposed rule. DOE presented to OIRA
for review the draft proposed rule and
other documents prepared for this
rulemaking, including the RIA, and has
included these documents in the
rulemaking record. They are available
for public review in the Resource Room
of DOE’s Building Technologies
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Program, 950 L’Enfant Plaza, SW., Suite
600, Washington, DC 20024, (202) 586–
2945, between 9:00 a.m. and 4:00 p.m.,
Monday through Friday, except Federal
holidays.
The RIA is contained in the TSD
prepared for the rulemaking. The RIA
consists of: (1) A statement of the
problem addressed by this regulation,
and the mandate for government action;
(2) a description and analysis of the
feasible policy alternatives to this
regulation; (3) a quantitative comparison
of the impacts of the alternatives; and
(4) the national economic impacts of the
proposed standards.
The RIA calculates the effects of
feasible policy alternatives to mandatory
standards for heating products, and
provides a quantitative comparison of
the impacts of the alternatives. DOE
evaluated each alternative in terms of its
ability to achieve significant energy
savings at reasonable costs, and
compared it to the effectiveness of the
proposed rule. DOE analyzed these
alternatives using a series of regulatory
scenarios for the three types of heating
products. It modified the heating
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product NIA models to allow inputs for
these policy alternatives. Of the four
product classes of residential water
heaters subject to proposed standards,
this RIA concerns only gas-fired storage
and electric storage water heaters,
which together represent the majority of
shipments. Of the five product classes of
DHE, this RIA concerns only gas wall
fan DHE and gas hearth DHE, which
• Bulk government purchases;
• Early replacement programs; and
• The proposed approach (energy
conservation standards).
DOE evaluated each alternative in
terms of its ability to achieve significant
energy savings at reasonable costs and
compared it to the effectiveness of the
proposed rule. Table VI.1 through Table
VI.5 show the results for energy savings
and consumer NPV.
together represent the majority of DHE
shipments.
DOE identified the following major
policy alternatives for achieving
increased energy efficiency in the three
types of heating products:
• No new regulatory action;
• Consumer rebates;
• Consumer tax credits;
• Manufacturer tax credits;
• Voluntary energy efficiency targets;
TABLE VI.1—IMPACTS OF NON-REGULATORY ALTERNATIVES FOR GAS-FIRED STORAGE WATER HEATERS THAT MEET THE
PROPOSED STANDARD (TSL 4)
Primary energy
savings
quads
Policy alternative
No New Regulatory Action ......................................................................................
Consumer Rebates ..................................................................................................
Consumer Tax Credits .............................................................................................
Manufacturer Tax Credits ........................................................................................
Voluntary Energy Efficiency Targets .......................................................................
Early Replacement ..................................................................................................
Bulk Government Purchases ...................................................................................
Proposed Standard ..................................................................................................
Net present value*
billion 2008$
7% discount rate
0.00
0.51
0.31
0.15
0.12
0.001
0.005
1.29
3% discount rate
0.00
1.19
0.72
0.36
0.29
¥0.02
0.01
3.09
0.00
3.46
2.08
1.04
0.83
¥0.04
0.04
9.04
* DOE determined the NPV from 2015 to 2045.
TABLE VI.2—IMPACTS OF NON-REGULATORY ALTERNATIVES FOR ELECTRIC STORAGE WATER HEATERS THAT MEET THE
PROPOSED STANDARD (TSL 4)
Primary energy
savings
quads
Policy alternative
No New Regulatory Action ....................................................................................
Consumer Rebates ................................................................................................
Consumer Tax Credits ...........................................................................................
Manufacturer Tax Credits ......................................................................................
Voluntary Energy Efficiency Targets .....................................................................
Early Replacement ................................................................................................
Bulk Government Purchases .................................................................................
Proposed Standard ................................................................................................
Net present value*
billion 2008$
7% discount rate
0.00
0.42
0.25
0.13
0.09
0.0023
0.0017
1.21
3% discount rate
0.00
0.47
0.28
0.14
0.19
¥0.03
0.004
1.59
0.00
1.87
1.12
0.56
0.60
¥0.05
0.01
6.02
* DOE determined the NPV from 2015 to 2045.
TABLE VI.3—IMPACTS OF NON-REGULATORY ALTERNATIVES FOR GAS WALL FAN DHE THAT MEET THE PROPOSED
STANDARD (TSL 3)
Primary energy
savings
quads
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Policy alternative
No New Regulatory Action ..................................................................................
Consumer Rebates ..............................................................................................
Consumer Tax Credits .........................................................................................
Manufacturer Tax Credits ....................................................................................
Voluntary Energy Efficiency Targets ...................................................................
Early Replacement ..............................................................................................
Bulk Government Purchases† .............................................................................
Proposed Standard ..............................................................................................
0.00
0.003
0.002
0.001
0.0003
<0.0001
NA
0.013
Net present value*
billion 2008$
7% discount rate
0.00
0.010
0.006
0.003
0.001
¥0.00001
NA
0.042
3% discount rate
0.00
0.023
0.006
0.003
0.001
¥0.00003
NA
0.11
* DOE determined the NPV from 2013 to 2043.
† DOE did not evaluate the bulk government purchase alternative for gas wall fan DHE because the market share associated with publiclyowned housing is minimal.
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TABLE VI.4—IMPACTS OF NON-REGULATORY ALTERNATIVES FOR GAS HEARTH DHE THAT MEET THE PROPOSED
STANDARD (TSL 3)
Net present value*
billion 2008$
Primary energy
savings
quads
Policy alternative
No New Regulatory Action ..................................................................................
Consumer Rebates ..............................................................................................
Consumer Tax Credits .........................................................................................
Manufacturer Tax Credits ....................................................................................
Voluntary Energy Efficiency Targets ...................................................................
Early Replacement ..............................................................................................
Bulk Government Purchases† .............................................................................
Proposed Standard ..............................................................................................
7% discount rate
0.00
0.03
0.02
0.01
0.012
<0.001
NA
0.14
3% discount rate
0.00
0.15
0.09
0.05
0.06
¥0.005
NA
0. 64
0.00
0.36
0.22
0.11
0.15
¥0.006
NA
1.52
* DOE determined the NPV from 2013 to 2043.
† DOE did not evaluate the bulk government purchase alternative for gas hearth DHE because the market share associated with publiclyowned housing is minimal.
TABLE VI.5—IMPACTS OF NON-REGULATORY ALTERNATIVES FOR POOL HEATERS THAT MEET THE PROPOSED STANDARDS
(TSL 4)
Primary
energy
savings
quads
Policy alternative
No New Regulatory Action ..................................................................................
Consumer Rebates ..............................................................................................
Consumer Tax Credits .........................................................................................
Manufacturer Tax Credits ....................................................................................
Voluntary Energy Efficiency Targets ...................................................................
Early Replacement ..............................................................................................
Bulk Government Purchases † .............................................................................
Proposed Standard ..............................................................................................
Net present value*
billion 2008$
7% discount rate
0.00
0.02
0.01
0.005
0.004
<0.001
NA
0.10
0.00
0.01
0.003
0.002
0.005
¥0.002
NA
0.03
3% discount rate
0.00
0.04
0.03
0.01
0.02
¥0.003
NA
0.25
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* DOE determined the NPV from 2013 to 2043.
† DOE did not evaluate the bulk government purchase alternative for pool heaters because there is no market share associated with publiclyowned housing.
The NPV amounts shown in Table
VI.1 through Table VI.5 refer to the NPV
of consumer benefits. The costs to the
government of each policy (such as
rebates or tax credits) are not included
in the costs for the NPV since, on
balance, consumers in the aggregate
both pay for rebates and tax credits
through taxes and receive their benefits.
The following paragraphs discuss the
cumulative effect of each policy
alternative listed in Table VI.1 through
Table VI.5. (See the regulatory impact
analysis in the NOPR TSD for details.)
For comparison with the results
reported below for the non-regulatory
policies, the combined impacts of the
proposed standards for the considered
products are projected as 2.75 quads of
national energy savings and an NPV of
$5.39 billion (at a 7-percent discount
rate).
No new regulatory action. The case in
which no regulatory action is taken
constitutes the ‘‘base case’’ (or ‘‘no
action’’) scenario. Since this is the base
case, energy savings and NPV are zero
by definition.
Rebates. If consumers were offered a
rebate that covered a portion of the
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incremental price difference between
products meeting baseline efficiency
levels and those meeting the energy
efficiency levels in the proposed
standard, DOE estimates that the
percentage of consumers purchasing the
more-efficient products would increase
by 17.5 percent to 40 percent,
depending on the product and the
product class. DOE assumed this policy
would permanently transform the
market so that the increased percentage
of consumers purchasing more-efficient
products seen in the first year of the
program would be maintained
throughout the forecast period. At the
estimated participation rates, the rebates
would provide 0.98 quads of national
energy savings and an NPV of $1.83
billion (at a 7-percent discount rate) for
the considered products. Although DOE
estimates that rebates would provide
national benefits, they are expected to
be much smaller than the benefits
resulting from the proposed national
standards.
Consumer Tax Credits. If consumers
were offered a tax credit that covered a
portion of the incremental price
difference between products meeting
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baseline efficiency levels and those
meeting the energy efficiency levels in
the proposed standards, DOE’s research
suggests that the number of consumers
buying a water heater, pool heater, or
DHE that would take advantage of the
tax credit would be approximately 60
percent of the number that would take
advantage of rebates. As a result of the
tax credit, the percentage of consumers
purchasing more-efficient products
would increase by 10.5 percent to 24
percent, depending on the product and
product class. Therefore, tax credits
would yield a fraction of the benefits of
rebates. DOE assumed this policy would
permanently transform the market so
that the increased percentage of
consumers purchasing more-efficient
products seen in the first year of the
program would be maintained
throughout the forecast period. At the
estimated participation rates, consumer
tax credits would provide 0.59 quads of
national energy savings and an NPV of
$1.10 billion (at a seven-percent
discount rate) for the considered
products.
Manufacturer Tax Credits. DOE
believes even smaller benefits would
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result from a manufacturer tax credit
program that would effectively result in
a lower price to the consumer by an
amount that covers part of the
incremental price difference between
products meeting baseline efficiency
levels and those meeting the proposed
standards. Because these tax credits
would go to manufacturers instead of
consumers, DOE believes that fewer
consumers would be aware of this
program than a consumer tax credit
program. DOE assumes that 50 percent
of the consumers who would take
advantage of consumer tax credits
would buy more-efficient products
offered through a manufacturer tax
credit program. Thus, as a result of the
manufacturer tax credit, the percentage
of consumers purchasing the moreefficient products would increase by 5.2
percent to 12 percent (i.e., 50 percent of
the impact of consumer tax credits),
depending on the product class.
DOE assumed this policy would
permanently transform the market so
that the increased percentage of
consumers purchasing more-efficient
products seen in the first year of the
program would be maintained
throughout the forecast period. At the
estimated participation rates, the rebates
would provide 0.30 quads of national
energy savings and an NPV of $0.56
billion (at a seven-percent discount rate)
for the considered products. Thus, DOE
estimated that manufacturer tax credits
would yield a fraction of the benefits
that consumer tax credits and rebates
would provide.
Voluntary Energy Efficiency Targets.
The Federal government’s ENERGY
STAR program has voluntary energy
efficiency targets for gas-fired and
electric storage water heaters and gasfired instantaneous water heaters. Some
equipment purchases that result from
the ENERGY STAR program already are
reflected in DOE’s base-case scenario.
DOE evaluated the potential impacts of
increased marketing efforts by ENERGY
STAR that would encourage the
purchase of products meeting the
proposed standard. DOE modeled the
voluntary efficiency program based on
this scenario and assumed that the
resulting increased percentage of
consumers purchasing more-efficient
products would be maintained
throughout the forecast period. DOE
estimated that the enhanced
effectiveness of voluntary energy
efficiency targets would provide 0.23
quads of national energy savings and an
NPV of $0.55 billion (at a 7-percent
discount rate) for the considered
products. Although this would provide
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national benefits, they would be much
smaller than the benefits resulting from
the proposed national standards.
Early Replacement Incentives. This
policy alternative envisions a program
to replace old, inefficient water heaters,
DHE, and pool heaters with models
meeting the efficiency levels in the
proposed standards. DOE projected a 4percent increase in the annual
retirement rate of the existing stock in
the first year of the program. It assumed
the program would last as long as it took
to completely replace all of the eligible
existing stock in the year that the
program begins (2013 or 2015). DOE
estimated that such an early
replacement program would provide
negligible national energy savings and
NPV for the considered products. The
national energy savings benefits would
be negligible in comparison with the
benefits resulting from the proposed
national standards, and the NPV would
actually be negative.
Bulk Government Purchases. Under
this policy alternative, the government
would be encouraged to purchase
increased amounts of equipment that
meet the efficiency levels in the
proposed standards. Federal, State, and
local government agencies could
administer such a program. At the
Federal level, this would be an
enhancement to the existing Federal
Energy Management Program (FEMP).
DOE modeled this program by assuming
an increase in installation of equipment
meeting the efficiency levels of the
proposed standards among those
households for whom government
agencies purchase or influence the
purchase of water heaters. (Because the
market share of DHE units in publiclyowned housing is minimal and the
market share of pool heaters in publiclyowned housing is zero, the Department
did not consider bulk government
purchases for those products.) DOE
estimated that bulk government
purchases would provide negligible
national energy savings (0.01 quads) and
NPV ($0.14 billion) for the considered
products, benefits that are much smaller
than those estimated for the proposed
national standards.
Proposed Standards. DOE proposes to
adopt the efficiency levels listed in
section V.C. As indicated in the
paragraphs above, none of the
alternatives DOE examined would save
as much energy as today’s proposed
standards. Also, several of the
alternatives would require new enabling
legislation because authority to carry
out those alternatives may not exist.
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Additional Policy Evaluation. In
addition to the above non-regulatory
policy alternatives, DOE evaluated the
potential impacts of a policy that would
allow States to require that some water
heaters installed in new homes have an
efficiency level higher than the Federal
standard. At present, States are
prohibited to require efficiency levels
higher than the Federal standard; the
considered policy would remove this
prohibition in the case of residential
water heaters. DOE notes that removing
the prohibition would require either
legislative authority or DOE approval,
after a case-by-case basis consideration
on the merits, of waivers submitted by
States. For the present rulemaking, DOE
evaluated the impacts that such a policy
would have for electric storage water
heaters.
Specifically, DOE estimated the
impacts for a policy case in which
several States adopted provisions in
their building codes that would require
electric storage water heaters to meet
efficiency level 6 (2.0 EF, heat pump
with two-inch insulation). DOE
assumed that such codes would affect
25 percent of water heaters in all new
homes built in the United States in 2015
and that the percentage would increase
linearly to 75 percent by 2045. (DOE did
not attempt to define the specific
geographic areas that would be
affected.) In this policy case, all other
water heaters (those bought for
replacement in existing homes) would
meet the proposed standard level of 0.95
(efficiency level 5). DOE’s analysis
accounts for the estimate that some new
homes would have a water heater with
EF greater than or equal to 2.0 (e.g., heat
pump technology) in the absence of any
amended standards (the base case).
Table VI.6 shows the additional
estimated national energy savings that
would result from the considered
building code policy, as well as the net
present value of additional benefits to
consumers (the purchasers of new
homes that have electric water heaters
that have an EF of at least 2.0). The table
also shows the estimated national
energy savings and NPV for electric
storage water heaters under the
proposed standards. The energy savings
from this State building code
requirement for new homes would be
greater than the savings from the
proposed standard for electric storage
water heaters. This contrasts with the
non-regulatory policy alternatives
discussed above, whose savings are
lower than those of the proposed
standards.
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TABLE VI.6—IMPACTS OF POLICY ALLOWING STATES TO INCORPORATE REQUIREMENTS FOR HIGH-EFFICIENCY ELECTRIC
STORAGE WATER HEATERS IN BUILDING CODES
Policy alternative
Proposed Standard (TSL 4) (Electric Storage Water Heaters) .................................
Proposed Standard (TSL 4) AND Policy Allowing States to Require Higher-Efficiency Electric Storage Water Heaters in New Homes .........................................
B. Review Under the Regulatory
Flexibility Act
The Regulatory Flexibility Act (5
U.S.C. 601 et seq.) requires preparation
of an initial regulatory flexibility
analysis (IRFA) 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
Net present value
billion 2008$
Primary
energy
savings
quads
7% discount
rate
3% discount
rate
1.21
6.02
1.69
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://
www.gc.doe.gov).
For the manufacturers of the three
types of heating products, 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,
30850 (May 15, 2000), as amended at 65
FR 53533, 53545 (September 5, 2000)
1.59
2.13
8.33
and codified at 13 CFR part 121.The size
standards are listed by North American
Industry Classification System (NAICS)
code and industry description and are
available at https://www.sba.gov/idc/
groups/public/documents/
sba_homepage/serv_sstd_tablepdf.pdf.
Residential water heater and pool heater
manufacturing are classified under
NAICS 335228, ‘‘Other Major
Household Appliance Manufacturing’’
and DHE is classified under NAICS
333414, ‘‘Heating Equipment (except
warm air furnaces) Manufacturing.’’ The
SBA sets a threshold of 500 employees
or less for an entity to be considered as
a small business for both of these
categories as shown in Table VI.7.
TABLE VI.7—SBA AND NAICS CLASSIFICATION OF SMALL BUSINESSES POTENTIALLY AFFECTED BY THIS RULE
Industry description
Revenue limit
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Residential Water Heater Manufacturing ..................................................................
Direct Heating Manufacturing ....................................................................................
Pool Heater Manufacturing ........................................................................................
DOE reviewed the potential standard
levels considered in today’s NOPR
under the provisions of the Regulatory
Flexibility Act and the procedures and
policies published on February 19,
2003. To better assess the potential
impacts of this rulemaking on small
entities, DOE conducted a more focused
inquiry of the companies that could be
small business manufacturers of
products covered by this rulemaking.
During its market survey, DOE used all
available public information to identify
potential small manufacturers. DOE’s
research involved several industry trade
association membership directories
(including AHRI, HPBA, and APSP),
product databases (e.g., AHRI, CEC, and
ENERGY STAR databases), individual
company Web sites, and marketing
research tools (e.g., Dunn and Bradstreet
reports) to create a list of every company
that manufactures or sells water heaters,
DHE, and gas-fired pool heaters covered
by this rulemaking. DOE also asked
stakeholders and industry
representatives if they were aware of
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N/A
N/A
N/A
any other small manufacturers during
manufacturer interviews and at previous
DOE public meetings. DOE reviewed all
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 water heaters, DHE, and pool
heaters. DOE screened out companies
that did not offer products covered by
this rulemaking, did not meet the
definition of a ‘‘small business,’’ or are
foreign owned and operated. Ultimately,
DOE identified five small residential
water heater manufacturers, 12 small
DHE manufacturers, and one small pool
heater manufacturer that produce
covered products and can be considered
small businesses. Next, DOE attempted
to contact these potential small business
manufacturers to request an interview
about the possible impacts on small
business manufacturers. The results of
discussions with manufacturers are set
forth below. From these discussions,
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Employee limit
500
500
500
NAICS
335228
333414
335228
DOE determined the expected impacts
of the rule on affected small entities.
DOE looked at each type of heating
product (water heaters, pool heaters,
and direct heating) separately for
purposes of determining whether
certification was appropriate or an
initial regulatory flexibility analysis was
needed.
1. Water Heater Industry
The majority of residential water
heaters are currently manufactured in
the United States. Three large
manufacturers control the
overwhelming majority of storage water
heater sales. Many foreign-owned and
foreign-operated manufacturers of
instantaneous gas-fired water heaters
offer products for sale in the United
States and make up part of the
remaining domestic residential water
heater market. A very small portion of
the remaining residential water heater
market is supplied by a combination of
international and domestic companies,
all of which have less than a one-
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percent total market share. Part of the
remaining market is also supplied by
domestic companies that focus
primarily on commercial, niche, or
other products, but also manufacture
residential water heaters that are
covered by this rulemaking.
DOE identified five domestic small
businesses that manufacture residential
water heaters. Each company’s product
offerings were examined to help
determine the potential impact of
amended energy conservation
standards.
Only one of the small businesses
identified by DOE manufactures
primarily products that are covered by
this rulemaking. This company offers
two gas-fired instantaneous water
heaters and is also developing a heat
pump water heater. The products
offered by this manufacturer are
expected to meet the ENERGY STAR
criteria for residential water heaters and
to achieve efficiencies higher than the
levels being proposed in this NOPR.
Therefore, DOE believes that none of the
products offered by this manufacturer
would be impacted by the proposed
energy conservation standards for
residential water heaters.
Three of the small businesses
identified by DOE manufacture covered
oil-fired residential water heaters, but
focus mainly on other products. One of
these three small businesses holds a
significant portion of the residential oilfired water heater market. The products
offered by this manufacturer exceed the
efficiencies of the proposed standard
levels for residential oil-fired storage
water heaters. Therefore, DOE does not
believe that the products offered by this
manufacturer would be impacted by the
proposed energy conservation standards
for residential water heaters. The two
other two small businesses that
manufacture residential oil-fired storage
water heaters both have a lower market
share and collectively ship fewer than
5,000 units per year. The first of these
companies with low market share offers
one residential oil-fired water heater
model, but it would not need to be
upgraded at the proposed energy
conservation standard level. In addition,
this manufacturer specializes in
products outside of the scope of
coverage for this rulemaking (e.g.,
commercial gas-fired storage water
heaters, indirect water heaters,
commercial electric storage water
heaters, storage tanks, and boilers). The
other company with low market share in
the residential oil-fired market offers
seven different oil-fired storage water
heater models. However, this company
does not certify these products on
public databases and does not provide
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information about the input capacity or
efficiency in its product literature,
making it difficult to determine whether
these are commercial or residential
products and if they would need to be
upgraded in response to the proposed
energy conversation standards.
However, from a review of the company
Web site, DOE believes this
manufacturer is also focused mostly on
non-covered products.
The final small manufacturer of
residential water heaters has a full line
of residential electric storage water
heaters that would need to be upgraded
or, possibly, discontinued in response to
the proposed energy conservation
standards. Depending on the importance
of this residential line, this small
business could exit the residential
electric storage market rather than
invest in the changes necessary to
upgrade and recertify its existing
electric storage products. However, this
manufacturer has less than a onepercent market share in the residential
storage water heater market. Product
certification databases and the company
Web site also indicate that this
manufacturer focuses primarily on
commercial water heaters and other
non-covered products including indirect
water heaters and boilers. Because of its
focus on non-covered products, it is
unlikely that this small business would
be forced out of business in response to
the proposed energy conservation
standards.
Because only one small manufacturer
with very low market share in the
electric storage water heater market and
potentially one small business with very
low market share in the residential oilfired market would potentially be
impacted by the proposed energy
conservation standards in today’s rule,
DOE certifies that the standards for
water heaters set forth in the proposed
rule, if promulgated, would not have a
significant economic impact on a
substantial number of small entities.
Accordingly, DOE has not prepared a
regulatory flexibility analysis for the
water heaters portion of this
rulemaking. DOE will transmit the
certification and supporting statement
of factual basis to the Chief Counsel for
Advocacy of the Small Business
Administration for review under 5
U.S.C. 605(b).
DOE requests comment on the above
analysis, as well as any information
concerning small businesses that could
be impacted by this rulemaking and the
nature and extent of those potential
impacts of the proposed energy
conservation standards on small
residential water heater manufacturers.
(See Issue 19 under ‘‘Issues on Which
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65985
DOE Seeks Comment’’ in section VII.E
of this NOPR.)
2. Pool Heater Industry
The vast majority of residential pool
heaters are currently manufactured in
the United States. Four manufacturers
supply over 95 percent of the market.
Based on its market research, DOE
identified only one small manufacturer
of residential gas-fired pool heaters. The
small manufacturer specializes in highefficiency products that exceed the
proposed energy conservation standard
level, and, therefore, DOE does not
believe the products offered by this
manufacturer would be impacted by the
proposed amended energy conservation
standards for residential pool heaters.
Additionally, this small business
manufacturer has a very low share of the
residential gas-fired pool heater market.
Because only one small business
manufacturer of residential gas-fired
pool heaters with small market share
exists and because this company’s
product exceeds the proposed energy
conservation standard levels, DOE
certifies that the standards for pool
heaters set forth in the proposed rule, if
promulgated, would not have a
significant economic impact on a
substantial number of small entities in
the gas-fired pool heater industry.
Accordingly, DOE has not prepared a
regulatory flexibility analysis for the
pool heaters portion of this rulemaking.
DOE will transmit this certification and
supporting statement of factual basis to
the Chief Counsel for Advocacy of the
Small Business Administration for
review under 5 U.S.C 605(b).
DOE requests comment on the above
analysis, as well as any information
concerning small businesses that could
be impacted by this rulemaking and the
nature and extent of those potential
impacts of the proposed energy
conservation standards on small
residential gas-fired pool heater
manufacturers. (See Issue 20 under
‘‘Issues on Which DOE Seeks Comment’’
in section VII.E of this NOPR.)
3. Direct Heating Equipment Industry
Characteristics
As discussed in further detail below,
DOE determined that it cannot certify
that the proposed energy conservation
standard levels for DHE, if promulgated,
would not have a significant economic
impact on a substantial number of small
entities. This determination results from
the large number of small DHE
manufacturers and the expected impact
of the proposed standards on these
manufacturers, as well as the likely
greater impact of the proposed
standards on these small businesses.
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Consequently, DOE has prepared an
IRFA for the direct heating equipment
portion of this rulemaking, a copy of
which DOE will transmit to the Chief
Counsel for Advocacy of the SBA for
review under 5 U.S.C 605(b). As
presented and discussed below, the
IFRA describes potential impacts on
small DHE manufacturers associated
with the required capital and product
conversion costs at each TSL and
discusses alternatives that could
minimize these impacts.
a. Description and Estimated Number of
Small Entities Regulated
After examining structure of the DHE
industry, DOE determined it necessary
to divide potential impacts on small
DHE manufacturers into two broad
categories: (1) Impacts on small
manufacturers of traditional DHE (i.e.,
manufacturers of gas wall fan, gas wall
gravity, gas floor, and gas room DHE);
and (2) impacts on small manufacturers
of gas hearth products. The IRFA
presents the results for traditional DHE
and gas hearth DHE separately to be
consistent with the MIA results in
section V.B.2.b, which also separate
DHE in this manner. Traditional DHE
and gas hearth DHE are made by
different manufacturers (i.e., all
manufacturers of gas hearth products do
not manufacture traditional DHE, and
vice versa, with one exception).
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
i. Traditional Direct Heating Equipment
Three major manufacturers control
almost 100 percent of the traditional
DHE market. Two of the three major
manufacturers of traditional DHE are
small businesses. One of the small
businesses produces only traditional
DHE and has products in all four
traditional DHE product classes (i.e., gas
wall fan, gas wall gravity, gas floor, and
gas room DHE). The second business
produces all five products classes of
DHE, including gas hearth DHE. DOE
identified a third small business with
less than a one-percent share of the
traditional DHE market. This company
offers two gas wall gravity models, but
is mainly focused on specialty hearth
products not covered by this
rulemaking.
ii. Gas Hearth Direct Heating Equipment
DOE identified 10 small
manufacturers of gas hearth DHE. Before
issuing this NOPR, DOE attempted to
contact the small business
manufacturers of gas hearth DHE. One
of the small businesses consented to
being interviewed during the MIA
interviews, and DOE received feedback
from an additional two small businesses
through survey responses. DOE also
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obtained information about small
business impacts while interviewing
manufacturers that exceed the small
business size threshold of 500
employees in this industry. Both small
business manufacturers and large
manufacturers indicated that the
number of competitors in the market has
been declining in recent years due to
industry consolidation and smaller
companies exiting the market. Three
major domestic manufacturers now
supply a majority of the marketplace.
None of the three major manufacturers
is considered a small business. The
remainder of the market is either
imported (mostly by Canadian
companies) or produced by one of 12
domestic manufacturers that hold
varying market shares.
b. Reasons for the Proposed Rule
Title III of EPCA sets forth a variety
of provisions designed to improve
energy efficiency. Part A of Title III (42
U.S.C. 6291–6309) provides for the
‘‘Energy Conservation Program for
Consumer Products Other Than
Automobiles.’’ The program covers
consumer products and certain
commercial equipment, including
residential DHE, and the statute directs
DOE to consider new and amended
energy conservation standards for those
products. (42 U.S.C. 6292(9)) DOE is
proposing in today’s notice to amend
energy conservation standards for DHE,
as required by EPCA. (42 U.S.C.
6295(e)(4))
c. Objectives of, and Legal Basis for, the
Proposed Rule
EPCA provides criteria for prescribing
new or amended standards for covered
products and equipment. (42 U.S.C
6295(o)) As indicated above, any new or
amended standard for the products 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)), although EPCA
precludes DOE from adopting any
standard that would not result in
significant conservation of energy. (42
U.S.C. 6295(o)(3)(B)) Moreover, DOE
may not prescribe a standard: (1) For
certain products, 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)) DOE’s current test
procedures for water heaters, vented
DHE, and pool heaters appear at Title 10
Code of Federal Regulations (CFR) part
430, subpart B, appendices E, O and P,
respectively. EPCA also provides that,
in deciding whether a standard is
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economically justified, DOE must, after
receiving comments on the proposed
standard, determine whether the
benefits of the standard exceed its
burdens by considering to the greatest
extent practicable seven enumerated
factors (described in section II.B above
of the preamble). (42 U.S.C.
6295(o)(2)(B)(i))
EPCA prescribes energy conservation
standards for direct heating products,
(42 U.S.C. 6295(e)(3)) and directs DOE
to conduct two cycles of rulemakings to
determine whether to amend these
standards. (42 U.S.C. 6295(e)(4)) This
rulemaking represents the first round of
amendments to the energy conservation
standards for DHE.
d. Description and Estimate of
Compliance Requirements
i. Traditional Direct Heating Equipment
The number of manufacturers in the
traditional DHE market has declined
over the past decade and leveled off
with three major manufacturers
remaining. While DOE explicitly
analyzed one representative input
capacity range for the gas wall gravity,
gas wall fan, gas floor, and gas room
types of DHE, manufacturers offer
product lines that typically span
multiple BTU ranges with many
different features. This can result in
many individual products, or stock
keeping units (SKUs), offered by each
manufacturer per product line. The
wide range of product offering by
manufacturers is a legacy of a highervolume market that now typically
supplies replacement units. The
remaining manufacturers have stayed in
business by consolidating brands and
the legacy products of companies that
are no longer in business to take
increasing shares of a smaller total
market. Because each product line is
manufactured in low volumes, the
discrepancy between unit shipments
and the number of product lines
requiring significant product and capital
conversion costs results in negative
impacts for all manufacturers. Many
product development costs (e.g., testing,
certification, and marketing) are
somewhat fixed, making manufacturing
scale an important consideration in
determining whether the product
conversion costs are economically
justified. Similarly, even though any
capital conversion costs can be
capitalized over a number of years,
these costs must be paid up front and
have a large enough volume to justify an
added per-unit cost.
DOE calculated its capital and
product conversion costs for traditional
DHE by estimating a per-product-line
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cost and assuming that every
manufacturer would face the same perproduct-line cost within each product
class. DOE also assumed that any
product line that did not meet the
efficiency level being analyzed would
be upgraded, thereby requiring product
conversion and capital conversion costs.
DOE used public data to calculate the
number of product lines that would
need to be upgraded at each TSL for
each product class. To show how the
small businesses could be differentially
harmed, DOE compared the conversion
costs for a typical large manufacturer
and a typical small manufacturer within
the industry. To calculate the
conversion costs for a typical small
manufacturer and a typical large
manufacturer, DOE used publiclyavailable information to determine the
average number of product lines that
met each efficiency level in each
product category for a typical small
65987
manufacturer and a typical large
manufacturer of traditional DHE. For
both small and large, DOE multiplied
the number of product lines that fell
below the required efficiency level by
its estimate of the per-line capital and
product conversion cost. Table VI.8 and
Table VI.9 show DOE’s estimates for the
average number of product lines at each
TSL for a typical small manufacturer
and a typical large manufacturer of
traditional DHE, respectively.
TABLE VI.8—NUMBER OF PRODUCT LINES OF A TYPICAL SMALL MANUFACTURER
Number of gas wall
fan-type product
lines at each TSL
Number of gas wall
gravity-type product
lines at each TSL
2
0
1
0.5
1
0
1
*1.5
1
0.5
0
0
1
1
Baseline .......................................
TSL 1 ...........................................
TSL 2 ...........................................
TSL 3 ...........................................
TSL 4 ...........................................
TSL 5 ...........................................
TSL 6 ...........................................
Number of gas
floor-type product
lines at each TSL
Number of gas
room-type product
lines at each TSL
0.5
0.5
0.5
0.5
0.5
0.5
0.5
Total product lines
for all product
classes
1
0.5
0.5
0
0
0
0
5
2
2.5
1
1.5
1.5
2.5
* Fractions of product lines result from taking the average number of product lines from publicly-available information.
TABLE VI.9—NUMBER OF PRODUCT LINES OF TYPICAL LARGE MANUFACTURER
Number of gas wall
fan-type product
lines at each TSL
Number of gas wall
gravity-type product
lines at each TSL
1
1
2
2
0
1
0
0
1
3
0
0
0
0
Baseline .......................................
TSL 1 ...........................................
TSL 2 ...........................................
TSL 3 ...........................................
TSL 4 ...........................................
TSL 5 ...........................................
TSL 6 ...........................................
Amended energy conservation
standards have the potential to
differentially affect the small
businesses, because they generally lack
the large-scale resources to alter their
existing products and production
facilities for those TSLs requiring major
redesigns. While all manufacturers
would be expected to be negatively
impacted by amended energy
Number of gas
floor-type product
lines at each TSL
Number of gas
room-type product
lines at each TSL
1
1
1
1
1
1
1
conservation standards to varying
degrees, the small businesses would
face higher product conversion costs at
lower TSLs than their large competitor.
Both large and small manufacturers
have several product offerings in each
product class, sometimes at varying
efficiency levels, but the larger
manufacturer produces products with
higher efficiencies in larger volumes. As
Total product lines
for all product
classes
0
0
0
1
1
0
0
2
3
6
4
2
2
1
a result, the small manufacturers would
have to upgrade more product lines than
the large manufacturer at lower TSLs.
As shown in Table VI.10 and Table
VI.11, modifying facilities and
developing new, more-efficient products
would cause a typical small
manufacturer to incur higher product
conversion costs than a typical larger
manufacturer for TSL 1 through TSL 5.
TABLE VI.10—TOTAL CONVERSION COSTS FOR A TYPICAL SMALL MANUFACTURER OF TRADITIONAL DIRECT HEATING
EQUIPMENT
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Capital conversion
costs for a typical
small manufacturer
(2008$ millions)
Product conversion
costs for a typical
small manufacturer
(2008$ millions)
Total conversion
costs for a typical
small manufacturer
(2008$ millions)
0
0.58
1.03
1.61
1.89
1.57
2.13
0
0.29
0.44
0.69
0.80
1.20
1.40
0
0.86
1.47
2.31
2.69
2.77
3.53
Baseline ...............................................................................................................
TSL 1 ...................................................................................................................
TSL 2 ...................................................................................................................
TSL 3 ...................................................................................................................
TSL 4 ...................................................................................................................
TSL 5 ...................................................................................................................
TSL 6 ...................................................................................................................
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Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
TABLE VI.11—TOTAL CONVERSION COSTS FOR A TYPICAL LARGE MANUFACTURER OF TRADITIONAL DIRECT HEATING
EQUIPMENT
Capital conversion
costs for a typical
large manufacturer
(2008$ millions)
Product conversion
costs for a typical
large manufacturer
(2008$ millions)
Total conversion
costs for a typical
large manufacturer
(2008$ millions)
0
0.05
0.31
1.24
1.82
1.52
2.49
0
0.06
0.15
0.54
0.77
1.08
1.47
0
0.11
0.46
1.77
2.59
2.60
3.96
Baseline ...............................................................................................................
TSL 1 ...................................................................................................................
TSL 2 ...................................................................................................................
TSL 3 ...................................................................................................................
TSL 4 ...................................................................................................................
TSL 5 ...................................................................................................................
TSL 6 ...................................................................................................................
Because the larger manufacturer offers
more products at higher efficiencies, a
typical small manufacturer faces
disproportionate costs at the lower TSLs
in absolute terms at TSL 1 through TSL
5. However, at TSL 4 through TSL 6 a
typical small manufacturer and a typical
large manufacturer face similar product
and capital conversion costs because a
similar number of product lines fall
below the required efficiencies. Despite
being similar in absolute terms, at these
TSLs the small manufacturers would be
more likely to be disproportionately
harmed at any TSL because they have a
much lower volume across which to
spread similar costs. To show how a
smaller scale would harm a typical
small business manufacturer, DOE used
estimates of the market shares within
the industry for each product class to
estimate the typical annual revenue,
operating profit, research and
development expense, and capital
expenditures for a typical large
manufacturer and a typical small
manufacturer using the financial
parameters in the DHE GRIM.
Comparing the conversion costs of a
typical small manufacturer to a typical
large manufacturer with operating profit
(earnings before interest and taxation
(EBIT)) is a rough estimate of how
quickly the investments could be
recouped. Table VI.12 and Table VI.13
show these comparisons.
TABLE VI.12—COMPARISON OF A TYPICAL SMALL MANUFACTURER’S CONVERSION COSTS TO ANNUAL EXPENSES,
REVENUE, AND OPERATING PROFIT
Capital conversion
cost as a
percentage of annual capital
expenditures
(percent)
Baseline ...................................................................................
TSL 1 .......................................................................................
TSL 2 .......................................................................................
TSL 3 .......................................................................................
TSL 4 .......................................................................................
TSL 5 .......................................................................................
TSL 6 .......................................................................................
Product
conversion cost as
a percentage of
annual R&D expense
(percent)
Total conversion
cost as a
percentage of annual revenue
(percent)
Total conversion
cost as a
percentage of annual EBIT
(percent)
..............................
170
242
378
443
367
499
..............................
128
155
245
283
425
495
..............................
6
8
12
14
15
19
..............................
163
221
347
404
416
531
TABLE VI.13—COMPARISON OF A TYPICAL LARGE MANUFACTURER’S CONVERSION COSTS TO ANNUAL EXPENSES,
REVENUE, AND OPERATING PROFIT
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Capital conversion
cost as a percentage of annual
capital expenditures
(percent)
Baseline ...................................................................................
TSL 1 .......................................................................................
TSL 2 .......................................................................................
TSL 3 .......................................................................................
TSL 4 .......................................................................................
TSL 5 .......................................................................................
TSL 6 .......................................................................................
Table VI.12 and Table VI.13 illustrate
that, although the investments required
at each TSL can be considered
substantial for all companies, the
impacts could be greater for a typical
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Product
conversion cost as
a percentage of
annual R&D expense
(percent)
Total conversion
cost as a
percentage of annual revenue
(percent)
Total conversion
cost as a
percentage of annual EBIT
(percent)
..............................
7
42
167
246
206
337
..............................
12
30
110
158
220
300
..............................
0
1
5
8
8
12
..............................
10
40
154
225
225
344
small business because of much lower
production volumes and a comparable
number of product offerings. At higher
TSLs, it is more likely that
manufacturers of traditional DHE would
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reduce the number of product lines they
offer to keep their conversion costs at
manageable levels. At higher TSLs,
small manufacturers would face
increasingly difficult decisions on
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jlentini on DSKJ8SOYB1PROD with PROPOSALS2
whether to invest the capital required to
be able to continue offering a full range
of products, cut product lines,
consolidate to maintain a large enough
combined scale to spread the required
conversion costs and operating
expenses, or exit the market altogether.
Because of the high conversion costs,
manufacturers would likely eliminate
their lower-volume product lines. Small
manufacturers might only be able to
afford to selectively upgrade their most
popular products and be forced to
discontinue lower-volume products
because the product development costs
that would be required to upgrade all of
their existing product lines would be
too high.
DOE’s product line analysis reveals
the potential for small businesses to be
disproportionately harmed by the
proposed standard levels and higher
TSLs. Small traditional direct heating
manufacturers have less access to
capital than their larger competitor.
Larger manufacturers profit from
offering a variety of products and have
the ability to fund required capital and
product conversion costs using cash
generated from all products. Unlike
large manufacturers, the small
manufacturers cannot leverage resources
from other departments. With these
considerations, it is more likely that the
small businesses would have to spend
an even greater proportion of their
annual R&D and capital expenditures
than shown in the industry-wide
figures.
In addition, small manufacturers have
less buying power than their larger
competitor. Traditional DHE is a lowvolume industry, which can make it
difficult for any manufacturer to take
advantage of bulk purchasing power or
economies of scale. The two small
businesses have approximately half the
market share of their large competitor,
which puts them at a disadvantage
when purchasing components and raw
materials. In addition, the large
manufacturer has a parent company that
manufactures products and equipment
other than traditional DHE. This
manufacturer’s larger scale and
additional manufacturing capacity
(required for products and equipment
other than DHE) also give the company
more leverage with its suppliers as it
purchases greater volumes of
components and raw materials. During
the manufacturer interviews, the small
businesses commented that to comply
with amended energy conservation
standards, they would likely need to
buy more purchased parts instead of
producing most of the final product inhouse. Because the large manufacturer
has an advantage in purchasing power
that would likely allow it to buy
purchased parts at lower costs, an
amended energy conservation standard
that requires more purchased parts may
differentially harm the profitability of
the small businesses.
Even though there is a potential for
small businesses to be negatively
impacted by the proposed standards,
DOE believes that manufacturers,
including the small businesses, would
be able to maintain viable number of
product offerings at TSL 3, the proposed
standard level. A typical small business
offers product families in three out of
the four product types that would meet
or exceed the proposed standard levels
in today’s NOPR. For example, products
are currently available on the market at
the proposed standard level for gas wall
gravity DHE, which comprise over 60
percent of the traditional DHE market.
The proposed standard levels do not
require manufacturers, including those
that are small, to completely redesign all
their product lines. For those product
lines that would need to be redesigned,
DOE believes that small manufacturers
would offer fewer product lines after
amended energy conservation
standards. However, DOE believes that
the proposed standards would allow the
small manufacturers to selectively
upgrade their existing product lines and
maintain viable production volumes
after the compliance date of the
amended energy conservation
standards. DOE seeks comment on the
potential impacts of amended standards
on the small traditional DHE
manufacturers. (See Issue 21 and 22
under ‘‘Issues on Which DOE Seeks
Comment’’ in section VII.E of this
NOPR.)
ii. Gas Hearth-Type Direct Heating
Equipment
While the three large manufacturers
have a larger product offering than the
65989
smaller manufacturers, both small and
large manufacturers typically offer a
wide range of covered gas hearth DHE.
During interviews, manufacturers
indicated that product lines typically
are not based on efficiency. Rather,
product lines are groups of gas stoves,
gas inserts, or gas fireplaces with similar
appearances and shapes that span input
ratings to appeal to a range of customers
with different heating and aesthetic
requirements. A product line is
typically built on the same production
platform and shares many of the same
appearance and optional features.
However, because products lines are
based on appearance, features, and
dimensions, product lines do not
necessarily have the same efficiency
across all input capacities.
DOE calculated the anticipated capital
and product development costs for gas
hearth DHE by estimating per-line cost.
DOE used certification databases,
product catalogs, interviews with
manufacturers, and sources of public
information to estimate the number of
product lines that meet each TSL for
every gas hearth DHE manufacturer for
which data was available. If a product
line contained several products that met
different efficiencies at different
capacities, DOE assumed that the
product line would be redesigned in
response to amended energy
conservation standards whenever the
least-efficient product did not meet the
required efficiency level.
To show how small manufacturers
would be potentially impacted
compared to the large manufacturers,
DOE assumed that the entire gas hearth
DHE industry was comprised of the 12
manufacturers identified in the market
and technology assessment (see chapter
3 of the TSD for more information).
Using all available public data, DOE
then identified the product lines and the
efficiency levels for each product line
made by these manufacturers. DOE used
this information calculate the product
line offerings of a ‘‘typical’’ large
manufacturer and small manufacturer.
Table VI.14 and Table VI.15 show DOE’s
estimates for the product lines of a
typical small and a typical large gas
hearth manufacturer.
TABLE VI.14—NUMBER OF PRODUCT LINES OF A TYPICAL SMALL MANUFACTURER
AFUE
(percent)
Baseline ...........................................................................................................................................................
TSL 1, 2, and 3 ................................................................................................................................................
TSL 4 and 5 .....................................................................................................................................................
TSL 6 ...............................................................................................................................................................
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Number of
product lines
64
67
72
93
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0
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TABLE VI.15—NUMBER OF PRODUCT LINES OF TYPICAL LARGE MANUFACTURER
AFUE
(percent)
Baseline ...........................................................................................................................................................
TSL 1, 2, and 3 ................................................................................................................................................
TSL 4 and 5 .....................................................................................................................................................
TSL 6 ...............................................................................................................................................................
Table VI.14 shows that a typical small
manufacturer currently offers nine total
product lines: 5 at baseline efficiency
(i.e., 64 percent AFUE), 3 at 67 percent
AFUE, and 1 at 72 percent AFUE. Table
VI.14 suggests that a typical small
manufacturer would need to upgrade up
to five product lines at TSL 1 through
TSL 3, up to eight product lines at TSL
4 and TSL 5, and up to nine at TSL 6.
Table VI.15 shows that a typical large
manufacturer currently offers 17 total
product lines: Eight at the baseline (64
percent AFUE), six at 67 percent AFUE,
and three at 72 percent AFUE. Table
VI.15 suggests that a typical large
manufacturer would upgrade up to eight
product lines at TSL 1 through TSL 3,
up to 14 product lines at TSL 4 and TSL
5, and up to 17 at TSL 6. However, DOE
recognizes that not all manufacturers of
gas hearth DHE currently report the
efficiency of their products using the
DOE test procedure, and as a result they
may offer products at other efficiencies.
DOE requests comment on its
characterization of a typical large and a
typical small gas hearth DHE
manufacturer. (See Issue 23 under
‘‘Issues on Which DOE Seeks Comment’’
in section VII.E of this NOPR.)
To calculate the capital and product
conversion costs for a typical large and
a typical small manufacturer, DOE
Number of
product lines
64
67
72
93
8
6
3
0
multiplied its estimate of the perproduct-line capital and product
conversion costs by the number of
product lines a typical large and a
typical small manufacturer would need
to upgrade at each TSL. As described in
section IV.H.2 above, DOE assumed
manufacturers would only upgrade fifty
percent of their existing product lines
that did not meet the required
efficiencies at each TSL for gas hearth
DHE. Table VI.16 and Table VI.17 show
DOE’s estimates for the product and
capital conversion costs that a typical
large manufacturer and a typical small
manufacturer would be expected to
incur at each TSL.
TABLE VI.16—TOTAL CONVERSION COSTS FOR A TYPICAL SMALL MANUFACTURER OF GAS HEARTH DIRECT HEATING
EQUIPMENT
Capital
conversion costs
for a typical
small manufacturer
Baseline ...........................................................................................................................
TSL 1, 2, and 3 ................................................................................................................
TSL 4 and 5 .....................................................................................................................
TSL 6 ...............................................................................................................................
Product
conversion costs
for a typical
small manufacturer
Total conversion
costs for a
typical small
manufacturer
............................
$25,000
75,000
400,000
............................
$66,667
200,000
800,000
............................
$91,667
275,000
1,200,000
TABLE VI.17—TOTAL CONVERSION COSTS FOR A TYPICAL LARGE MANUFACTURER OF GAS HEARTH DIRECT HEATING
EQUIPMENT
Capital
conversion costs
for a typical large
manufacturer
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Baseline ...........................................................................................................................
TSL 1, 2, and 3 ................................................................................................................
TSL 4 and 5 .....................................................................................................................
TSL 6 ...............................................................................................................................
Because a typical large manufacturer
has significantly higher market shares
and a greater number product lines, a
large manufacturer would have higher
conversion costs on an absolute basis
than a typical small manufacturer.
However, at every TSL, a typical small
business manufacturer could be
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Product
conversion costs
for a typical large
manufacturer
Total conversion
costs for a typical large manufacturer
............................
$50,000
125,000
800,000
............................
$133,333
333,333
1,600,000
............................
$183,333
458,333
2,400,000
disproportionately impacted. To show
how a much smaller manufacturing
scale could harm small business
manufacturers as compared to large
manufacturers, DOE used the market
share of a typical large manufacturer
and a typical small manufacturer to
estimate the annual revenue, EBIT, R&D
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expense, and capital expenditures for a
typical large and typical small
manufacturer. DOE then compared these
costs to the required capital and product
conversion costs at each TSL for a
typical large and typical small
manufacturer. Table VI.18 through
Table VI.19 show these comparisons.
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TABLE VI.18—COMPARISON OF A TYPICAL SMALL GAS HEARTH DIRECT HEATING EQUIPMENT MANUFACTURER’S
CONVERSION COSTS TO ANNUAL EXPENSES, REVENUE, AND PROFIT
Capital
conversion cost
as a percentage
of annual capital
expenditures
(percent)
Baseline ...........................................................................................
TSL 1, 2, and 3 ................................................................................
TSL 4 and 5 .....................................................................................
TSL 6 ...............................................................................................
Product
conversion cost
as a percentage
of annual R&D
expense
(percent)
Total conversion
cost as a
percentage of
annual revenue
(percent)
Total conversion
cost as a
percentage of
annual EBIT
(percent)
............................
33.2
99.7
531.9
............................
141.8
425.5
1,702.2
............................
2.9
8.8
38.3
–
83.0
248.9
1,086.2
TABLE VI.19—COMPARISON OF A TYPICAL LARGE GAS HEARTH-TYPE DIRECT HEATING EQUIPMENT MANUFACTURER’S
CONVERSION COSTS TO ANNUAL EXPENSES, REVENUE, AND PROFIT
Capital
conversion cost
as a percentage
of annual capital
expenditures
(percent)
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Baseline ...........................................................................................
TSL 1, 2, and 3 ................................................................................
TSL 4 and 5 .....................................................................................
TSL 6 ...............................................................................................
DOE’s product line analysis illustrates
that small businesses have the potential
to be differentially impacted by any
amended energy conservation standard
because the small businesses have a
disproportionate number of product
lines relative to their much smaller
scale. For TSLs 4, 5 and 6, amended
energy conservation standards could
force a typical small business to hire
additional engineers, discontinue
product lines, or selectively upgrade
more popular products with their
present limited engineering and product
development resources. Because the
annual shipments of small
manufacturers are several times lower
than those of major manufacturers and
small manufacturers typically only
manufacture gas hearth DHE, small
companies have less buying power than
their larger competitors. The much
larger production volumes of large
manufacturers give them more leverage
to negotiate lower prices with
component and material suppliers.
Because these conversion costs are more
substantial relative to the size of a
typical small business, large
manufacturers could take additional
market share from small manufacturers
at TSL 4 through TSL 6. Because TSLs
4 and 5 require additional plant
modifications, the added conversion
costs make it more likely that small
manufacturers could discontinue some
of their least popular product lines at
TSL 4 and TSL 5. At TSL 6, the
substantial conversion costs could cause
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Product
conversion cost
as a percentage
of annual R&D
expense
(percent)
Total conversion
cost as a
percentage of
annual revenue
(percent)
Total conversion
cost as a
percentage of
annual EBIT
(percent)
............................
3.2
7.9
50.7
............................
13.5
33.8
162.1
............................
0.3
0.7
3.6
............................
7.9
19.8
103.4
even a large manufacturer to potentially
decide to offer fewer product lines, to
bring down the significant product
conversion costs. Consequently, it is
increasingly likely that higher
conversion costs could cause many
small businesses to exit the market or
become severely constrained with the
number of product lines offered at TSLs
4, 5, and 6.
At TSLs 1 through 3, a typical small
manufacturer would not face
prohibitively large conversion costs to
meet the amended energy conservation
standards. At these TSLs, the amended
energy conservation standards could be
met with products that use electric
ignition, which is not particularly
capital intensive. These changes would
also not require significant investments
in product development costs by small
businesses. The most substantial portion
of the conversion costs at TSLs 1
through 3 would be testing, recertifying,
and remarketing all the existing product
lines that currently meet the baseline
efficiencies. In addition, at TSL 1
through TSL 3, it is likely that small
manufacturers would not discontinue a
large number of product lines to lower
product and capital conversion costs
because these costs are not substantial.
A typical small manufacturer has
multiple product lines that meet and
exceed the required efficiencies at TSL
3. Also, the proposed standard levels do
not require manufacturers to
substantially redesign product lines that
fall below TSL 3.
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DOE’s analysis indicates that a typical
small manufacturer of gas hearth DHE
already offers multiple product lines
that meet and exceed the required
efficiencies at TSL 3, the proposed
energy conservation standard. In
addition, the proposed standard levels
do not require substantial redesign to
existing product lines that do not meet
the proposed TSL 3. Because most of the
product lines that do not meet the
proposed TSL could be upgraded with
relatively minor changes, DOE believes
that manufacturers, including the small
businesses, will be able to maintain a
viable number of product offerings at
the proposed standard level. DOE seeks
comment on the potential impacts on
the small gas hearth DHE
manufacturers. (See Issue 24 under
‘‘Issues on Which DOE Seeks Comment’’
in section VII.E of this NOPR.)
e. 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 considered
today.
f. Significant Alternatives to the
Proposed Rule
The discussion above analyzes
impacts on small businesses that would
result from the other TSLs DOE
considered. Though TSLs lower than
the proposed TSLs are expected to
reduce the impacts on small entities,
DOE is required by EPCA to establish
standards that achieve the maximum
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improvement in energy efficiency that
are technically 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. For DHE,
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. While these
alternatives may mitigate the economic
impacts on small entities compared to
the proposed standards, the energy
savings of these regulatory alternatives
are at least four times smaller than those
expected from the proposed standard
levels. Thus, DOE rejected these
alternatives and is proposing the
standards set forth in this rulemaking.
DOE continues to seek input from
businesses that would be affected by
this rulemaking and will consider
comments received in the development
of any final rule.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
C. Review Under the Paperwork
Reduction Act of 1995
This rule contains a collection-ofinformation requirement subject to the
Paperwork Reduction Act (PRA) which
has been approved by OMB under
control number 1910–1400. Public
reporting burden for compliance
reporting for energy and water
conservation standards 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.
Send comments regarding this burden
estimate, or any other aspect of this data
collection, including suggestions for
reducing the burden, to DOE (see
ADDRESSES) and by e-mail to
Christine_J._Kymn@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
DOE has prepared a draft
environmental assessment (EA) of the
impacts of the proposed rule, pursuant
to the National Environmental Policy
Act of 1969 (42 U.S.C. 4321 et seq.), the
regulations of the Council on
Environmental Quality (40 CFR parts
1500–1508), and DOE’s regulations for
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compliance with the National
Environmental Policy Act (10 CFR part
1021). This assessment includes an
examination of the potential effects of
emission reductions likely to result from
the rule in the context of global climate
change, as well as other types of
environmental impacts. The draft EA
has been incorporated into the TSD.
Before issuing a final rule for the three
type of heating products, DOE will
consider public comments and, as
appropriate, determine whether to issue
a finding of no significant impact
(FONSI) as part of a final EA or to
prepare an environmental impact
statement (EIS) for this rulemaking.
E. Review Under Executive Order 13132
Executive Order 13132, ‘‘Federalism,’’
64 FR 43255 (August 4, 1999) imposes
certain requirements on 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 today’s proposed 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 proposed 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(d)) 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’’ (61 FR 4729 (Feb. 7, 1996))
imposes on Executive agencies the
general duty to adhere to the following
requirements: (1) Eliminate drafting
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errors and ambiguity; (2) write
regulations to minimize litigation; and
(3) provide a clear legal standard for
affected conduct rather than a general
standard and promote simplification
and burden reduction. Section 3(b) of
Executive Order 12988 specifically
requires that 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
proposed 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 (Pub. L. 104–4)
(UMRA) requires each Federal agency to
assess the effects of Federal regulatory
actions on State, local, and Tribal
governments and the private sector. 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 of the
rule 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 proposed
‘‘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 small
governments. On March 18, 1997, DOE
published a statement of policy on its
process for intergovernmental
consultation under UMRA (62 FR
12820) (also available at https://
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www.gc.doe.gov). Although today’s
proposed rule does not contain a
Federal intergovernmental mandate, it
may impose expenditures of $100
million or more on the private sector.
Today’s proposed rule would likely
result in a final rule that could impose
expenditures of $100 million or more
between 2013 and 2045 in the
residential sector. Therefore, DOE must
publish a written statement assessing
the costs, benefits, and other effects of
the rule on the national economy.
Section 205 of UMRA also requires DOE
to identify and consider a reasonable
number of regulatory alternatives before
promulgating a rule for which UMRA
requires such a written statement. DOE
must 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 EPCA (42 U.S.C.
6295(o)), today’s proposed energy
conservation standards for the three
types of heating products would achieve
the maximum improvement in energy
efficiency that DOE has determined to
be both technologically feasible and
economically justified. DOE may not
select a regulatory alternative that does
not meet this statutory standard. A full
discussion of the alternatives
considered by DOE is presented in the
‘‘Regulatory Impact Analysis’’ section of
the TSD for this proposed rule. Also,
section 202(c) of UMRA authorizes an
agency to prepare the written statement
required by UMRA in conjunction with
or as part of any other statement or
analysis that accompanies the proposed
rule. (2 U.S.C. 1532(c)) The TSD,
preamble, and regulatory impact
analysis for today’s proposed rule
contain a full discussion of the rule’s
costs, benefits, and other effects on the
national economy, and, therefore satisfy
UMRA’s written statement requirement.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
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.
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I. Review Under Executive Order 12630
DOE has determined under Executive
Order 12630, ‘‘Governmental Actions
and Interference with Constitutionally
Protected Property Rights,’’ 53 FR 8859
(March 18, 1988), 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 agencies to review most
disseminations of information to the
public under 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 notice 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 tentatively concluded that
today’s regulatory action, which sets
forth energy conservation standards for
three types of heating products, is not a
‘‘significant energy action’’ because the
proposed 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
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65993
the Administrator at OIRA. Therefore,
DOE has not prepared a Statement of
Energy Effects on the proposed 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 (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.’’ 70 FR 2664, 2667
(Jan. 14, 2005).
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 on 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: https://
www1.eere.energy.gov/buildings/
appliance_standards/peer_review.htm.
VII. Public Participation
A. Public Meeting
The time, date and location of the
public meeting are listed in the DATES
and ADDRESSES sections at the beginning
of this document. To attend the public
meeting, please notify Ms. Brenda
Edwards at (202) 586–2945 or
Brenda.Edwards@ee.doe.gov. As
explained in the ADDRESSES section,
foreign nationals visiting DOE
Headquarters are subject to advance
security screening procedures.
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B. Procedure for Submitting Requests To
Speak
Any person who has an interest in
today’s notice, or who is a
representative of a group or class of
persons that has an interest in these
issues, may request an opportunity to
make an oral presentation. Such persons
may hand-deliver requests to speak,
along with a computer diskette or CD in
WordPerfect, Microsoft Word, PDF, or
text (ASCII) file format, to the address
shown in the ADDRESSES section at the
beginning of this NOPR between the
hours of 9 a.m. and 4 p.m., Monday
through Friday, except Federal holidays.
Requests may also be sent by mail, or by
e-mail to: Brenda.Edwards@ee.doe.gov.
Persons requesting an opportunity to
speak should briefly describe the nature
of their interest in this rulemaking and
provide a telephone number for contact.
DOE requests persons scheduled to
make an oral presentation to submit an
advance copy of their statements at least
one week before the public meeting. At
its discretion, DOE may permit any
person who cannot supply an advance
copy of their statement to participate, if
that person has made advance
alternative arrangements with the
Building Technologies Program. The
request to give an oral presentation
should ask for such alternative
arrangements.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
C. Conduct of Public Meeting
DOE will designate a DOE official to
preside at the public meeting and may
also use a professional facilitator to aid
discussion. The meeting will not be a
judicial or evidentiary-type public
hearing, but DOE will conduct it in
accordance with section 336 of EPCA.
(42 U.S.C. 6306) A court reporter will be
present to record the proceedings and to
prepare a transcript. DOE reserves the
right to schedule the order of
presentations and to establish the
procedures governing the conduct of the
public meeting. After the public
meeting, interested parties may submit
further comments on the proceedings as
well as on any aspect of the rulemaking
until the end of the comment period.
The public meeting will be conducted
in an informal, conference style. DOE
will present summaries of comments
received before the public meeting,
allow time for presentations by
participants, and encourage all
interested parties to share their views on
issues affecting this rulemaking. Each
participant will be allowed to make a
prepared general statement (within time
limits determined by DOE), before the
discussion of specific topics. DOE will
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permit other participants to comment
briefly on any general statements.
At the end of all prepared statements
on a topic, DOE will permit participants
to clarify their statements briefly and
comment on statements made by others.
Participants should be prepared to
answer questions from DOE and from
other participants concerning these
issues. DOE representatives may also
ask questions of participants concerning
other matters relevant to this
rulemaking. The official conducting the
public meeting will accept additional
comments or questions from those
attending, as time permits. The
presiding official will announce any
further procedural rules or modification
of the above procedures that may be
needed for the proper conduct of the
public meeting.
DOE will make the entire record of
this proposed rulemaking, including the
transcript from the public meeting,
available for inspection at the U.S.
Department of Energy, Resource Room
of the Building Technologies Program,
950 L’Enfant Plaza, SW., Washington,
DC 20024, (202) 586–2945, between 9
a.m. and 4 p.m., Monday through
Friday, except Federal holidays.
D. Submission of Comments
DOE will accept comments, data, and
other information on the proposed rule
before or after the public meeting, but
no later than the date provided at the
beginning of this NOPR. Comments,
data, and other information submitted to
DOE’s e-mail address for this
rulemaking should be provided in
WordPerfect, Microsoft Word, PDF, or
text (ASCII) file format. Interested
parties should avoid the use of special
characters or any form of encryption
and, wherever possible, comments
should carry the electronic signature of
the author. Comments, data, and
information submitted to DOE via mail
or hand delivery/courier should include
one signed original paper copy. No
telefacsimiles (faxes) will be accepted.
According to 10 CFR 1004.11, any
person submitting information that he
or she believes to be confidential and
exempt by law from public disclosure
should submit two copies: one copy of
the document including all the
information believed to be confidential,
and one copy of the document with the
information believed to be confidential
deleted. DOE will make its own
determination about the confidential
status of the information and treat it
according to its determination.
Factors of interest to DOE when
evaluating requests to treat submitted
information as confidential include: (1)
A description of the items; (2) whether
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and why such items are customarily
treated as confidential within the
industry; (3) whether the information is
generally known by or available from
other sources; (4) whether the
information has previously been made
available to others without obligation
concerning its confidentiality; (5) an
explanation of the competitive injury to
the submitting person which would
result from public disclosure; (6) when
such information might lose its
confidential character due to the
passage of time; and (7) why disclosure
of the information would be contrary to
the public interest.
E. Issues on Which DOE Seeks Comment
DOE is particularly interested in
receiving comments and views of
interested parties concerning the
following issues:
1. The max-tech efficiency levels
identified for the analyses, including
whether the efficiency levels identified
by DOE can be achieved using the
technologies screened-in during the
screening analysis (see section IV.B),
and whether higher efficiencies are
achievable using technologies that were
screened-in during the screening
analysis.
2. The potential burdens to
manufacturers of hearth-type DHE as a
result of the testing, certification,
reporting, and enforcement provisions.
3. EPCA’s efficiency descriptor
requirements in any potential test
procedure revisions for electric pool
heaters.
4. DOE’s proposed definition for
vented hearth heaters.
5. DOE’s product classes for water
heaters. In particular, DOE is seeking
comment about the need for a separate
product class for low-boy water heaters.
6. DOE’s approach for analyzing ultralow NOX gas-fired storage water heaters
and the need for a separate product
class.
7. DOE’s approach to developing the
energy efficiency equations, the
appropriate slope of energy efficiency
equations at each efficiency level
analyzed, and the appropriate storage
volumes for changing the slope of the
line. DOE is also interested in any
alternatives to the energy efficiency
equations that DOE should consider for
the final rule.
8. The need for a separate product
class for heat pump water heaters.
Specifically, DOE is interested in
receiving comments on whether a heat
pump water heater can be used as a
direct replacement for an electric
resistance water heater, and the types
and frequency of instances a heat pump
water heater cannot be used as a direct
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replacement for an electric resistance
water heater.
9. DOE’s proposed product classes for
the four existing types of DHE.
10. DOE’s proposed product class
divisions for gas hearth DHE.
11. The manufacturability of heat
pump water heaters and the capability
of manufacturers to ramp up production
of heat pump water heaters.
Specifically, DOE is seeking comment
on how long it would take and the
magnitude of the costs for
manufacturers to convert all product
lines to heat pump water heaters if it
were required by an amended energy
conservation standard. In addition, DOE
is seeking comment about the length of
time required to retrain installers and
servicers of water heaters for the
installation and servicing of heat pump
water heaters.
12. DOE’s estimated manufacturer
production costs for storage water
heaters at storage volumes outside of the
representative volume.
13. DOE’s analysis of installation
costs for water heaters. DOE is
particularly interested in comments on
its analysis of installation costs for heat
pump water heaters.
14. DOE’s analysis of repair and
maintenance costs for heat pump water
heaters.
15. DOE’s approach for analyzing fuel
switching that may result from the
proposed standards on water heaters
and the other heating products. In
particular, DOE requests comments on
its general approach, which does not
involve price elasticities; its analysis of
switching to gas-fired storage water
heaters in the case of a standard that
effectively requires an electric heat
pump water heater; its conclusion that
the proposed standards would not
induce switching from a gas storage
water heater to an electric storage water
heater; and its conclusion that the
proposed standards would not induce
switching for gas-fired instantaneous
water heaters, DHE, and pool heaters.
16. DOE’s consideration of TSL 6 in
the final rule for residential water
heaters and the associated issues DOE
has identified surrounding heat pump
water heaters.
17. DOE’s consideration of TSL 5 in
the final rule for residential water
heaters and the associated issues DOE
has identified surrounding standards
that effectively require different
technologies for different subsets of
products.
18. The appropriateness of TSL 4 for
residential pool heaters in light of the
negative life cycle costs for a majority of
consumers. In addition, DOE’s
consideration of other TSLs, including
TSL 3, as an alternative for the final
standard level.
19. The impacts of the proposed
amended energy conservation standards
on small manufacturers of residential
water heaters.
20. The impacts of the proposed
amended energy conservation standards
on small manufacturers of gas-fired
residential pool heaters.
21. The impacts of the proposed
amended energy conservation standards
on small manufacturers of traditional
DHE. DOE is interested in specific
information regarding the potential for
small manufacturers of traditional DHE
to discontinue particular product lines
as a result of the proposed standard, as
well as the potential economic effect
discontinuing those particular product
lines would have on small
manufacturers of traditional DHE.
22. Alternatives to the proposed
amended energy conservation standards
for traditional DHE. Specifically, DOE is
interested in information regarding
alternatives that could provide
significant cost-savings for small
manufacturers while meeting DOE’s
energy conservation goals.
23. DOE’s characterization of typical
small and large gas hearth DHE
manufacturers.
24. The impacts of the proposed
amended energy conservation standards
on small manufacturers of gas hearth
DHE.
VIII. Approval of the Office of the
Secretary
The Secretary of Energy has approved
publication of today’s proposed rule.
List of Subjects in 10 CFR Part 430
Administrative practice and
procedure, Confidential business
65995
information, Energy conservation,
Household appliances, Imports,
Intergovernmental relations, Reporting
and recordkeeping requirements, and
Small businesses.
Issued in Washington, DC, on November
23, 2009.
Cathy Zoi,
Assistant Secretary, Energy Efficiency and
Renewable Energy.
For the reasons set forth in the
preamble, DOE proposes to amend
chapter II, subchapter D, of title 10 of
the Code of Federal Regulations, as set
forth below:
PART 430—ENERGY CONSERVATION
PROGRAM FOR CONSUMER
PRODUCTS
1. The authority for part 430
continues to read as follows:
Authority: 42 U.S.C. 6291–6309; 28 U.S.C.
2461 note.
2. In § 430.2, add the definitions
‘‘Direct heating equipment’’ and
‘‘Vented hearth heater,’’ in alphabetical
order to read as follows:
§ 430.2
Definitions.
*
*
*
*
*
Direct heating equipment means
vented home heating equipment and
unvented home heating equipment.
*
*
*
*
*
Vented hearth heater means a vented,
freestanding, recessed, zero clearance
fireplace heater, a gas fireplace insert or
a gas-stove, which simulates a solid fuel
fireplace and is designed to furnish
warm air, without ducts to the space in
which it is installed.
*
*
*
*
*
3. In § 430.32 revised paragraphs (d),
(i), (k) to read as follows:
§ 430.32 Energy and water conservation
standards and their effective dates.
*
*
*
*
*
(d) Water heaters. The energy factor of
water heaters shall not be less than the
following for products manufactured on
or after the indicated dates.
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Product class
Energy factor as of
January 20, 2004
Energy factor as of [INSERT DATE 5 YEARS AFTER DATE OF
PUBLICATION OF THE FINAL RULE]
Gas-fired Water Heater ...................
0.67¥(0.0019 × Rated Storage
Volume in gallons).
Oil-fired Water Heater .....................
0.59¥(0.0019 × Rated Storage
Volume in gallons).
0.97¥(0.00132 × Rated Storage
Volume in gallons).
For tanks with Rated Storage Volume at or below 60 gallons:
0.675¥(0.0012 × Rated Storage Volume in gallons);
For tanks with Rated Storage Volume above 60 gallons:
0.717¥(0.0019 × Rated Storage Volume in gallons).
0.68¥(0.0019 × Rated Storage Volume in gallons).
Electric Water Heater ......................
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0.96¥(0.0003 × Rated Storage Volume in gallons);
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65996
Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 / Proposed Rules
Energy factor as of
(percent)January 20, 2004
Product class
Tabletop Water Heater ....................
Instantaneous
Gas-fired
Water
Heater.
Instantaneous Electric Water Heater.
0.93¥(0.00132 × Rated Storage
Volume in gallons).
0.62¥(0.0019 × Rated Storage
Volume in gallons).
0.93¥(0.00132 × Rated Storage
Volume in gallons).
Energy factor as of [INSERT DATE 5 YEARS AFTER DATE OF
PUBLICATION OF THE FINAL RULE]
For tanks with Rated Storage Volume above
1.088¥(0.0019 × Rated Storage Volume in gallons).
0.93¥(0.00132 × Rated Storage Volume in gallons).
80
gallons:
0.82¥(0.0019 × Rated Storage Volume in gallons).
0.93¥(0.00132 × Rated Storage Volume in gallons).
Note: The Rated Storage Volume equals the water storage capacity of a water heater, in gallons, as specified by the manufacturer.
*
*
*
*
*
(i) Direct heating equipment. (1)
Direct heating equipment manufactured
on or after January 1, 1990 and before
[INSERT DATE 3 YEARS AFTER DATE
OF PUBLICATION OF THE FINAL
RULE], shall have an annual fuel
utilization efficiency no less than:
Product class
Annual fuel utilization
efficiency, Jan. 1, 1990
(percent)
1. Gas wall fan type up to 42,000 Btu/h .............................................................................................................................
2. Gas wall fan type over 42,000 Btu/h ...............................................................................................................................
3. Gas wall gravity type up to 10,000 Btu/h ........................................................................................................................
4. Gas wall gravity type over 10,000 Btu/h up to 12, 000 Btu/h .........................................................................................
5. Gas wall gravity type over 12,000 Btu/h up to 15,000 Btu/h ..........................................................................................
6. Gas wall gravity type over 15,000 Btu/h up to 19,000 Btu/h ..........................................................................................
7. Gas wall gravity type over 19,000 Btu/h and up to 27,000 Btu/h ...................................................................................
8. Gas wall gravity type over 27,000 Btu/h and up to 46,000 Btu/h ...................................................................................
9. Gas wall gravity type over 46,000 Btu/h .........................................................................................................................
10. Gas floor up to 37,000 Btu/h .........................................................................................................................................
11. Gas floor over 37,000 Btu/h ..........................................................................................................................................
12. Gas room up to 18,000 Btu/h ........................................................................................................................................
13. Gas room over 18,000 Btu/h up to 20,000 Btu/h ..........................................................................................................
14. Gas room over 20,000 Btu/h up to 27,000 Btu/h ..........................................................................................................
15. Gas room over 27,000 Btu/h up to 46,000 Btu/h ..........................................................................................................
16. Gas room over 46,000 Btu/h .........................................................................................................................................
73
74
59
60
61
62
63
64
65
56
57
57
58
63
64
65
(2) Direct heating equipment
manufactured on or after [INSERT
DATE 3 YEARS AFTER DATE OF
PUBLICATION OF THE FINAL RULE],
shall have an annual fuel utilization
efficiency no less than:
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
Product class
Annual fuel utilization
efficiency, [INSERT
DATE 3 YEARS AFTER
DATE OF PUBLICATION OF THE FINAL
RULE]
(percent)
1. Gas wall fan type up to 42,000 Btu/h .............................................................................................................................
2. Gas wall fan type over 42,000 Btu/h ...............................................................................................................................
3. Gas wall gravity type up to 27,000 Btu/h ........................................................................................................................
4. Gas wall gravity type over 27,000 Btu/h up to 46,000 Btu/h ..........................................................................................
5. Gas wall gravity type over 46,000 Btu/h .........................................................................................................................
6. Gas floor up to 37,000 Btu/h ...........................................................................................................................................
7. Gas floor over 37,000 Btu/h ............................................................................................................................................
8. Gas room up to 20,000 Btu/h ..........................................................................................................................................
9. Gas room over 20,000 Btu/h up to 27,000 Btu/h ............................................................................................................
10. Gas room over 27,000 Btu/h up to 46,000 Btu/h ..........................................................................................................
11. Gas room over 46,000 Btu/h .........................................................................................................................................
12. Gas hearth up to 20,000 Btu/h ......................................................................................................................................
13. Gas hearth over 20,000 Btu/h and up to 27,000 Btu/h ................................................................................................
14. Gas hearth over 27,000 Btu/h and up to 46,000 Btu/h ................................................................................................
15. Gas hearth over 46,000 Btu/h .......................................................................................................................................
76
77
70
71
72
57
58
62
67
68
69
61
66
67
68
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*
*
*
*
(k) Pool heaters. (1) Gas-fired pool
heaters manufactured on or after
January 1, 1990 and before [INSERT
DATE 3 YEARS AFTER DATE OF
PUBLICATION OF THE FINAL RULE],
jlentini on DSKJ8SOYB1PROD with PROPOSALS2
*
VerDate Nov<24>2008
20:45 Dec 10, 2009
Jkt 220001
shall have a thermal efficiency not less
than 78%.
(2) Gas-fired pool heaters
manufactured on or after [INSERT
DATE 3 YEARS AFTER DATE OF
PUBLCIATION OF THE FINAL RULE],
PO 00000
Frm 00147
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65997
shall have a thermal efficiency not less
than 84%.
*
*
*
*
*
[FR Doc. E9–28774 Filed 12–10–09; 8:45 am]
BILLING CODE 6450–01–P
E:\FR\FM\11DEP2.SGM
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Agencies
[Federal Register Volume 74, Number 237 (Friday, December 11, 2009)]
[Proposed Rules]
[Pages 65852-65997]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-28774]
[[Page 65851]]
-----------------------------------------------------------------------
Part II
Department of Energy
-----------------------------------------------------------------------
10 CFR Part 430
Energy Conservation Program: Energy Conservation Standards for
Residential Water Heaters, Direct Heating Equipment, and Pool Heaters;
Proposed Rule
Federal Register / Vol. 74, No. 237 / Friday, December 11, 2009 /
Proposed Rules
[[Page 65852]]
-----------------------------------------------------------------------
DEPARTMENT OF ENERGY
10 CFR Part 430
[Docket Number EE-2006-BT-STD-0129]
RIN 1904-AA90
Energy Conservation Program: Energy Conservation Standards for
Residential Water Heaters, Direct Heating Equipment, and Pool Heaters
AGENCY: Office of Energy Efficiency and Renewable Energy, Department of
Energy.
ACTION: Notice of proposed rulemaking and public meeting.
-----------------------------------------------------------------------
SUMMARY: The Energy Policy and Conservation Act (EPCA) prescribes
energy conservation standards for various consumer products and
commercial and industrial equipment, including residential water
heaters, direct heating equipment (DHE), and pool heaters. EPCA also
requires the U.S. Department of Energy (DOE) to determine whether more
stringent, amended standards for these products would be
technologically feasible and economically justified, and would save a
significant amount of energy. In this notice, DOE is proposing amended
energy conservation standards for residential water heaters (other than
tabletop and electric instantaneous models), gas-fired DHE, and gas-
fired pool heaters. DOE also is announcing a public meeting to receive
comment on these proposed standards and associated analyses and
results.
DATES: DOE will hold a public meeting on Thursday, January 7, 2010,
from 9 a.m. to 4 p.m., in Washington, DC. DOE must receive requests to
speak at the public meeting before 4 p.m., Wednesday, December 23,
2009. DOE must receive a signed original and an electronic copy of
statements to be given at the public meeting before 4 p.m., Wednesday,
December 30, 2009.
DOE will accept comments, data, and information regarding this
notice of proposed rulemaking (NOPR) before and after the public
meeting, but no later than February 9, 2010. See section VII, ``Public
Participation,'' of this NOPR for details.
ADDRESSES: The public meeting will be held at the U.S. Department of
Energy, Forrestal Building, Room 1E-245, 1000 Independence Avenue, SW.,
Washington, DC 20585-0121. To attend the public meeting, please notify
Ms. Brenda Edwards at (202) 586-2945. Please note that foreign
nationals visiting DOE Headquarters are subject to advance security
screening procedures. Any foreign national wishing to participate in
the meeting should advise DOE as soon as possible by contacting Ms.
Brenda Edwards to initiate the necessary procedures.
Any comments submitted must identify the NOPR for Energy
Conservation Standards for Heating Products, and provide the docket
number EE-2006-BT-STD-0129 and/or regulatory information number (RIN)
number 1904-AA90. Comments may be submitted using any of the following
methods:
1. Federal eRulemaking Portal: https://www.regulations.gov. Follow
the instructions for submitting comments.
2. E-mail: ResWaterDirectPoolHtrs@ee.doe.gov. Include docket number
EE-2006-BT-STD-0129 and/or RIN 1904-AA90 in the subject line of the
message.
3. Mail: Ms. Brenda Edwards, U.S. Department of Energy, Building
Technologies Program, Mailstop EE-2J, 1000 Independence Avenue, SW.,
Washington, DC 20585-0121. Please submit one signed paper original.
4. Hand Delivery/Courier: Ms. Brenda Edwards, U.S. Department of
Energy, Building Technologies Program, 950 L'Enfant Plaza, SW., Suite
600, Washington, DC 20024. Telephone: (202) 586-2945. Please submit one
signed paper original.
For detailed instructions on submitting comments and additional
information on the rulemaking process, see section VII of this document
(Public Participation).
Docket: For access to the docket to read background documents or
comments received, visit the U.S. Department of Energy, Resource Room
of the Building Technologies Program, 950 L'Enfant Plaza, SW., Suite
600, Washington, DC, (202) 586-2945, between 9 a.m. and 4 p.m., Monday
through Friday, except Federal holidays. Please call Ms. Brenda Edwards
at the above telephone number for additional information regarding
visiting the Resource Room.
FOR FURTHER INFORMATION CONTACT: Mr. Mohammed Khan, U.S. Department of
Energy, Office of Energy Efficiency and Renewable Energy, Building
Technologies Program, EE-2J, 1000 Independence Avenue, SW., Washington,
DC 20585-0121. Telephone: (202) 586-7892. E-mail:
Mohammed.Khan@ee.doe.gov.
Mr. Eric Stas or Mr. Michael Kido, U.S. Department of Energy,
Office of the General Counsel, GC-72, 1000 Independence Avenue, SW.,
Washington, DC 20585-0121. Telephone: (202) 586-9507. E-mail:
Eric.Stas@hq.doe.gov or Michael.Kido@hq.doe.gov.
For information on how to submit or review public comments and on
how to participate in the public meeting, contact Ms. Brenda Edwards,
U.S. Department of Energy, Office of Energy Efficiency and Renewable
Energy, Building Technologies Program, EE-2J, 1000 Independence Avenue,
SW., Washington, DC 20585-0121. Telephone: (202) 586-2945. E-mail:
Brenda.Edwards@ee.doe.gov.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Summary of the Proposed Rule
II. Introduction
A. Consumer Overview
B. Authority
C. Background
1. Current Standards
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
2. History of Standards Rulemaking for Water Heaters, Direct
Heating Equipment, and Pool Heaters
III. General Discussion
A. Test Procedures
1. Water Heaters
2. Direct Heating Equipment
3. Standby Mode and Off Mode Energy Consumption
B. Technological Feasibility
1. General
2. Maximum Technologically Feasible Levels
C. Energy Savings
1. Determination of Savings
2. Significance of Savings
D. Economic Justification
1. Specific Criteria
a. Economic Impact on Manufacturers and Consumers
b. Life-Cycle Costs
c. Energy Savings
d. Lessening of Utility or Performance of Products
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. Consideration of Products for Inclusion in This Rulemaking
a. Determination of Coverage Under the Act
b. Covered Products Not Included in This Rulemaking
2. Definition of Gas Hearth Direct Heating Equipment
3. Product Classes
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
B. Screening Analysis
1. Comments on the Screening Analysis
a. General Comments
b. Water Heaters
2. Technologies Considered
3. Heat Pump Water Heaters Discussion
a. Consumer Utility
b. Production, Installation, and Servicing Issues
[[Page 65853]]
c. General Comments
C. Engineering Analysis
1. Representative Products for Analysis
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
2. Ultra-Low NOX Gas-Fired Storage Water Heaters
3. Efficiency Levels Analyzed
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
4. Cost Assessment Methodology
a. Teardown Analysis
b. Cost Model
c. Manufacturing Production Cost
d. Cost-Efficiency Curves
e. Manufacturer Markup
f. Shipping Costs
g. Manufacturer Interviews
5. Results
6. Scaling to Additional Rated Storage Capacities for Water
Heaters
7. Energy Efficiency Equations
D. Markups to Determine Product Price
E. Life-Cycle Cost and Payback Period Analyses
1. Product Cost
2. Installation Cost
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
3. Annual Energy Consumption
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
d. Rebound Effect
4. Energy Prices
5. Repair and Maintenance Costs
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
6. Product Lifetime
7. Discount Rates
8. Compliance Date of the Amended Standards
9. Product Energy Efficiency in the Base Case
a. Water Heaters
b. DHE
c. Pool Heaters
10. Inputs to Payback Period Analysis
11. Rebuttable-Presumption Payback Period
F. National Impact Analysis--National Energy Savings and Net
Present Value Analysis
1. Shipments
a. Water Heaters
b. Direct Heating Equipment
c. Pool Heaters
d. Impacts of Standards on Shipments
2. Other Inputs
a. Base-Case Forecasted Efficiencies
b. Standards-Case Forecasted Efficiencies
c. Annual Energy Consumption
d. Site-to-Source Energy Conversion
e. Total Installed Costs and Operating Costs
f. Discount Rates
3. Other Inputs
a. Effects of Standards on Energy Prices
G. Consumer Subgroup Analysis
H. Manufacturer Impact Analysis
1. Overview
a. Phase 1: Industry Profile
b. Phase 2: Industry Cash-Flow Analysis
c. Phase 3: Subgroup Impact Analysis
2. GRIM Analysis
a. GRIM Key Inputs
b. GRIM Scenarios
3. Discussion of Comments
a. Responses to General Comments
b. Water Heater Comments
4. Manufacturer Interviews
a. Storage Water Heater Key Issues
b. Gas-Fired Instantaneous Water Heater Key Issues
c. Direct Heating Equipment Key Issues (Gas Wall Fan, Gas Wall
Gravity, Gas Floor, and Gas Room Direct Heating Equipment)
d. Direct Heating Equipment Key Issues (Gas Hearth Direct
Heating Equipment)
e. Pool Heater Key Issues
I. Employment Impact Analysis
J. Utility Impact Analysis
K. Environmental Analysis
1. Impacts of Standards on Emissions
2. Valuation of CO2 Emissions Reductions
3. Valuation of Other Emissions Reductions
V. Analytical Results
A. Trial Standard Levels
1. Water Heaters
2. Direct Heating Equipment
3. Gas-Fired Pool Heaters
B. Economic Justification and Energy Savings
1. Economic Impacts on Consumers
a. Life-Cycle Cost and Payback Period
b. Analysis of Consumer Subgroups
c. Rebuttable Presumption Payback
2. Economic Impacts on Manufacturers
a. Water Heater Cash-Flow Analysis Results
b. Direct Heating Equipment Cash-Flow Analysis Results
c. Pool Heaters Cash-Flow Analysis Results
d. Impacts on Employment
e. Impacts on Manufacturing Capacity
f. Cumulative Regulatory Burden
g. Impacts on Small Businesses
3. National Impact Analysis
a. Significance of Energy Savings
b. Net Present Value of Consumer Costs and Benefits
c. Net Present Value of Benefits from Energy Price Impacts
d. Impacts on Employment
4. Impact on Utility or Performance of Products
5. Impact of Any Lessening of Competition
6. Need of the Nation to Conserve Energy
7. Other Factors
C. Proposed Standards
1. Water Heaters
2. Direct Heating Equipment
3. Pool Heaters
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Order 12866
B. Review Under the Regulatory Flexibility Act
1. Water Heater Industry
2. Pool Heater Industry
3. Direct Heating Equipment Industry Characteristics
a. Description and Estimated Number of Small Entities Regulated
b. Reasons for the Proposed Rule
c. Objectives of, and Legal Basis for, the Proposed Rule
d. Description and Estimate of Compliance Requirements
e. Duplication, Overlap, and Conflict With Other Rules and
Regulations
f. Significant Alternatives to the Proposed Rule
C. Review Under the Paperwork Reduction Act of 1995
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
VII. Public Participation
A. Public Meeting
B. Procedure for Submitting Requests to Speak
C. Conduct of Public Meeting
D. Submission of Comments
E. Issues on Which DOE Seeks Comment
VIII. Approval of the Office of the Secretary
I. Summary of the Proposed Rule
The Energy Policy and Conservation Act (42 U.S.C. 6291 et seq.;
EPCA or the Act), as amended, provides that any new or amended energy
conservation standard DOE prescribes for certain consumer products,
including residential water heaters, direct heating equipment (DHE),
and pool heaters (collectively referred to in this document as the
``three heating products''), shall be designed to ``achieve the maximum
improvement in energy efficiency * * * which the Secretary determines
is technologically feasible and economically justified.'' (42 U.S.C.
6295(o)(2)(A)) Furthermore, the new or amended standard must ``result
in 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 the
three types of heating products listed above. Compliance with the
proposed standards would be required for all residential water heaters
listed in Table I.1 that are manufactured in or imported into the
United States on or after five years after the date of publication of
the final rule. The proposed standards would apply to all DHE and pool
heaters listed in Table I.1 that are manufactured in or imported into
the United States on or after three years after the date of publication
of the final rule. Table I.1 sets forth the proposed standards for the
products that are the subject of this rulemaking.
[[Page 65854]]
Table I.1--Proposed Amended Energy Conservation Standards for
Residential Water Heaters, Direct Heating Equipment, and Pool Heaters
------------------------------------------------------------------------
------------------------------------------------------------------------
Product class Proposed standard level
------------------------------------------------------------------------
Residential water heaters *
------------------------------------------------------------------------
Gas-fired Storage........... For tanks with a For tanks with a
Rated Storage Rated Storage
Volume at or below Volume above 60
60 gallons: EF = gallons: EF = 0.717
0.675 - (0.0012 x - (0.0019 x Rated
Rated Storage Storage Volume in
Volume in gallons). gallons).
Electric Storage............ For tanks with a For tanks with a
Rated Storage Rated Storage
Volume at or below Volume above 80
80 gallons: EF = gallons: EF = 1.088
0.96 - (0.0003 x - (0.0019 x Rated
Rated Storage Storage Volume in
Volume in gallons). gallons).
-------------------------------------------
Oil-fired Storage........... EF = 0.68 - (0.0019 x Rated Storage Volume
in gallons).
Gas-fired Instantaneous..... EF = 0.82 - (0.0019 x Rated Storage Volume
in gallons).
------------------------------------------------------------------------
Product class Proposed standard level
------------------------------------------------------------------------
Direct heating equipment **
------------------------------------------------------------------------
Gas wall fan type up to 42,000 AFUE = 76%
Btu/h.
Gas wall fan type over 42,000 Btu/ AFUE = 77%
h.
Gas wall gravity type up to AFUE = 70%
27,000 Btu/h.
Gas wall gravity type over 27,000 AFUE = 71%
Btu/h up to 46,000 Btu/h.
Gas wall gravity type over 46,000 AFUE = 72%
Btu/h.
Gas floor up to 37,000 Btu/h..... AFUE = 57%
Gas floor over 37,000 Btu/h...... AFUE = 58%
Gas room up to 20,000 Btu/h...... AFUE = 62%
Gas room over 20,000 Btu/h up to AFUE = 67%
27,000 Btu/h.
Gas room over 27,000 Btu/h up to AFUE = 68%
46,000 Btu/h.
Gas room over 46,000 Btu/h....... AFUE = 69%
Gas hearth up to 20,000 Btu/h.... AFUE = 61%
Gas hearth over 20,000 Btu/h and AFUE = 66%
up to 27,000 Btu/h.
Gas hearth over 27,000 Btu/h and AFUE = 67%
up to 46,000 Btu/h.
Gas hearth over 46,000 Btu/h..... AFUE = 68%
------------------------------------------------------------------------
Pool heaters
------------------------------------------------------------------------
Gas-fired........................ Thermal Efficiency = 84%
------------------------------------------------------------------------
* EF is the ``energy factor,'' and the ``Rated Storage Volume'' equals
the water storage capacity of a water heater (in gallons), as
specified by the manufacturer.
** Btu/h is ``British thermal units per hour'' and AFUE is ``Annual Fuel
Utilization Efficiency.''
DOE's analyses indicate that the proposed standards would save a
significant amount of energy--an estimated 2.85 quads of cumulative
energy over a 30-year period. This amount is equivalent to 61 days of
U.S. gasoline use. Breaking these figures down by product type, the
national energy savings of the proposed standards is estimated to be
2.60 quads for residential water heaters, 0.22 quads for DHE, and 0.03
quads for pool heaters.
The cumulative national net present value (NPV) of total consumer
costs and savings from the proposed standards (in 2008$) ranges from
$5.73 billion (at 7-percent discount rate) to $18.1 billion (at 3-
percent discount rate). This is the estimated total value of future
operating-cost savings minus the estimated increased product and
installation costs, discounted to 2010.
The NPV of the proposed standards for water heaters ranges from
$4.79 billion (7-percent discount rate) to $15.6 billion (3-percent
discount rate). DOE estimates the industry net present value (INPV) for
water heaters to be approximately $1,455 million in 2008$. If DOE
adopts the proposed standards, it estimates U.S. water heater
manufacturers will lose between 0.2 percent and 5.6 percent of the
INPV, which is approximately -$2.4 to -$81.0 million. However, the NPV
for consumers (at the 7-percent discount rate) is 59 to 1996 times
larger than the industry losses due to the proposed standards with the
7-percent discount rate, and 193 to 6500 times larger than the industry
losses due to the proposed standards with the 3-percent discount rate.
For DHE, the NPV of the proposed standards ranges from $0.91
billion (7-percent discount rate) to $2.22 billion (3-percent discount
rate). DOE estimates the INPV for DHE to be approximately $104 million
in 2008$. If DOE adopts the proposed standards, it estimates U.S. DHE
manufacturers will lose between 1.9 percent and 5.9 percent of the
INPV, which is approximately -$2.0 to -$6.2 million. However, the NPV
for consumers (at the 7-percent discount rate) is 147 to 455 times
larger than the industry losses due to the proposed standards with the
7-percent discount rate, and 358 to 1,110 times larger than the
industry losses due to the proposed standards with the 3-percent
discount rate.
For pool heaters, the NPV of the proposed standard ranges from
$0.03 billion (7-percent discount rate) to $0.25 billion (3-percent
discount rate). DOE estimates the INPV for pool heaters to be
approximately $61.4 million in 2008$. If DOE adopts the proposed
standards, it expects the impacts on U.S. pool heater manufacturers
will be between a gain of 0.9 percent and a loss of 12.1 percent of the
INPV, which is approximately -$0.5 million to -$7.5 million. However,
the NPV for consumers (at the seven-percent discount rate) is 4 to 60
times larger than the industry losses due to the proposed standards at
the 7-percent discount rate, and 33 to 498 times larger than the
industry losses due
[[Page 65855]]
to the proposed standards at the 3-percent discount rate.
The economic impacts of the proposed standards on individual
consumers (i.e., the average life-cycle cost (LCC) savings) are
predominately positive. For water heaters, DOE projects that the
average LCC impact is a gain of $68 for gas-fired storage water
heaters, $39 for electric storage water heaters, and $395 for oil-fired
storage water heaters, and no change for gas-fired instantaneous water
heaters. For DHE, DOE projects that the average LCC impact for
consumers is a gain of $104 for gas wall fan DHE, $192 for gas wall
gravity DHE, $13 for gas floor DHE, $143 for gas room DHE, and $96 for
gas hearth DHE. For pool heaters, DOE projects that the average LCC
impact for consumers is a loss of $13 (which represents only 0.2
percent of the average total LCC).
In addition, the proposed standards would be expected to provide
significant environmental benefits. The proposed standards would
potentially result in cumulative greenhouse gas emission reductions of
167 million tons (Mt) of carbon dioxide (CO2) from 2013 to
2045. Specifically, the proposed standards for water heaters would
reduce CO2 emissions by 154 Mt; the proposed standards for
DHE would reduce CO2 emissions by 8.5 Mt; and the proposed
standard for pool heaters would reduce CO2 emissions by 4.2
Mt. For the three types of heating products together, DOE estimates
that the range of the monetized value of CO2 emission
reductions based on global estimates of the value of avoided
CO2 is $0.399 billion to $4.386 billion at a 7-percent
discount rate and $0.902 billion to $9.925 billion at a 3-percent
discount rate.
The proposed standards would also be expected to result in
reduction in cumulative nitrogen oxides (NOX) emissions of
129 kilotons (kt). Specifically, the proposed water heater standards
would result in cumulative NOX emissions reductions of 118
kt; the proposed standards for DHE would result in 7.7 kt of
NOX emissions reductions; and the proposed standard for pool
heaters would result in 3.7 kt of NOX emissions reductions.
The proposed standards for heating products would also be expected
to result in power plant mercury (Hg) emissions reductions. For water
heaters, cumulative Hg emissions would be reduced by 0.20 tons (t). The
proposed standards for DHE and pool heaters would be expected to have a
negligible impact on mercury emissions.
The benefits and costs of today's proposed rule can also be
expressed in terms of annualized values. The annualized values refer to
consumer operating cost savings, consumer incremental product and
installation costs, the quantity of emissions reductions for
CO2, NOX, and Hg, and the monetary value of
emissions reductions. DOE calculated annualized values using discount
rates of three percent and seven percent. Although DOE calculated
annualized values, this does not imply that the time-series of cost and
benefits from which the annualized values were determined are a steady
stream of payments.
Table I.2, Table I.3, and Table I.4 present the annualized values
for the standards proposed for water heaters, DHE, and pool heaters,
respectively. The tables also present the annualized net benefit that
results from summing the two monetary benefits and subtracting the
consumer incremental product and installation costs. Although summing
the value of operating cost savings with the value of CO2
reductions (and other emissions reductions) provides a valuable
perspective, please note the following. The operating cost savings are
domestic U.S. consumer monetary savings found in market transactions,
but in contrast, the CO2 value is based on an estimate of
imputed marginal social cost of carbon (SCC), which is meant to reflect
the global benefits of CO2 reductions. In addition, the
assessments of operating cost savings and CO2 savings are
performed with different computer models, leading to different time
frames for analysis. The operating cost savings are measured for the
lifetime of appliances shipped in 2015-2045 or 2013-2043. The value of
CO2, on the other hand is meant to reflect the present value
of all future climate-related impacts, even those beyond 2065.
Table I.2--Annualized Benefits and Costs of Proposed Standards for Water Heaters (TSL 4)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Primary estimate (AEO Low estimate (AEO low- High estimate (AEO
reference case) growth case) high-growth case)
Category Unit -----------------------------------------------------------------------
7% 3% 7% 3% 7% 3%
--------------------------------------------------------------------------------------------------------------------------------------------------------
Benefits
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Operating Cost Savings.............. Million 2008$................... 1487.1 1842.4 1383.7 1708.4 1590.5 1976.2
Quantified Emissions Reductions............... CO2 (Mt)........................ 4.58 4.92 5.34 5.28 0.61 1.04
NOX (kt)........................ 3.54 3.79 4.17 4.11 0.58 0.92
Hg (t).......................... 0.009 0.008 (0.003) (0.011) 0.010 0.013
Monetized Avoided Emissions Reductions * CO2 (at $20/t).................. 157.1 187.3 184.8 222.1 20.2 41.9
(Million 2008$).
NOX............................. 8.2 9.1 9.7 10.9 0.4 1.6
Hg.............................. 0.1 0.1 (0.1) (0.1) 0.1 0.2
--------------------------------------------------------------------------------------------------------------------------------------------------------
Costs
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Incremental Product and Installation Million 2008$................... 945.5 917.3 894.4 861.7 997.0 973.4
Costs.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Net Benefits
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Value **............................ Million 2008$................... 698.8 1112.4 674.1 1068.9 613.7 1044.7
--------------------------------------------------------------------------------------------------------------------------------------------------------
* For CO2, benefits reflect value of $20/t, which is in the middle of the values considered by DOE for valuing the potential global benefits resulting
from reduced CO2 emissions. For NOX and Hg, the benefits reflect values of $2,491/t and $17 million/t, respectively. These values are the midpoint of
the range considered by DOE.
** Monetized Value does not include monetized avoided emissions reductions for NOX and Hg.
[[Page 65856]]
Table I.3--Annualized Benefits and Costs of Proposed Standards for Direct Heating Equipment (TSL 3)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Primary estimate (AEO Low estimate (AEO low- High estimate (AEO
reference case) growth case) high-growth case)
Category Unit -----------------------------------------------------------------------
7% 3% 7% 3% 7% 3%
--------------------------------------------------------------------------------------------------------------------------------------------------------
Benefits
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Operating Cost Savings.............. Million 2008$................... 132.2 164.4 126.4 156.9 136.2 169.6
Quantified Emissions Reductions............... CO2 (Mt)........................ 0.24 0.27 0.43 0.46 0.13 0.14
NOX (kt)........................ 0.22 0.24 0.36 0.38 0.14 0.15
Hg (t).......................... 0.000 (0.001) 0.000 (0.001) 0.000 0.000
Monetized Avoided CO2 Value (at $20/t) .* Million 2008$................... 8.2 9.8 2.5 2.9 21.0 42.6
--------------------------------------------------------------------------------------------------------------------------------------------------------
Costs
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Incremental Product and Installation Million 2008$................... 41.8 40.6 41.8 40.6 41.8 40.6
Costs.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Net Benefits
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Value............................... Million 2008$................... 98.5 133.5 87.1 119.2 115.4 171.6
--------------------------------------------------------------------------------------------------------------------------------------------------------
* For CO2, benefits reflect value of $20/t, which is in the middle of the values considered by DOE for valuing the potential global benefits resulting
from reduced CO2 emissions. For NOX and Hg, the annual benefits are very small and are thus not reported in the table.
Table I.4--Annualized Benefits and Costs of Proposed Standards for Pool Heaters (TSL 4)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Primary estimate (AEO Low estimate (AEO low- High estimate (AEO
reference case) growth case) high-growth case)
Category Unit -----------------------------------------------------------------------
7% 3% 7% 3% 7% 3%
--------------------------------------------------------------------------------------------------------------------------------------------------------
Benefits
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Operating Cost Savings.............. Million 2008$................... 59.88 68.79 57.29 65.66 61.62 70.86
Quantified Emissions Reductions............... CO2 (Mt)........................ 0.13 0.13 0.16 0.17 0.09 0.10
NOX (kt)........................ 0.112 0.119 0.134 0.143 0.085 0.091
Hg (t).......................... 0.000 0.000 (0.000) (0.001) (0.000) 0.000
Monetized Avoided CO2 Value (at $20/t).* Million 2008$................... 4.20 4.84 5.24 6.08 3.01 3.47
--------------------------------------------------------------------------------------------------------------------------------------------------------
Costs
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Incremental Product and Installation 2008$........................... 56.66 54.59 56.66 54.59 56.66 54.59
Costs.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Net Benefits
--------------------------------------------------------------------------------------------------------------------------------------------------------
Monetized Value............................... Million 2008$................... 7.41 19.04 5.88 17.15 7.97 19.74
--------------------------------------------------------------------------------------------------------------------------------------------------------
* For CO2, benefits reflect value of $20/t, which is in the middle of the values considered by DOE for valuing the potential global benefits resulting
from reduced CO2 emissions. For NOX and Hg, the annual benefits are very small and are thus not reported in the table.
DOE has tentatively concluded that the proposed standards represent
the maximum improvement in energy efficiency that is technologically
feasible and economically justified, and would result in significant
conservation of energy. Products achieving these standard levels are
already commercially available. Based on the analyses culminating in
this proposal, DOE found the benefits to the Nation of the proposed
standards (energy savings, consumer LCC savings, national NPV increase,
and emission reductions) outweigh the burdens (loss of INPV and LCC
increases for some consumers). DOE considered higher efficiency levels
as trial standard levels, and is still considering them in this
rulemaking; however, DOE has tentatively concluded that the burdens of
the higher efficiency levels would outweigh the benefits. With that
said, based on consideration of public comments DOE receives in
response to this notice and related information, DOE may adopt
efficiency levels in the final rule that are either higher or lower
than the proposed standards, or some level(s) in between the proposed
standards and other efficiency levels presented.
DOE is proposing TSL 4 for residential water heaters as the level
which it has tentatively concluded meet the applicable statutory
criteria (i.e., the highest level that is technologically feasible,
economically justified, and would result in significant conservation of
energy). Based upon public comments and any accompanying data
submissions, DOE would strongly consider other TSLs (as presented in
this NOPR or at some level in between), some of which might provide an
even higher level of energy savings and promote a market for advanced
water heating technologies, including heat pump and condensing water
heaters. Accordingly, DOE is presenting a variety of issues throughout
today's notice upon which it is seeking
[[Page 65857]]
comment which will bear upon its consideration of TSL 5 or TSL 6 for
residential water heaters in the final rule.
II. Introduction
A. Consumer Overview
EPCA currently prescribes energy conservation standards for the
three heating products that are the subject of this rulemaking. DOE is
proposing to raise the standards for the products shown in Table I.1.
The proposed standards would apply to residential water heaters
manufactured or imported on or after five years after the final rule
publication date (i.e., approximately March 31, 2015). The proposed
standards would apply to DHE and pool heaters manufactured or imported
on or after three years after the final rule publication date (i.e.,
approximately March 31, 2013).
DOE's analyses suggest that consumers would realize benefits from
the proposed standards. Although DOE expects that the purchase price of
the more-efficient heating products would be higher than the average
prices of these products today, for most consumers, the energy
efficiency gains would result in lower energy costs that would more
than offset the higher purchase price. For water heaters, the median
payback period is 2.7 years for gas-fired storage water heaters, 5.8
years for electric storage water heaters, 0.5 years for oil-fired
storage water heaters, and 23.5 years for gas-fired instantaneous water
heaters. For DHE, the median payback period is 6.0 years for gas wall
fan DHE, 8.3 years for gas wall gravity DHE, 14.7 years for gas floor
DHE, 5.3 years for gas room DHE and 0.0 years for gas hearth DHE. (The
reason that the median payback period for gas hearth DHE is zero is
because for about two-thirds of the consumers, there is no incremental
cost to get to the proposed standard level). For pool heaters, the
median payback period is 13.0 years.
When the overall net savings are summed over the lifetime of these
products, water heater consumers will save, on average, $68 for gas-
fired storage water heaters, $30 for electric storage water heaters,
$305 for oil-fired storage water heaters, and $0 for gas-fired
instantaneous water heaters, compared to their life-cycle expenditures
on base-case water heaters (i.e., the equipment expected to be
purchased in the absence of revised energy conservation standards).
(For gas-fired instantaneous water heaters, the average LCC for the
proposed standard level is the same as the average LCC in the base
case, so the savings are zero.) The average LCC impact for DHE
consumers is a gain of $104 for gas wall fan DHE, $192 for gas wall
gravity DHE, $13 for gas floor DHE, $143 for gas room DHE, and $96 for
gas hearth DHE, compared to their life-cycle expenditures on base-case
products. Pool heater consumers will see, on average, a slight increase
in their life-cycle costs, compared to their expenditures on base-case
products.
B. Authority
Title III of EPCA sets forth a variety of provisions designed to
improve energy efficiency. Part A \1\ of Title III (42 U.S.C. 6291-
6309) establishes the Energy Conservation Program for Consumer Products
Other Than Automobiles. The program covers consumer products and
certain commercial equipment (referred to hereafter as ``covered
products''), including the three types of heating products that are
subject to this rulemaking. (42 U.S.C. 6292(a)(4), (9) and (11)) EPCA
prescribes energy conservation standards for the three heating
products. (42 U.S.C. 6295(e)(1)-(3)) The statute further directs DOE to
conduct two cycles of rulemakings to determine whether to amend these
standards. (42 U.S.C. 6295(e)(4)) As explained in further detail in
section II.C, ``Background,'' this rulemaking represents the second
round of amendments to the water heater standards, and the first round
of amendments to the DHE and pool heater standards.
---------------------------------------------------------------------------
\1\ This part was originally titled Part B. It was redesignated
Part A in the United States Code for editorial reasons.
---------------------------------------------------------------------------
Under the Act, DOE's energy conservation program for covered
products consists essentially of three parts: (1) Testing; (2)
labeling; and (3) Federal energy conservation standards. The Federal
Trade Commission (FTC) is responsible for the labeling provisions for
consumer products, and DOE implements the remainder of the program.
Section 323 of the Act authorizes DOE, subject to certain criteria and
conditions, to develop test procedures to measure the energy
efficiency, energy use, or estimated annual operating cost of each
covered product. Manufacturers of covered products must use the DOE
test procedure as the basis for certifying to DOE that their products
comply with applicable energy conservation standards adopted under EPCA
and for representing the efficiency of those products. Similarly, DOE
must use these test procedures to determine whether the products comply
with standards adopted under EPCA. (42 U.S.C. 6293) The test procedures
for water heaters, unvented DHE, vented DHE, and pool heaters appear at
Title 10 Code of Federal Regulations (CFR) part 430, subpart B,
appendices E, G, O, and P, respectively.
EPCA provides criteria for prescribing amended standards for
covered products. As indicated above, any amended 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)) Furthermore, EPCA precludes DOE
from adopting any standard that would not result in significant
conservation of energy. (42 U.S.C. 6295(o)(3)(B)) Moreover, DOE may not
prescribe a standard for certain products (including the three heating
products) if no test procedure has been established. (42 U.S.C.
6295(o)(3)(A)) The Act also provides that, 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 do so 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 imposition of the
standard;
3. The total projected amount of energy (or, as applicable, water)
savings likely to result directly from the imposition of the standard;
4. Any lessening of the utility or the performance of the covered
products likely to result from the imposition of 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
imposition of the standard;
6. The need for national energy and water conservation; and
7. Other factors the Secretary considers relevant.
(42 U.S.C. 6295(o)(2)(B)(i)(I)-(VII))
Furthermore, EPCA contains what is commonly known as an ``anti-
backsliding'' provision, which prohibits
[[Page 65858]]
the Secretary from prescribing any amended 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 a new or amended 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) with 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))
Under 42 U.S.C. 6295(o)(2)(B)(iii), EPCA 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. * * *''
Under 42 U.S.C. 6295(q)(1), EPCA specifies requirements for
promulgation of a standard for a type or class of covered product that
has two or more subcategories. DOE must specify a different standard
level than that which applies generally to such type or class of
products ``for any group of covered products which have the same
function or intended use, if * * * 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'' than applies or will apply to the other products. (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))
Federal energy conservation requirements generally supersede State
laws or regulations concerning energy conservation testing, labeling,
and standards. (42 U.S.C. 6297(a)-(c)) However, DOE can grant waivers
of Federal preemption for particular State laws or regulations in
accordance with the procedures and other provisions of section 327(d)
of the Act. (42 U.S.C. 6297(d))
Finally, section 310(3) of the Energy Independence and Security Act
of 2007 (EISA 2007; Pub. L. 110-140) amended EPCA to prospectively
require that energy conservation standards address standby mode and off
mode energy use. Specifically, when DOE adopts new or amended standards
for a covered product after July 1, 2010, the final rule must, if
justified by the criteria for adoption of standards in section 325(o)
of EPCA, incorporate standby mode and off mode energy use into a single
standard if feasible, or otherwise adopt a separate standard for such
energy use for that product. (42 U.S.C. 6295(gg)(3)) Because the final
rule in this rulemaking is scheduled for adoption by March 2010, this
requirement does not apply in this rulemaking, and DOE has not
attempted to address the standby mode or off mode energy use here. DOE
is currently working on a test procedure rulemaking to address standby
mode and off mode energy consumption for the three types of heating
products that are the subject of this rulemaking.
C. Background
1. Current Standards
a. Water Heaters
On January 17, 2001, DOE prescribed the current energy conservation
standards for residential water heaters manufactured on or after
January 20, 2004. 66 FR 4474. This final rule completed the first
amended standards rulemaking for water heaters required under 42 U.S.C.
6295(e)(4)(A). The standards consist of minimum energy factors (EF)
that vary based on the storage volume of the water heater, the type of
energy it uses (i.e., gas, oil, or electricity), and whether it is a
storage, instantaneous, or tabletop model. 10 CFR 430.32(d). The water
heater energy conservation standards are set forth in Table II.1 below.
Table II.1--Current Federal Energy Conservation Standards for
Residential Water Heaters
------------------------------------------------------------------------
Energy factor as of January 20,
Product class 2004
------------------------------------------------------------------------
1. Gas-Fired Storage Water Heater...... EF = 0.67 - (0.0019 x Rated
Storage Volume in gallons).
2. Oil-Fired Storage Water Heater...... EF = 0.59 - (0.0019 x Rated
Storage Volume in gallons).
3. Electric Storage Water Heater....... EF = 0.97 - (0.00132 x Rated
Storage Volume in gallons).
4. Tabletop Water Heater............... EF = 0.93 - (0.00132 x Rated
Storage Volume in gallons).
5. Gas-Fired Instantaneous Water Heater EF = 0.62 - (0.0019 x Rated
Storage Volume in gallons).
6. Instantaneous Electric Water Heater. EF = 0.93 - (0.00132 x Rated
Storage Volume in gallons).
------------------------------------------------------------------------
b. Direct Heating Equipment
EPCA prescribes the energy conservation standards for DHE, which
apply to gas-fired products manufactured on or after January 1, 1990.
(42 U.S.C. 6295(e)(3)) These standards consist of several minimum
annual fuel utilization efficiency (AFUE) levels, each of which applies
to units of a particular type (i.e., wall fan, wall gravity, floor,
room) and heating capacity range. Id. These statutory standards have
been codified in DOE's regulations at 10 CFR 430.32(i). The DHE energy
conservation standards are set forth in Table II.2 below. DOE notes
that while electric DHE are available, standards for these products are
outside the scope of today's rulemaking. See IV.A.1.b for a more
detailed discussion of DHE coverage under EPCA.
[[Page 65859]]
Table II.2--Current Federal Energy Conservation Standards for Direct
Heating Equipment
------------------------------------------------------------------------
Annual fuel
utilization
Direct heating equipment Product class Btu/h efficiency, as
design type of Jan. 1, 1990
%
------------------------------------------------------------------------
Gas Wall Fan.................. Up to 42,000.......... 73
Over 42,000........... 74
Gas Wall Gravity.............. Up to 10,000.......... 59
Over 10,000 and up to 60
12,000.
Over 12,000 and up to 61
15,000.
Over 15,000 and up to 62
19,000.
Over 19,000 and up to 63
27,000.
Over 27,000 and up to 64
46,000.
Over 46,000........... 65
Gas Floor..................... Up to 37,000.......... 56
Over 37,000........... 57
Gas Room...................... Up to 18,000.......... 57
Over 18,000 and up to 58
20,000.
Over 20,000 and up to 63
27,000.
Over 27,000 and up to 64
46,000.
Over 46,000........... 65
------------------------------------------------------------------------
c. Pool Heaters
EPCA requires pool heaters manufactured on or after January 1, 1990
to have a thermal efficiency no less than 78 percent. The thermal
efficiency for this product is measured by testing in accordance with
the DOE test procedure for pool heaters codified in 10 CFR 430, subpart
B, Appendix P. The statutory standard for pool heaters has been
codified in DOE's regulations at 10 CFR 430.32(k).
2. History of Standards Rulemaking for Water Heaters, Direct Heating
Equipment, and Pool Heaters
Before being amended by the National Appliance Energy Conservation
Act of 1987 (NAECA; Pub. L. 100-12), Title III of EPCA included water
heaters and home heating equipment as covered products. NAECA's
amendments to EPCA included replacing the term ``home heating
equipment'' with ``direct heating equipment,'' adding pool heaters as a
covered product, establishing energy conservation standards for these
two products as well as residential water heaters, and requiring that
DOE determine whether these standards should be amended. (42 U.S.C.
6295(e)(1)-(4)) As indicated above, DOE amended the statutorily-
prescribed standards for water heaters in 2001 (66 FR 4474 (Jan. 17,
2001)), but has not amended the statutory standards for DHE or pool
heaters.
DOE initiated this rulemaking on September 27, 2006, by publishing
on its Web site its ``Rulemaking Framework for Residential Water
Heaters, Direct Heating Equipment, and Pool Heaters.'' (A PDF of the
framework document is available at https://www.eere.energy.gov/buildings/appliance_standards/residential/pdfs/heating_equipmentframework_092706.pdf.) DOE also published a notice announcing
the availability of the framework document and a public meeting and
requesting comments on the matters raised in the document. 71 FR 67825
(Nov. 24, 2006). The framework document described the procedural and
analytical approaches that DOE anticipated using to evaluate potential
energy conservation standards for the three heating products and
identified various issues to be resolved in conducting the rulemaking.
DOE held the public meeting on January 16, 2007, where it:
Presented the contents of the framework document; described the
analyses it planned to conduct during the rulemaking; sought comments
from interested parties on these subjects; and in general, sought to
inform interested parties about, and facilitate their involvement in,
the rulemaking. Interested parties that participated in the public
meeting discussed the following issues: the scope of coverage for the
rulemaking; product classes; efficiency levels analyzed in the
engineering analysis; installation, repair, and maintenance costs; and
product and fuel switching. At the meeting and during the public
comment period, DOE received many comments that helped DOE identify and
resolve the issues involved in this rulemaking to consider amended
energy conservation standards for the three types of heating products.
DOE then gathered additional information and performed preliminary
analyses to help develop the potential energy conservation standards
for the three heating products. This process culminated in DOE's
announcement of another public meeting to discuss and receive comments
on the following matters: The product classes DOE planned to analyze;
the analytical framework, models, and tools that DOE has been using to
evaluate standards; the results of the preliminary analyses DOE
performed; and potential standard levels that DOE could consider. 74 FR
1643 (Jan. 13, 2009) (the January 2009 notice). DOE also invited
written comments on these subjects and announced the availability of a
preliminary technical support document (preliminary TSD) to inform
interested parties and enable them to provide comments. Id. (The
preliminary TSD is available at: https://www1.eere.energy.gov/buildings/appliance_standards/residential/water_pool_heaters_prelim_tsd.html.) DOE stated its interest in receiving comments on other
relevant issues that participants believe DOE should address in this
NOPR, which would affect energy conservation standards for the three
heating products. Id. at 1646.
The preliminary TSD provided an overview of the activities DOE
undertook in developing potential standard levels for the three heating
products and discussed the comments DOE received in response to the
framework document. It also described the analytical framework that DOE
used (and continues to use in this rulemaking), including a description
of the methodology, the analytical tools, and the relationships among
the various analyses that are part of the rulemaking. The preliminary
TSD described in detail each analysis DOE performed up to that point,
including inputs, sources,
[[Page 65860]]
methodologies, and results. DOE examined each of the three heating
products in each of the following analyses:
A market and technology assessment addressed the scope of
this rulemaking (i.e., which types of heating products this rulemaking
covers), identified the potential classes for each product,
characterized the markets for these products, and reviewed techniques
and approaches for improving product efficiency.
A screening analysis reviewed technology options to
improve the efficiency of each of the three heating products and
weighed these options against DOE's four prescribed screening criteria
(i.e., technological feasibility; practicability to manufacture,
install, and service; adverse impacts on product utility or product
availability; and adverse impacts on health or safety).
An engineering analysis estimated the manufacturer selling
prices (MSPs) associated with more efficient water heaters, DHE, and
pool heaters.
An energy use analysis estimated the annual energy use in
the field of each of the three heating products.
A markups analysis developed factors to convert estimated
MSPs derived from the engineering analysis to consumer prices.
A life-cycle cost 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 a given standard.
A payback period (PBP) analysis estimated the amount of
time it takes consumers to recover the higher purchase expense of more
energy efficient products through lower operating costs.
A shipments analysis estimated shipments of each of the
three heating products over the time period examined in the analysis
(i.e., 2015-2045 for water heaters and 2013-2043 for DHE and pool
heaters) under both a base-case scenario (i.e., assuming no new
standards) and a standards-case scenario (i.e., assuming new standards
at the various levels under consideration). The shipments analysis
provides key inputs to the national impact analysis (NIA).
A national impact analysis assessed the aggregate impacts
at the national level of potential energy conservation standards for
each of the three heating products, as measured by the net present
value of total consumer economic impacts and national energy savings.
A preliminary manufacturer impact analysis took the
initial steps in evaluating the effects on manufacturers of potential
new efficiency standards.
In the January 2009 notice, DOE summarized in detail the nature and
function of the following analyses: (1) Engineering, (2) energy use
characterization, (3) markups to determine installed prices, (4) LCC
and PBP analyses, and (5) national impact analysis. 74 FR 1643, 1645-46
(Jan. 13, 2009).
The public meeting announced in the January 2009 notice took place
on February 9, 2009. At this meeting, DOE presented the methodologies
and results of the analyses set forth in the preliminary TSD. The major
topics discussed at the February 2009 public meeting included the
product classes for the rulemaking, the treatment of ultra-low
NOX water heaters, heat pump water heaters screening
considerations, installation costs and concerns for heat pump water
heaters, the manufacturing costs for max-tech products, pool heater
shipments, the energy-use adjustment for gas-fired instantaneous water
heaters, and the compliance dates for amended standards. The comments
received since publication of the January 2009 notice, including those
received at the February 2009 public meeting, have contributed to DOE's
proposed resolution of the issues in this rulemaking. This NOPR quotes
and summarizes many of these comments, and responds to the issues they
raised. (A parenthetical reference at the end of a quotation or
paraphrase provides the location of the relevant source in the public
record.)
III. General Discussion
A. Test Procedures
As noted above, DOE's current test procedures for water heaters,
vented DHE, and pool heaters appear at Title 10 Code of Federal
Regulations (CFR) part 430, subpart B, appendices E, O, and P,
respectively. DOE uses these test procedures to determine whether the
products comply with standards adopted under EPCA. (42 U.S.C. 6293)
1. Water Heaters
During the preliminary analysis, DOE received a number of comments
on the test procedure for residential water heaters. Edison Electric
Institute (EEI) stated that DOE should modify the values for hot water
use and the number of daily draws in the water heater test procedure to
more closely resemble field conditions (i.e., include more shorter
draws, rather than fewer longer draws), and SEISCO INTERNATIONAL
(SEISCO) recommended the adoption of a testing protocol for water
heaters that can best simulate real world usage patterns. (EEI, No. 40
at p.5; SEISCO, No. 41 at p. 3) \2\ Southern Company (Southern), Bock
Water Heaters (Bock), and EEI all stated that DOE needs to revise the
test procedure to account for the actual performance of gas-fired
instantaneous water heaters. (Southern, No. 50 at p. 2; Bock, No. 53 at
p. 3; EEI, No. 40 at