Energy Conservation Program for Commercial and Industrial Equipment: Packaged Terminal Air Conditioner and Packaged Terminal Heat Pump Energy Conservation Standards, 58772-58830 [E8-23312]
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
DEPARTMENT OF ENERGY
10 CFR Part 431
[Docket Number: EERE–2007–BT–STD–
0012]
RIN 1904–AB44
Energy Conservation Program for
Commercial and Industrial Equipment:
Packaged Terminal Air Conditioner
and Packaged Terminal Heat Pump
Energy Conservation Standards
Office of Energy Efficiency and
Renewable Energy, Department of
Energy.
ACTION: Final rule.
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AGENCY:
SUMMARY: The Department of Energy
(DOE) has determined that its adoption
of amended energy conservation
standards for commercial standard size
packaged terminal air conditioners
(PTACs) and packaged terminal heat
pumps (PTHPs), at efficiency levels
more stringent than those in American
Society of Heating, Refrigerating, and
Air-Conditioning Engineers (ASHRAE)/
Illuminating Engineering Society of
North America (IESNA) Standard 90.1–
1999, is supported by clear and
convincing evidence that such
standards would result in significant
additional conservation of energy and
are technologically feasible and
economically justified. On this basis,
DOE is today amending the existing
energy conservation standards for these
types of equipment. In addition, DOE
has determined that its adoption of
amended energy conservation standards
more stringent than the efficiency levels
specified by ASHRAE Standard 90.1–
1999 for non-standard size PTACs and
PTHPs is not supported by clear and
convincing evidence, thus, DOE is
adopting the efficiency levels in
ASHRAE Standard 90.1–1999 for nonstandard size PTACs and PTHPs in
today’s final rule.
DATES: The effective date of this rule is
November 6, 2008. The standards
established in today’s final rule will be
applicable starting October 8, 2012 for
standard size PTACs and PTHPs. The
standards established in today’s final
rule will be applicable starting October
7, 2010 for non-standard size PTACs
and PTHPs.
ADDRESSES: For access to the docket to
read background documents, the
technical support document, transcripts
of the public meetings in this
proceeding, or comments received, visit
the U.S. Department of Energy, Resource
Room of the Building Technologies
Program, 950 L’Enfant Plaza, SW., 6th
Floor, Washington, DC 20024, (202)
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586–2945, between 9 a.m. and 4 p.m.,
Monday through Friday, except Federal
holidays. For more information about
visiting the Resource Room, please call
Ms. Brenda Edwards at (202) 586–2945.
(Note: DOE’s Freedom of Information
Reading Room no longer houses
rulemaking materials.) You may also
obtain copies of the final rule notice in
this proceeding, related documents (e.g.,
the notice of proposed rulemaking and
technical support document DOE used
to reassess whether to adopt certain
efficiency levels in ASHRAE Standard
90.1), draft analyses, public meeting
materials, and related test procedure
documents from the Office of Energy
Efficiency and Renewable Energy’s Web
site at https://www.eere.energy.gov/
buildings/appliance_standards/
commercial/packaged_ac_hp.html.
FOR FURTHER INFORMATION CONTACT: Wes
Anderson, Project Manager, Energy
Conservation Standards for Packaged
Terminal Air Conditioners and
Packaged Terminal Heat Pumps, U.S.
Department of Energy, Energy Efficiency
and Renewable Energy, Building
Technologies Program, EE–2J, 1000
Independence Avenue, SW.,
Washington, DC 20585–0121. Phone:
(202) 586–7335. E-mail:
Wes.Anderson@ee.doe.gov.
Francine Pinto, Esq., or Michael Kido,
Esq., U.S. Department of Energy, Office
of General Counsel, GC–72, 1000
Independence Avenue, SW.,
Washington, DC 20585. Phone: (202)
586–9507. E-mail: Francine.Pinto@hq.
doe.gov or Michael.Kido@hq.doe.gov.
SUPPLEMENTARY INFORMATION:
I. Summary of the Final Rule and Its Benefits
A. The Standard Levels
B. Current Federal Standards for Packaged
Terminal Air Conditioners and Packaged
Terminal Heat Pumps
C. Benefits to Customers of Packaged
Terminal Air Conditioners and Packaged
Terminal Heat Pumps
D. Impact on Manufacturers
E. National Benefits
F. Other Considerations
G. Conclusion
II. Introduction
A. Authority
B. Background
1. Current Standards
2. History of Standards Rulemaking for
Packaged Terminal Equipment
III. General Discussion
A. Test Procedures
B. Technological Feasibility
1. General
2. Maximum Technologically Feasible
Levels
C. Energy Savings
D. Economic Justification
1. Economic Impact on Commercial
Consumers and Manufacturers
2. Life-Cycle Costs
3. Energy Savings
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4. Lessening of Utility or Performance of
Equipment
5. Impact of Any Lessening of Competition
6. Need of the Nation To Conserve Energy
7. Other Factors
IV. Analysis Methodology and Discussion of
Comments on Analysis Methodology
A. Market and Technology Assessment
1. Equipment Classes—Generally
2. Comments
B. Screening Analysis
1. Scroll Compressors
2. ECM Motors
3. Fan Motors
4. Micro-Channel Heat Exchangers
5. Thermal Expansion Valves
C. Engineering Analysis
1. Material Prices for the Cost Model
2. Impacts of the Refrigerant Phaseout on
PTAC and PTHP Equipment
Performance
3. Manufacturer Production Cost Increases
With R–410A
D. Energy Use Characterization
E. Life-Cycle Cost Analysis
1. Equipment Prices
2. Installation Costs
3. Annual Energy Use
4. Electricity Prices
5. Maintenance Costs
6. Repair Costs
7. Equipment Lifetime
8. Discount Rate
F. National Impact Analysis—National
Energy Savings and Net Present Value
Analysis
1. Shipments Analysis
2. Base Case and Standards Case
Forecasted Distribution of Efficiencies
G. Manufacturer Impact Analysis
1. GRIM Input Updates
2. Cumulative Regulatory Burden
3. Employment Impacts
H. Employment Impact Analysis
I. Utility Impact Analysis
J. Environmental Analysis
K. Other Comments
1. Burdens on Small, Non-Standard Size
PTAC and PTHP Manufacturers
2. PTAC and PTHP Labeling
V. Analytical Results and Conclusions
A. Trial Standard Levels
B. Significance of Energy Savings
C. Economic Justification
1. Economic Impact on Commercial
Consumers
2. Economic Impact on Manufacturers
3. National Net Present Value and Net
National Employment
4. Impact on Utility or Performance of
Equipment
5. Impact of Any Lessening of Competition
6. Need of the Nation to Conserve Energy
7. Other Factors
D. Conclusion
1. Standard Size PTACs and PTHPs
2. Non-Standard Size PTACs and PTHPs
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Order 12866
B. Review Under the Regulatory Flexibility
Act
1. Reasons for the Final Rule
2. Objectives of, and Legal Basis for, the
Rule
3. Description and Estimated Number of
Small Entities Regulated
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4. Description and Estimate of Compliance
Requirements
5. Significant Issues Raised by Public
Comments
6. Steps DOE Has Taken To Minimize the
Economic Impact on Small, NonStandard Size PTAC and PTHP
Manufacturers
C. Review Under the Paperwork Reduction
Act
D. Review Under the National
Environmental Policy Act
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 of 1999
I. Review Under Executive Order 12630
J. Review Under the Treasury and General
Government Appropriations Act of 2001
K. Review Under Executive Order 13211
L. Review Under the Information Quality
Bulletin for Peer Review
M. Congressional Notification
VII. Approval of the Office of the Secretary
I. Summary of the Final Rule and Its
Benefits
A. The Standard Levels
The Energy Policy and Conservation
Act, as amended (EPCA), (42 U.S.C.
6291, et seq.), establishes mandatory
energy conservation standards for
certain commercial equipment covered
by the American Society of Heating,
Refrigerating, and Air-Conditioning
Engineers (ASHRAE) and the
Illuminating Engineering Society of
North America (IESNA) Standard 90.1,
including packaged terminal air
conditioners (PTACs) and packaged
terminal heat pumps (PTHPs)
(collectively referred to as ‘‘packaged
terminal equipment’’). EPCA states that
the Department of Energy (DOE) may
prescribe amended standards for this
equipment that exceed the stringency of
efficiency levels contained in
amendments to ASHRAE Standard 90.1,
only if DOE determines by rule that any
such standard ‘‘would result in
significant additional conservation of
energy and is technologically feasible
and economically justified.’’ (42 U.S.C.
6313(a)(6)(A)(ii)(II)) This determination
must be ‘‘supported by clear and
convincing evidence.’’ Id. If DOE is
unable to find that clear and convincing
evidence exists that a more stringent
efficiency level than the efficiency level
contained in ASHRAE Standard 90.1
58773
would result in a significant additional
energy savings and is technologically
feasible and economically justified, then
EPCA states DOE must establish an
amended uniform national standard for
the product at the minimum level
specified in the amended ASHRAE/IES
Standard 90.1. (42 U.S.C.
6313(a)(6)(A)(ii)(I)) The standards in
today’s final rule, which apply to all
packaged terminal equipment, satisfy
these requirements and will achieve the
maximum improvements in energy
efficiency that are technologically
feasible and economically justified. (See
42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(A).)
Table I.1 shows the amended energy
conservation standards that DOE is
adopting today. These amended energy
conservation standards will apply to
standard size PTACs and PTHPs
manufactured for sale in the United
States, or imported to the United States,
on or after October 8, 2012 and nonstandard size PTACs and PTHPs
manufactured for sale in the United
States, or imported to the United States,
on or after October 7, 2010.
TABLE I.1—AMENDED ENERGY CONSERVATION STANDARDS FOR PTACS AND PTHPS
Equipment class
Energy conservation standards *
Equipment
Category
Cooling capacity
(British thermal units per hour [Btu/h])
PTAC .................
Standard Size ** .....................................
<7,000 ....................................................
7,000–15,000 .........................................
>15,000 ..................................................
EER = 11.7
EER = 13.8¥(0.300 × Cap ††)
EER = 9.3
Non-Standard Size † ...............................
<7,000 ....................................................
7,000–15,000 .........................................
>15,000 ..................................................
EER = 9.4
EER = 10.9 ¥ (0.213 × Cap ††)
EER = 7.7
Standard Size ** .....................................
<7,000 ....................................................
EER = 11.9
COP = 3.3
EER = 14.0 ¥ (0.300 × Cap ††)
COP = 3.7 ¥ (0.052 × Cap ††)
EER = 9.5
COP = 2.9
PTHP .................
7,000–15,000 .........................................
>15,000 ..................................................
Non-Standard Size † ...............................
<7,000 ....................................................
7,000–15,000 .........................................
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>15,000 ..................................................
EER = 9.3
COP = 2.7
EER = 10.8 ¥ (0.213 × Cap ††)
COP = 2.9 ¥ (0.026 × Cap ††)
EER = 7.6
COP = 2.5
* For equipment rated according to the DOE test procedure (Air-Conditioning and Refrigeration Institute [ARI] Standard 310/380–2004), all energy efficiency ratio (EER) values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled equipment and evaporatively cooled equipment and at 85 °F entering water temperature for water-cooled equipment. All coefficient of performance (COP) values must be rated at 47 °F
outdoor dry-bulb temperature for air-cooled equipment.
** Standard size refers to PTAC or PTHP equipment with wall sleeve dimensions having an external wall opening greater than or equal to 16
inches high or greater than or equal to 42 inches wide, and a cross-sectional area greater than or equal to 670 square inches.
† Non-standard size refers to PTAC or PTHP equipment with existing wall sleeve dimensions having an external wall opening of less than 16
inches high or less than 42 inches wide, and a cross-sectional area less than 670 square inches.
†† Cap means cooling capacity in thousand Btu/h (kBtu/h) at 95 °F outdoor dry-bulb temperature.
DOE only presents the benefits and
burdens of adopting a standard level
higher than the efficiency levels
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specified in ASHRAE Standard 90.1–
1999. The benefits and burdens of
adopting the efficiency levels in
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ASHRAE Standard 90.1–1999 for nonstandard size PTACs and PTHPs are not
calculated in this rulemaking because
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DOE considers this the baseline
efficiency levels even though they
represent an increase in energy
efficiency when compared to the current
Federal energy conservation standards.
energy conservation standards for
PTACs and PTHPs.
B. Current Federal Standards for
Packaged Terminal Air Conditioners
and Packaged Terminal Heat Pumps
Table I.2 presents the minimum
efficiency levels in the current Federal
TABLE I.2—EXISTING FEDERAL ENERGY CONSERVATION STANDARDS FOR PTACS AND PTHPS
Equipment class
Existing Federal energy conservation
standards*
Equipment
Cooling capacity
(Btu/h)
PTAC .......................................................................
<7,000 .....................................................................
7,000–15,000 ..........................................................
>15,000 ...................................................................
<7,000 .....................................................................
PTHP .......................................................................
7,000–15,000 ..........................................................
>15,000 ...................................................................
EER = 8.88
EER = 10.0 ¥ (0.16 × Cap**)
EER = 7.6
EER = 8.88
COP = 2.7
EER = 10.0 ¥ (0.16 × Cap**)
COP = 1.3 + (0.16 × EER)
EER = 7.6
COP = 2.5
* For equipment rated according to the ARI standards, all EER values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled products and evaporatively cooled products and at 85 °F entering water temperature for water-cooled products. All COP values must be rated at
47 °F outdoor dry-bulb temperature for air-cooled products, and at 70 °F entering water temperature for water-source heat pumps.
** Cap means cooling capacity in kBtu/h at 95 °F outdoor dry-bulb temperature.
C. Benefits to Customers of Packaged
Terminal Air Conditioners and
Packaged Terminal Heat Pumps
conservation standards adopted in
today’s final rule.
Table I.3 presents the impacts on
commercial customers of the energy
TABLE I.3—IMPACTS OF NEW STANDARDS FOR A SAMPLE OF COMMERCIAL CUSTOMERS *
Total
installed
cost
Equipment class
Amended energy
conservation standard
Standard Size PTAC, 9,000 Btu/h Cooling Capacity ......
Standard Size PTAC, 12,000 Btu/h Cooling Capacity ....
Standard Size PTHP, 9,000 Btu/h Cooling Capacity ......
11.1 EER ...........................
10.2 EER ...........................
11.3 EER ...........................
3.2 COP
10.4 EER ...........................
3.0 COP
8.6 EER .............................
8.5 EER .............................
Standard Size PTHP, 12,000 Btu/h Cooling Capacity ....
Non-Standard Size PTAC, 11,000 Btu/h Cooling Capacity.
Non-Standard Size PTHP, 11,000 Btu/h Cooling Capacity.
Total installed cost
increase
Life-cycle
cost savings
Payback
period
(years)
1,229
1,469
1,362
$22
16
40
($3)
(2)
28
13.7
13.1
4.4
1,603
38
24
4.6
1,570
** N/A
** N/A
** N/A
1,692
** N/A
** N/A
** N/A
2.6 COP
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* The values in Table I.3 represent average values and all monetary values are expressed in 2007$.
** DOE did not calculate the implications on commercial customers of non-standard equipment because DOE is adopting the efficiency levels
in ASHRAE Standard 90.1–1999 (i.e., the baseline efficiency levels).
The economic impacts on commercial
consumers (i.e., the average life-cycle
cost (LCC) savings) are positive. For
example, the typical, standard size
PTAC with a cooling capacity of 9,000
Btu/h that meets the existing Federal
energy conservation standards has an
installed price of $1,207 and an annual
energy cost of $109 (cooling only). A
typical, standard size PTHP of the same
cooling capacity that meets the existing
Federal energy conservation standards
has an installed price of $1,362 and an
annual energy cost of $209. To meet the
new standard, DOE estimates that the
installed price of a typical, standard size
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PTAC with a cooling capacity of 9,000
Btu/h will be $1,229, an increase of $22.
This price increase will be offset by an
annual energy savings of about $3.
Similarly, for a typical, standard size
PTHP of the same cooling capacity to
meet the new standard, the increase in
installed price would be $40, offset by
an annual energy savings of $11.
Whereas the typical, non-standard size
PTAC that meets the ASHRAE Standard
90.1–1999 efficiency levels has an
installed price of $1,570 and an annual
energy cost of $180.
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D. Impact on Manufacturers
Using a real corporate discount rate of
five-percent, DOE estimates the net
present value (NPV) of the standard size
packaged terminal equipment industry
to be $427 million in 2007$ and the
NPV of the non-standard size packaged
terminal equipment industry to be $30
million in 2007$. DOE expects the
impact of today’s standards on the
industry net present value (INPV) of
manufacturers of standard size packaged
terminal equipment to be between a
two-percent loss and a 14 percent loss
(¥$8 million to ¥$61 million). Based
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on DOE’s interviews with the
manufacturers of PTACs and PTHPs,
DOE expects minimal plant closings or
loss of employment as a result of the
standards for both the standard size and
non-standard size industries.
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E. National Benefits
DOE estimates the amended energy
conservation standards will save
approximately 0.032 quads (quadrillion
(1015) Btu) of energy over 30 years
(2012–2042). This is equivalent to all
the electricity used annually by
approximately 500 motels.1
By 2042, DOE expects the energy
savings from the standards to eliminate
the need for approximately one new 82megawatt (MW) power plant. These
energy savings will result in cumulative
greenhouse gas emission reductions of
approximately 1.06 million tons (Mt) of
carbon dioxide (CO2), or an amount
equal to that produced by
approximately 6,700 cars every year.
Additionally, the standards will help
alleviate air pollution by resulting in
between approximately 90 and 2,130
tons (0.09 and 2.13 kilotons (kt)) of
nitrogen oxides (NOX) cumulative
emission reductions from 2012 through
2042. Finally, the standards will also
alleviate air pollution by resulting in
between approximately 0 and 0.037 tons
of mercury (Hg) cumulative emission
reductions from 2012 through 2042.
The national NPV of the standard for
standard size PTACs and PTHPs is $10
million using a seven-percent discount
rate and $54 million using a threepercent discount rate, cumulative from
2012 to 2062 in 2007$. This is the
estimated total value of future savings
minus the estimated increased
equipment costs, discounted to 2008.
The benefits and costs of today’s final
rule can also be expressed in terms of
annualized 2007$ values over the
forecast period 2012 through 2042.
Using a seven-percent discount rate for
the annualized cost analysis, the cost of
the amended energy conservation
standards established in today’s final
rule for standard size PTACs and PTHPs
is $4.7 million per year in increased
equipment and installation costs while
the annualized benefits are $5.7 million
per year in reduced equipment
operating costs. Using a three-percent
discount rate, the cost of the amended
energy conservation standards
established in today’s final rule for
standard size PTACs and PTHPs is $4.1
million per year, whereas the benefits of
1 Energy Informaton Agency. 2003 CBECS public
use sample, where specific building activity =
‘‘motel or inn’’ (PBAPLUS8=39). Anual electricity
use averages about 177,700 kWh per yer.
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today’s amended energy conservation
standards are $6.5 million per year.
F. Other Considerations
DOE noted in the April 2008 Notice
of Proposed Rulemaking (NOPR) that
PTAC and PTHP equipment
manufacturers also face a mandated
refrigerant phaseout on January 1, 2010.
73 FR 18858, 18860 (April 7, 2008). R–
22, the only refrigerant currently used
by PTACs and PTHPs, is a
hydrochlorofluorocarbon (HCFC)
refrigerant subject to the phaseout
requirement. Phaseout of this refrigerant
could have a significant impact on the
manufacturing, performance, and cost of
PTAC and PTHP equipment. DOE
discussed and estimated the impacts of
the refrigerant phaseout on PTAC and
PTHP equipment and on the
manufacturers of this equipment in the
NOPR, see generally, 73 FR 18872–74,
and today’s final rule.
G. Conclusion
DOE concludes that the benefits
(energy savings, commercial customer
LCC savings, positive national NPV, and
emissions reductions) to the Nation of
the amended standards for standard size
equipment outweigh their costs (loss of
manufacturer INPV and commercial
customer LCC increases for some users
of PTACs and PTHPs). DOE believes
that these amended standards are
technologically feasible, economically
justified, and will save additional
significant amounts of energy as
compared to the savings that would
result from adoption of the efficiency
levels for standard size PTACs and
PTHPs in ASHRAE Standard 90.1–1999.
DOE also believes that the standards for
non-standard size equipment (i.e., the
efficiency levels in ASHRAE Standard
90.1–1999) are technologically feasible,
economically justified, and will save
significant amounts of energy compared
to the current Federal energy
conservation standards. Finally, DOE
concludes that today’s standards for
PTACs and PTHPs are designed to
achieve the maximum improvements in
energy efficiency that are
technologically feasible and
economically justified. Currently,
PTACs and PTHPs that meet the new
standard levels are commercially
available utilizing R–22 refrigerant. DOE
believes that PTACs and PTHPs
utilizing R–410A equipment at the new
standard levels will be commercially
available by the effective dates of the
new standard levels.
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58775
II. Introduction
A. Authority
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. Part A–1 of Title III (42
U.S.C. 6311–6317) establishes a similar
program for ‘‘Certain Industrial
Equipment,’’ including PTACs and
PTHPs, the subjects of this rulemaking.2
DOE publishes today’s final rule
pursuant to Part A–1 of Title III, which
provides for test procedures, labeling,
and energy conservation standards for
PTACs and PTHPs and certain other
equipment, and authorizes DOE to
require information and reports from
manufacturers. The test procedure for
PTACs and PTHPs appears in title 10
Code of Federal Regulations (CFR)
section 431.96.
EPCA established Federal energy
conservation standards that generally
correspond to the levels in ASHRAE
Standard 90.1, effective October 24,
1992, for most types of covered
equipment listed in section 342(a) of
EPCA, including PTACs and PTHPs. (42
U.S.C. 6313(a)) For each type of
equipment, EPCA directs that if
ASHRAE Standard 90.1 is amended,
DOE must adopt an amended standard
at the new level in ASHRAE Standard
90.1, unless clear and convincing
evidence supports a determination that
adoption of a more stringent level as a
national standard would produce
significant additional energy savings
and be technologically feasible and
economically justified. (42 U.S.C.
6313(a)(6)(A)(ii)(II))
EPCA also provides that in deciding
whether a more stringent standard is
economically justified for equipment
such as PTACs and PTHPs, DOE must,
after receiving comments on the
proposed standard, determine whether
the benefits of such a standard exceed
its burdens by considering the following
seven factors to the greatest extent
practicable:
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
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
2 This part was originally titled Part C. However,
it was redesignated Part A–1 after Part B of Title
III of EPCA was repealed by Public Law 109–58.
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result from the imposition of the
standard;
3. The total projected amount of
energy savings likely to result directly
from the imposition of the standard;
4. Any lessening of the utility or the
performance of the 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
conservation; and
7. Other factors the Secretary of
Energy (Secretary) considers relevant.
(42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)–(ii))
EPCA also contains an ‘‘antibacksliding’’ provision, which prohibits
DOE from prescribing any amended
energy conservation standard that either
increases the maximum allowable
energy use or decreases the minimum
required energy efficiency of covered
equipment. (42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(1)) It is a fundamental principle
in EPCA’s statutory scheme that DOE
cannot amend standards downward;
that is, DOE may not weaken standards
that have been previously promulgated.
Natural Resources Defense Council v.
Abraham, 355 F.3d 179 (2d Cir. 2004).
In addition, EPCA, as amended (42
U.S.C. 6295(o)(2)(B)(iii)), 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 (and as
applicable, water) savings during the
first year that the consumer will receive
as a result of the standard,’’ as
calculated under the test procedure in
place for that standard. This approach
provides an alternative path in
establishing economic justification
under the EPCA factors. (42 U.S.C.
6295(o)(2)(B)(iii)) DOE considered this
test, but believes that the criterion it
applies (i.e., a limited payback period)
is not sufficient for determining
economic justification. Instead, DOE has
considered a full range of impacts,
including those to the consumer,
manufacturer, Nation, and environment.
Additionally, the Secretary may not
prescribe an 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 product type (or class)’’ with
performance characteristics, features,
sizes, capacities, and volumes that are
substantially the same as those generally
available in the United States at the time
of the Secretary’s finding. (42 U.S.C.
6316(a); 42 U.S.C. 6295(o)(4))
Section 325(q)(1) of EPCA directs that
DOE must specify a different standard
level than that which applies generally
to such type or class of equipment for
any group of 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
within that type or class. (42 U.S.C.
6295(q)(1)(A) and (B)) In determining
whether a performance-related feature
justifies such 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. (42
U.S.C. 6295(q)(1)) Any rule prescribing
such a standard must include an
explanation of the basis on which DOE
established such higher or lower level.
(42 U.S.C. 6295(q)(2))
Federal energy efficiency
requirements for commercial equipment
generally supersede State laws or
regulations concerning energy
conservation testing, labeling, and
standards. (42 U.S.C. 6297(a)–(c); 42
U.S.C. 6316(a) and (b)) However, DOE
can grant waivers of preemption for
particular State laws or regulations, in
accordance with the procedures and
other provisions of section 327(d) of the
Act, as amended. (42 U.S.C. 6297(d); 42
U.S.C. 6316(b)(2)(D))
B. Background
1. Current Standards
As described in greater detail in the
NOPR, 73 FR 18861–62, the current
energy conservation standards in EPCA
for PTACs and PTHPs apply to all
equipment manufactured on or after
January 1, 1994. (42 U.S.C. 6313(a)(3);
10 CFR 431.97) Table I.2 details these
standards.
2. History of Standards Rulemaking for
Packaged Terminal Equipment
On October 29, 1999, ASHRAE
adopted ASHRAE Standard 90.1–1999,
which revised the efficiency levels for
various categories of commercial
equipment covered by EPCA, including
PTACs and PTHPs. In amending the
ASHRAE Standard 90.1–1989 levels for
packaged terminal equipment, ASHRAE
used the equipment classes contained in
EPCA, which are distinguished by
equipment type (i.e., air conditioner
(PTAC) or heat pump (PTHP)) and
cooling capacity. However, ASHRAE
further divided these classes by wall
sleeve dimensions, because they affect
the energy efficiency of PTACs and
PTHPs. Table II.1 shows the efficiency
levels in ASHRAE Standard 90.1–1999
for this equipment.
TABLE II.1—ASHRAE STANDARD 90.1–1999 ENERGY EFFICIENCY LEVELS FOR PTACS AND PTHPS
Equipment class
ASHRAE standard 90.1–1999 efficiency
levels *
Category
Cooling capacity
(Btu/h)
PTAC .................
Standard Size ** .....................................
<7,000 ....................................................
7,000–15,000 .........................................
>15,000 ..................................................
EER = 11.0
EER = 12.5 ¥ (0.213 × Cap ††)
EER = 9.3
Non-Standard Size † ...............................
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Equipment
<7,000 ....................................................
7,000–15,000 .........................................
>15,000 ..................................................
EER = 9.4
EER = 10.9 ¥ (0.213 × Cap ††)
EER = 7.7
Standard Size ** .....................................
<7,000 ....................................................
EER = 10.8
COP = 3.0
EER = 12.3 ¥ (0.213 × Cap ††)
COP = 3.2 ¥ (0.026 × Cap ††)
PTHP .................
7,000–15,000 .........................................
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58777
TABLE II.1—ASHRAE STANDARD 90.1–1999 ENERGY EFFICIENCY LEVELS FOR PTACS AND PTHPS—Continued
Equipment class
Equipment
ASHRAE standard 90.1–1999 efficiency
levels *
Cooling capacity
(Btu/h)
Category
>15,000 ..................................................
Non-Standard Size † ...............................
EER = 9.1
COP = 2.8
<7,000 ....................................................
EER = 9.3
COP = 2.7
EER = 10.8 ¥ (0.213 × Cap ††)
COP = 2.9 ¥ (0.026 × Cap ††)
EER = 7.6
COP = 2.5
7,000–15,000 .........................................
>15,000 ..................................................
* For equipment rated according to ARI standards, all EER values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled products
and evaporatively cooled products and at 85 °F entering water temperature for water-cooled products. All COP values must be rated at 47 °F
outdoor dry-bulb temperature for air-cooled products.
** Standard size refers to PTAC or PTHP equipment with wall sleeve dimensions greater than or equal to 16 inches high, or greater than or
equal to 42 inches wide.
† Non-standard size refers to PTAC or PTHP equipment with wall sleeve dimensions less than 16 inches high and less than 42 inches wide.
ASHRAE Standard 90.1–1999 also includes a factory labeling requirement for non-standard size PTAC and PTHP equipment as follows: ‘‘MANUFACTURED FOR REPLACEMENT APPLICATIONS ONLY; NOT TO BE INSTALLED IN NEW CONSTRUCTION PROJECTS.’’
†† Cap means cooling capacity in kBtu/h at 95 °F outdoor dry-bulb temperature.
After publication of ASHRAE
Standard 90.1–1999, DOE analyzed
many of its equipment categories to
evaluate possible consideration of more
stringent efficiency levels than those
specified in the Standard. DOE
summarized this analysis in a report,
Screening Analysis for EPACT-Covered
Commercial HVAC [Heating, Ventilating
and Air-Conditioning] and WaterHeating Equipment (commonly referred
to as the 2000 Screening Analysis).3 On
January 12, 2001, DOE published a final
rule adopting the efficiency levels in
ASHRAE Standard 90.1–1999 for many
types of commercial HVAC and water
heating equipment, excluding packaged
terminal equipment and certain other
types of equipment. 66 FR 3336.
Regarding PTACs and PTHPs, the
preamble to the final rule stated that the
2000 Screening Analysis indicated at
least a reasonable possibility of finding
‘‘clear and convincing evidence’’ that
more stringent standards ‘‘would be
technologically feasible and
economically justified and would result
in significant additional conservation of
energy.’’ 66 FR 3349–50. Under EPCA,
these are the criteria for DOE’s adoption
of standards more stringent than the
efficiency levels in ASHRAE Standard
90.1. (42 U.S.C. 6313(a)(6)(A)(ii)(II)).
More recently, DOE announced the
availability of a technical support
document (TSD) it developed to reassess
whether to adopt as national standards
certain efficiency levels that were in
amendments to ASHRAE Standard 90.1,
including the levels in the 1999
amendments for PTACs and PTHPs. 71
FR 12634 (March 13, 2006) (Notice of
Availability). According to DOE,
although the revised analysis in the TSD
reduced the potential energy savings
that might result from standards more
stringent than the efficiency levels
specified in ASHRAE Standard 90.1–
1999 for PTACs and PTHPs, DOE was
inclined to pursue standards that are
more stringent because there was a
possibility that clear and convincing
evidence exists that such standards are
warranted. Id. at 12638–39. DOE stated
that it would explore more stringent
efficiency levels than those in ASHRAE
Standard 90.1–1999 for PTACs and
PTHPs through a separate rulemaking.
Id. at 12639.
DOE proposed energy conservation
standards for PTACs and PTHPs in a
NOPR published on April 7, 2008. 73
FR 18858. In conjunction with the
NOPR, DOE also published on its Web
site the complete TSD for the proposed
rule, which incorporated the final
analyses that DOE conducted and
technical support documentation of
each analysis. The NOPR TSD included
the LCC spreadsheets, the national
impact analysis spreadsheets, and the
manufacturer impact analysis (MIA)
spreadsheet—all of which are available
on DOE’s PTAC and PTHP webpage.
The proposed standards were as
follows:
TABLE II.2—NOPR PROPOSED ENERGY CONSERVATION STANDARDS FOR PTACS AND PTHPS
Equipment class
Proposed energy conservation standards *
Category
Cooling capacity
(Btu/h)
PTAC ................
Standard Size ** ............................
<7,000 ...........................................
7,000–15,000 ................................
>15,000 .........................................
EER = 11.4
EER = 13.0¥(0.233 × Cap ††)
EER = 9.5
Non-Standard Size ........................
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Equipment
<7,000 ...........................................
7,000–15,000 ................................
>15,000 .........................................
EER = 10.2
EER = 11.7¥(0.213 × Cap ††)
EER = 8.5
3 U.S. Department of Energy, Office of Energy
Efficiency and Renewable Energy. ‘‘Energy
Conservation Program for Consumer Products:
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Screening Analysis for EPACT-Covered Commercial
HVAC and Water-Heating Equipment Screening
Analysis.’’ April 2000. https://www.eere.energy.gov/
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TABLE II.2—NOPR PROPOSED ENERGY CONSERVATION STANDARDS FOR PTACS AND PTHPS—Continued
Equipment class
Proposed energy conservation standards *
Equipment
Category
Cooling capacity
(Btu/h)
PTHP ................
Standard Size ** ............................
<7,000 ...........................................
7,000–15,000 ................................
>15,000 .........................................
Non-Standard Size ........................
<7,000 ...........................................
7,000–15,000 ................................
>15,000 .........................................
EER = 11.8
COP = 3.3
EER = 13.4¥(0.233 × Cap ††)
COP = 3.7¥(0.053 × Cap ††)
EER = 9.9
COP = 2.9
EER = 10.8
COP = 3.0
EER = 12.3¥(0.213 × Cap ††)
COP = 3.1¥(0.026 × Cap ††)
EER = 9.1
COP = 2.8
* For equipment rated according to the DOE test procedure (ARI Standard 310/380–2004), all EER values must be rated at 95 °F outdoor drybulb temperature for air-cooled equipment and evaporatively cooled equipment and at 85 °F entering water temperature for water-cooled equipment. All COP values must be rated at 47 °F outdoor dry-bulb temperature for air-cooled equipment, and at 70 °F entering water temperature for
water-source heat pumps.
** Standard size refers to PTAC or PTHP equipment with wall sleeve dimensions greater than or equal to 16 inches high, or greater than or
equal to 42 inches wide.
† Non-standard size refers to PTAC or PTHP equipment with wall sleeve dimensions less than 16 inches high and less than 42 inches wide.
†† Cap means cooling capacity in kBtu/h at 95 °F outdoor dry-bulb temperature.
The NOPR also included additional
background information on the history
of this rulemaking. 73 FR 18862–63.
DOE held a public meeting in
Washington, DC, on May 1, 2008, to
accept oral comments on and solicit
information relevant to the proposed
rule.
III. General Discussion
A. Test Procedures
Section 343(a) of EPCA, as amended,
authorizes the Secretary to amend the
test procedures for PTACs and PTHPs to
the latest version generally accepted by
industry or the rating procedures
developed or recognized by the ARI, or
ASHRAE as referenced in ASHRAE
Standard 90.1, unless the Secretary
determines by clear and convincing
evidence that the latest version of the
industry test procedure does not meet
specific requirements. (See 42 U.S.C.
6314(a)(4) As the NOPR explains, DOE
has determined that its existing test
procedure for PTACs and PTHPs does
not need modification. 73 FR 18863.
Accordingly, DOE has not adopted a
revised test procedure for this
equipment.
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B. Technological Feasibility
1. General
To adopt standards for PTACs and
PTHPs that are more stringent than the
efficiency levels in ASHRAE Standard
90.1 as amended, DOE must determine,
supported by clear and convincing
evidence, that such standards are
technologically feasible. (42 U.S.C.
6313(a)(6)(A)(ii)(II)) DOE considers a
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design option to be technologically
feasible if it is in use by the respective
industry or if research has progressed to
the development of a working
prototype. DOE defines technological
feasibility as follows: ‘‘Technologies
incorporated in commercially available
products or in working prototypes will
be considered technologically feasible.’’
10 CFR part 430, subpart C, appendix A,
section 4(a)(4)(i).
This final rule considers the same
design options as those evaluated in the
NOPR. (See the final rule TSD
accompanying this notice, Chapter 4.)
Based on equipment literature, the
teardown analysis, manufacturer
interviews, and the equipment
performance degradations provided by
AHRI during the NOPR phase of the
rulemaking, DOE considered the
following design options in the final
rule analysis: (1) Higher efficiency
compressors; (2) increasing the heat
exchanger area; and (3) recircuiting the
heat exchanger coils. Since these three
design options are commercially
available, have been used in PTAC and
PTHP equipment, and are the most
common ways by which manufacturers
improve the energy efficiency of their
PTACs and PTHPs, DOE has determined
that clear and convincing evidence
supports the conclusion that all of the
efficiency levels evaluated in this notice
are technologically feasible. DOE further
discusses the technical feasibility of
PTAC and PTHP equipment utilizing R–
410A in section IV.C. of today’s notice.
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2. Maximum Technologically Feasible
Levels
In order to evaluate whether energy
conservation standards for PTACs and
PTHPs are economically justified, DOE
determines the maximum improvement
in energy efficiency or maximum
reduction in energy use that is
technologically feasible. (42 U.S.C.
6316(a); 42 U.S.C. 6295(p)(2)) DOE
determined the maximum
technologically feasible level (‘‘maxtech’’) efficiency levels in its
engineering analysis for the NOPR. 73
FR 18863–64. (See NOPR TSD Chapter
5.) In the NOPR, DOE based its
identification of the max-tech efficiency
levels on standard size and nonstandard size PTAC and PTHP
equipment utilizing R–22 that is
currently available on the market. For
the final rule, DOE revised the max-tech
efficiency levels for standard size and
non-standard size PTACs and PTHPs
based on submitted comments, which
are discussed in section IV.C of today’s
notice. The max-tech efficiency levels
considered for today’s final rule are
based on the efficiency levels identified
in the NOPR and factor performance
degradations stemming from the switch
to R–410A refrigerant.4 Table III.1 lists
the max-tech efficiency levels that DOE
identified for this rulemaking for the
4 DOE expects the overall system efficiency of
R–410A PTAC and PTHP equipment will be lower
than if that equipment used R–22, which DOE
estimated using an overall system performance
degradation. This estimate is based on data
submitted by manufacturers and AHRI pointing to
a decline in performance when using R–410A
refrigerant in place of R–22 refrigerant.
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estimated system performance of
equipment utilizing R–410A. DOE
58779
discusses these levels further in section
IV.C.
TABLE III.1—R–410A MAX-TECH EFFICIENCY LEVELS (7,000–15,000 BTU/H EQUIPMENT CLASSES) *
Equipment type
Equipment class
Cooling capacity
(Btu/h)
PTAC ................
Standard Size † .............................
9,000 .............................................
12,000 ...........................................
11.5 EER
10.8 EER
Non-Standard Size †† ....................
11,000 ...........................................
10.0 EER
Standard Size † .............................
9,000 .............................................
12,000 ...........................................
11.5 EER
3.3 COP
10.8 EER
3.1 COP
11,000 ...........................................
10.0 EER
2.9 COP
PTHP ................
Non-Standard Size †† ....................
R–410A ‘‘Max-Tech’’ efficiency level **
* As discussed in the NOPR, DOE is presenting the results for two cooling capacities of standard size PTACs and PTHPs, 9,000 and 12,000
Btu/h, which fall within the equipment classes of PTACs and PTHPs with cooling capacities of 7,000–15,000 Btu/h. 73 FR 18870–18871.
** For equipment rated according to the DOE test procedure, all EER values would be rated at 95 °F outdoor dry-bulb temperature for aircooled products and evaporatively cooled products and at 85 °F entering water temperature for water-cooled products. All COP values must be
rated at 47 °F outdoor dry-bulb temperature for air-cooled products and at 70 °F entering water temperature for water-source heat pumps.
† Standard size refers to PTAC or PTHP equipment with wall sleeve dimensions having an external wall opening of greater than or equal to 16
inches high or greater than or equal to 42 inches wide, and having a cross-sectional area greater than or equal to 670 square inches.
†† Non-standard size refers to PTAC or PTHP equipment with existing wall sleeve dimensions having an external wall opening of less than 16
inches high or less than 42 inches wide, and having a cross-sectional area less than 670 square inches.
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C. Energy Savings
DOE forecasted energy savings in its
national energy savings (NES) analysis
using an NES spreadsheet tool, which
the NOPR discussed in greater detail.
See generally, 73 FR 18864, 18876,
18880–83, 18899.
Among the criteria that govern DOE’s
adoption of more stringent standards for
PTACs and PTHPs than the amended
levels in ASHRAE Standard 90.1, clear
and convincing evidence must support
a determination that the standards
would result in ‘‘significant’’ energy
savings. (42 U.S.C. 6313(a)(6)(A)(ii)(II))
Although EPCA does not define
‘‘significant,’’ the U.S. Court of Appeals
for the District of Columbia indicated
that Congress intended ‘‘significant’’
energy savings to mean savings that
were not ‘‘genuinely trivial’’ in Section
325 of the Act. Natural Resources
Defense Council v. Herrington, 768 F.2d
1355, 1373 (D.C. Cir. 1985). DOE’s
estimates of the energy savings for each
of the TSLs considered for today’s rule
provide clear and convincing evidence
that the additional energy savings each
would achieve by exceeding the
corresponding efficiency levels in
ASHRAE Standard 90.1–1999 are
nontrivial. Therefore, DOE considers
these savings to be ‘‘significant’’ as
required by 42 U.S.C.
6313(a)(6)(A)(ii)(II).
D. Economic Justification
As noted earlier, EPCA provides
seven factors to be evaluated in
determining whether an energy
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conservation standard for PTACs and
PTHPs is economically justified. (42
U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)–(ii)) The following
paragraphs discuss how DOE has
addressed each of those seven factors in
this rulemaking.
1. Economic Impact on Commercial
Consumers and Manufacturers
DOE considered the economic impact
of the standards on commercial
consumers and manufacturers. For
customers, DOE measures the economic
impact as the change in installed cost
and life-cycle operating costs, i.e., the
LCC. (See section V.C.1 and Chapter 8
of the TSD.) DOE investigates the
impacts of amended energy
conservation standards of PTACs and
PTHPs on manufacturers through the
manufacturer impact analysis (MIA).
(See section V.C.2 and Chapter 13 of the
TSD.) This factor is discussed in detail
in the NOPR. See generally 73 FR
18860–61, 18864–66, 18869, 18883–87,
18893–99, 18906–07, 18910–12.
2. Life-Cycle Costs
DOE considered life-cycle costs of
PTACs and PTHPs. This factor is
discussed in detail in the NOPR. See
generally 73 FR 18860–61, 18865,
18876–80, 18883, 18888, 18891–93.
DOE calculated the sum of the purchase
price and the operating expense—
discounted over the lifetime of the
equipment—to estimate the range in
LCC benefits that commercial customers
would expect to achieve due to the
standards.
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3. Energy Savings
Although significant additional
conservation of energy is a separate
statutory requirement for imposing a
more stringent energy conservation
standard than the level in the most
current ASHRAE Standard 90.1, EPCA
also requires that DOE consider the total
projected energy savings that will likely
result directly from the standard in
determining whether a standard is
economically justified. (42 U.S.C.
6316(a); 42 U.S.C. 6295(o)(2)(B)(i)(III))
DOE used the NES spreadsheet results
in its consideration of total projected
savings. 73 FR 18860–61, 18864, 18876,
18880–83, 18899. DOE presents the
energy savings at each TSL for standard
size and non-standard size PTACs and
PTHPs in section V.B of today’s notice.
4. Lessening of Utility or Performance of
Equipment
In selecting today’s standard levels,
DOE sought to avoid new standards for
PTACs and PTHPs that would lessen the
utility or performance of that
equipment. (42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)(IV)) 73 FR 18865,
18866–68, 18900. The design options
considered in the engineering analysis
of this rulemaking, which include
higher efficiency compressors,
increasing the heat exchanger area, and
recircuiting the heat exchanger coils, do
not involve changes in equipment
design or unusual installation
requirements that could reduce the
utility or performance of PTACs and
PTHPs. In the NOPR, DOE considered
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industry concerns that one-third of the
non-standard size market subject to the
more stringent standards under
ASHRAE Standard 90.1–1999 definition
would not be able to meet the efficiency
levels specified by ASHRAE Standard
90.1–1999 for standard size equipment
due to the physical size constraints of
the wall sleeve if this equipment class
delineation was adopted. In today’s
final rule, DOE is adopting the
equipment class delineations specified
in Addendum t to ASHRAE Standard
90.1–2007. This action should mitigate
manufacturers’ concerns regarding the
misclassification of non-standard
equipment classes. DOE further
discusses the equipment classes it is
adopting today and the comments
received from interested parties
regarding equipment classes in section
IV.A of today’s rulemaking.
5. Impact of Any Lessening of
Competition
DOE considers any lessening of
competition likely to result from
standards. As discussed in the NOPR
(73 FR 18865, 18900), DOE requested
that the Attorney General transmit to the
Secretary a written determination of the
impact of any lessening of competition
likely to result from the proposed
standards, together with an analysis of
the nature and extent of such impact.
(42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)(V) and (B)(ii))
To assist the Attorney General in
making such a determination, DOE
provided DOJ with copies of the
proposed rule and the TSD for review.
(DOJ, No. 21 at p. 1–2) 5 The Attorney
General’s response is discussed in
section IV.K.1, and is reprinted at the
end of today’s rulemaking.
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6. Need of the Nation To Conserve
Energy
In considering standards for PTACs
and PTHPs, the Secretary must consider
the need of the Nation to conserve
energy. (42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)(VI)) The Secretary
recognizes that energy conservation
benefits the Nation in several important
ways. The non-monetary benefits of the
standards will likely be reflected in
improvements to the security and
reliability of the Nation’s energy system.
5 ‘‘DOJ, No. 21 at pp 1–2’’ refers to (1) a statement
that was submitted by the Department of Justice and
is recorded in the Resource Room of the Building
Technologies Program in the docket under ‘‘Energy
Conservation Program for Commercial and
Industrial Equipment: Packaged Terminal Air
Conditioner and Packaged Terminal Heat Pump
Energy Conservation Standards,’’ Docket Number
EERE–2007–BT–STD–0012, as comment number
21; and (2) a passage that appears on pages 1 and
2 of that statement.
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Today’s standards also will likely result
in environmental benefits. As discussed
in the proposed rule, DOE has
considered these factors in adopting
today’s standards. See generally, 73 FR
at 18860, 18865, 18888, 18900–02,
18912.
7. Other Factors
In determining whether a standard is
economically justified, EPCA directs the
Secretary of Energy to consider any
other factors that the Secretary deems to
be relevant. (42 U.S.C. 6316(a); 42
U.S.C. 6295(o)(2)(B)(i)(VII)) In adopting
today’s standard, DOE considered (1)
the impacts of setting different amended
standards for PTACs and PTHPs, (2) the
potential that amended standards could
cause equipment switching (i.e.,
purchase of PTACs instead of PTHPs)
and the effects of any such switching,
(3) the uncertainties associated with the
impending phaseout in 2010 of R–22
refrigerant, and (4) the impact of
amended standards on the manufacture
of and market for non-standard size
packaged terminal equipment (e.g.,
impacts on small businesses). See
generally, 73 FR at 18860, 18865–66,
18872–74, 18882, 18884–87, 18893–98,
18902, 18911–12.
IV. Analysis Methodology and
Discussion of Comments on Analysis
Methodology
DOE used several analytical tools that
it developed previously and adapted for
use in this rulemaking. The first tool is
a spreadsheet that calculates LCC and
payback period (PBP). The second tool
calculates national energy savings and
national NPV. DOE also used the
Government Regulatory Impact Model
(GRIM), among other methods, in its
MIA. Finally, DOE developed an
approach using the National Energy
Modeling System (NEMS) to estimate
impacts of PTAC and PTHP energy
efficiency standards on electric utilities
and the environment. The NOPR
discusses each analytical tool in detail.
73 FR at 18866–89.
As a basis for this final rule, DOE has
continued to use the spreadsheets and
approaches described above and in the
NOPR. DOE used the same general
methodology as applied in the NOPR,
but revised some of the assumptions
and inputs for the final rule in response
to comments from interested parties.
The following paragraphs discuss these
revisions.
A. Market and Technology Assessment
When beginning an energy
conservation standards rulemaking,
DOE develops information that provides
an overall picture of the market for the
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equipment concerned, including the
purpose of the equipment, the industry
structure, and market characteristics.
This activity includes both quantitative
and qualitative assessments based
primarily on publicly available
information. DOE presented various
subjects in the market and technology
assessment for this rulemaking. (See the
NOPR and Chapter 3 of the NOPR TSD.)
These include equipment classes,
manufacturers, quantities and types of
equipment sold and offered for sale,
retail market trends, and regulatory and
nonregulatory programs. 73 FR 18866–
69 and Chapter 3 of the NOPR TSD. In
response to publication of the NOPR,
DOE received comments from interested
parties about the establishment of
equipment classes for the rulemaking.
1. Equipment Classes—Generally
When evaluating and establishing
energy conservation standards, DOE
generally divides covered equipment
into equipment classes by the type of
energy used, capacity, or other
performance-related features that affect
efficiency. Different energy conservation
standards may apply to different
equipment classes. (42 U.S.C. 6316(a);
42 U.S.C. 6295(q))
PTACs and PTHPs can be divided
into various equipment classes
categorized by physical characteristics
that affect equipment efficiency. Key
characteristics that affect the energy
efficiency of the PTAC or PTHP are
whether the equipment has reverse
cycle heating (i.e., air conditioner or
heat pump), the cooling capacity, and
the physical dimensions of the unit.
In the NOPR, DOE presented two
alternative methods for defining PTAC
and PTHP equipment classes. 73 FR
18866–18868. DOE explained the two
alternative methods of defining the
PTAC and PTHP equipment classes
consistent with the delineations
provided in ASHRAE Standard 90.1–
1999 or Addendum t to ASHRAE
Standard 90.1–2007 in the NOPR. Id. at
18867.
ASHRAE Standard 90.1–1999 refers to
wall sleeve dimensions in two
categories: ‘‘New Construction’’ and
‘‘Replacement.’’ Although ASHRAE
Standard 90.1–1999 does not describe
‘‘New Construction,’’ Table 6.21D,
footnote b of ASHRAE Standard 90.1–
1999 states that ‘‘replacement’’
efficiencies apply only to units that are:
(1) ‘‘Factory labeled as follows:
Manufactured for Replacement
Applications Only; Not to be Installed
in New Construction Projects’’; and (2)
manufactured ‘‘with existing wall
sleeves less than 16 inches high and less
than 42 inches wide.’’ Based on this
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2. Comments
In the NOPR, DOE stated that
ASHRAE must adopt AHRI’s 6
continuous maintenance proposal
before DOE can officially use this
definition as the basis for DOE’s
standard because AHRI’s proposed
definitions would effectively reclassify
some equipment under ASHRAE 90.1–
1999’s delineations as non-standard size
equipment. (42 U.S.C. 6313(a)(6)(A)(ii))
When the NOPR was published, AHRI’s
continuous maintenance proposal on
PTACs and PTHPs had been approved
by ASHRAE as Addendum t to ASHRAE
Standard 90.1–2007. At the time of the
NOPR, that Addendum was the subject
of public review by ASHRAE. DOE
stated in the NOPR that if ASHRAE
were to adopt the Addendum before
September 2008, which is the deadline
by which DOE must issue a final rule for
this rulemaking, DOE proposed to
incorporate the modified definition
specified by that version of the ASHRAE
standard in its final rule. In the NOPR,
DOE sought comment from interested
parties on its proposal to adopt
Addendum t to ASHRAE Standard
90.1–2007. 73 FR 18867.
AHRI commented that all standard
and non-standard manufacturers who
are AHRI members support adoption of
Addendum t. AHRI had not received
comments challenging the content in
Addendum t during ASHRAE’s formal
comment period, and ASHRAE was
planning to adopt the Addendum
during the ASHRAE annual meeting in
June 2008. AHRI added that
manufacturers believe that the
definitions in Addendum t are needed
to deter against the reclassification of
large numbers of non-standard size
PTACs and PTHPs as standard
equipment, which will not be able to
meet the proposed standards. (Public
Meeting Transcript, No. 12 at p. 31–32,
AHRI, No. 23 at pp. 6–7) 7
ECR, McQuay, Carrier, and Ice Air
also commented that DOE should use
the delineations within Addendum t to
classify non-standard equipment.
(Public Meeting Transcript (ECR and
McQuay), No. 12 at p. 31; ECR, No. 15
at p. 4; Carrier, No. 16 at p. 1; Ice Air,
No. 25 at p. 5) ECR also noted that if
DOE used the delineations in ASHRAE
Standard 90.1–1999 to define the
equipment classes for PTACs and
PTHPs, approximately 50 percent of
their equipment would be eliminated
from the market as a result of being
reclassified into the standard size
category. (ECR, No. 15 at p. 4)
ECR commented that non-standard
equipment is burdened by space
constraints that are more stringent than
the constraints for standard size PTACs
and PTHPs. ECR added that the
delineations within ASHRAE Standard
90.1–1999, coupled with the proposed
standards (TSL 4), would force
manufacturers to include more heat
exchanger surface area within the
limited volumes of physical chassis of
the equipment, to use compressors
incorporating inverter technology, and
to use variable speed motors, which
would result in equipment switching.
(ECR, No. 15 at p. 2)
AHRI, ECR, McQuay, Ice Air, and
Cold Point also commented that nonstandard size PTACs and PTHPs meet a
specific demand that exists in the
market, particularly for older buildings.
These commenters stated that if DOE
adopted the delineations in ASHRAE
Standard 90.1–1999, which could
further eliminate non-standard size
PTACs and PTHPs from the market, this
would decrease competition and limit
customer choices. (Public Meeting
Transcript, No. 12 at pp. 20 (ECR), 22
(AHRI), 38 (McQuay); AHRI, No. 23 at
p. 7; ECR, No. 15 at p. 4; Ice Air, No.
25 at p. 4; Cold Point, No. 18 at p. 2)
DOE also received comments about
the potential for creating a loophole by
adopting Addendum t in the final rule.
In this regard, these commenters
6 The Air-Conditioning and Refrigeration Institute
(ARI) and the Gas Appliance Manufacturers
Association (GAMA) announced on December 17,
2007, that their members voted to approve the
merger of the two trade associations to represent the
interests of cooling, heating, and commercial
refrigeration equipment manufacturers. The merged
association became AHRI on Jan. 1, 2008.
7 A notation in the form ‘‘ECR, Public Meeting
Transcript, No. 12 at pp. 30, 37, 182’’ identifies (1)
an oral comment that DOE received during the May
30, 2008, NOPR public meeting by ECR, which was
recorded in the public meeting transcript in the
docket for this rulemaking as comment number 12;
and (2) a passage that appears on page 30 of that
transcript.
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provision, DOE understands that the
‘‘New Construction’’ category under
ASHRAE Standard 90.1–1999 is
residual, and covers all other PTAC and
PTHPs. Hence, this category consists of
equipment with wall sleeve dimensions
greater than or equal to 16 inches high
and greater than or equal to 42 inches
wide, or lacking the requisite label.
Addendum t to ASHRAE Standard
90.1–2007 includes a new definition for
non-standard size PTACs and PTHPs in
place of the ‘‘replacement’’ delineation
in ASHRAE Standard 90.1–1999. The
new definition reads as follows:
‘‘equipment with existing sleeves
having an external wall opening of less
than 16 in. high or less than 42 in. wide,
and having a cross-sectional area less
than 670 in 2.’’
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58781
supported DOE’s adoption of an
alternative definition for non-standard
size PTACs and PTHPs.
Specifically, General Electric (GE) and
the American Council for an Energy
Efficient Economy (ACEEE)
recommended that DOE modify the nonstandard definitions and equipment
classes to have the wall sleeve
dimension requirements set
significantly below the proposed
dimensions, consistent with the nonstandard size equipment currently on
the market. (Public Meeting Transcript,
No. 12 at pp. 16 (GE), 33–34 (GE), 36–
37 (ACEEE), 208 (ACEEE); GE, No. 8 at
p. 2; GE, No. 20 at pp. 2–3) GE asked
DOE to make the difference in the wall
sleeve dimensions of standard size and
non-standard size PTACs and PTHPs
large enough to prevent non-standard
PTACs/PTHPs from being installed in
standard size PTAC and PTHP
openings. GE used the example of a
PTAC (15.75 × 41.75 inches) that GE
believes could easily fit inside a
standard size PTAC wall sleeve, yet this
unit would be classified as non-standard
size equipment subject to less stringent
energy conservation standards. (Public
Meeting Transcript, No. 12 at pp. 16,
33–34; GE, No. 8 at p. 2)
GE stated that the wording in
Addendum t might encourage the
design of new PTAC and PTHP
equipment that may circumvent the
intent of DOE’s regulations. (Public
Meeting Transcript, No. 12 at pp. 16,
33–34; GE, No. 8 at p. 2) As an
alternative, GE suggested DOE use the
wall sleeve dimensions of the largest
non-standard size PTAC and PTHP
equipment currently on the market to
define non-standard size PTACs and
PTHPs. (Public Meeting Transcript, No.
12 at p. 33)
ECR, McQuay, and AHRI responded
to concerns about the potential for a
loophole for less efficient standard size
equipment to enter the market if DOE
adopts the delineations in Addendum t.
(ECR, No. 15 at pp. 1, 4; Public Meeting
Transcript, No. 12 at pp. 20 (ECR), 22
(AHRI), 31–32 (AHRI), 38 (McQuay))
AHRI stated that the same potential
loophole exists in the delineations
within ASHRAE Standard 90.1–1999 for
standard size and non-standard size
PTACs and PTHPs. AHRI commented
that if manufacturers want to introduce
less efficient standard size equipment
with wall sleeve dimensions just shy of
the standard size limitations,
manufacturers would have introduced
this type of equipment already because
this loophole has been in existence
since 1999. However, AHRI pointed out
that none of the manufacturers in the
PTAC and PTHP industry have taken
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advantage of this potential loophole.
AHRI also noted that Addendum t
requires non-standard size equipment to
be labeled to prevent misapplications of
less efficient non-standard equipment
entering into newly constructed
projects. (AHRI, No. 23 at pp. 6–7)
ECR also commented that it does not
believe that non-standard size
equipment will be used in newly
constructed buildings. ECR stated that
commercial customers would not
purchase non-standard equipment
because it is rated at lower efficiencies;
rather, customers make purchases based
on the characteristics and needs of the
installation (i.e., wall sleeve
dimensions). Placing non-standard size
equipment in newly constructed
buildings does not make economic
sense. (ECR, No. 15 at pp. 1, 4; Public
Meeting Transcript, No. 12 at p. 20)
McQuay pointed out that non-standard
equipment is needed to meet a specific
demand that exists in the market,
particularly for older buildings, and that
phasing out the market would decrease
competition and limit customer choices.
(Public Meeting Transcript, No. 12 at p.
38) If DOE were to adopt the
delineations within ASHRAE Standard
90.1–1999, ECR believes building
owners and commercial customers
would keep their older, much less
efficient units in place longer because
replacements could become unavailable.
(ECR, No. 15 at p. 1)
On June 22, 2008, ASHRAE Standard
90.1’s committee voted to officially
approve the publication of Addendum t
to ASHRAE Standard 90.1–2007 for
PTACs and PTHPs.8 This action
finalizes Addendum t, which means
that DOE can officially use this
delineation as the basis for amended
energy conservation standards. (42
U.S.C. 6313(a)(6)(A)(ii))
DOE divides equipment classes by the
type of energy used or by capacity or
other performance-related features that
affect efficiency. Different energy
conservation standards may apply to
different equipment classes. (42 U.S.C.
6295(q)) When installed, PTACs and
PTHPs are fitted into a wall sleeve.
There is a wide variety of wall sleeve
sizes found in different buildings. Wall
sleeve sizes are market driven (i.e., the
applications or facilities where the
PTACs or PTHPs are installed is what
8 To obtain a copy of Addendum t to ASHRAE
Standard 90.1–2007, contact the ASHRAE
publications department at: orders@ashrae.org or
1–(800) 527–4723.
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determines the ‘‘market standard’’ wall
sleeve dimension) and this factor
requires manufacturers to offer various
PTACs and PTHPs that can fit into
various wall sleeve dimensions. For
new units, the industry has
standardized the wall sleeve dimension
for PTACs and PTHPs in buildings over
the past 20 years to be 16 inches high
by 42 inches wide. Therefore, units that
have a wall sleeve dimension of 16
inches high by 42 inches wide are
considered ‘‘standard size’’ equipment
and all other units are considered ‘‘nonstandard size’’ equipment. In contrast,
the industry does not have a common
wall sleeve dimension that is typical for
all older existing facilities. These
facilities, such as high-rise buildings
found in large cities, typically use nonstandard size equipment. In these
installations, altering the existing wall
sleeve opening to accommodate the
more efficient, standard size equipment
could include extensive structural
changes to the building, which could be
very costly, and is, therefore, rarely
done.
DOE believes that wall sleeve sizes
are performance-related features that
affect PTAC and PTHP efficiency.
Manufacturers typically use various
heat exchanger sizes in different wall
sleeve size equipment, and the size of
the heat exchanger directly affects the
energy efficiency of the equipment. By
examining the market data, DOE found
that non-standard size PTACs and
PTHPs typically are less efficient than
standard size PTACs and PTHPs.
Consequently, DOE is adopting the
delineations in Addendum t to ASHRAE
Standard 90.1–2007 to differentiate
between standard size and non-standard
size equipment.
DOE believes the delineations within
Addendum t will help to mitigate the
impacts on manufacturers of nonstandard size equipment, and will not
cause any equipment unavailability
issues for commercial customers. DOE
was concerned that, absent nonstandard equipment, commercial
customers could be forced to invest in
costly building modifications to convert
non-standard sleeve openings to
standard size dimensions. Alternatively,
customers may choose to use less
efficient through-the-wall air
conditioners or maintain their older,
less efficient equipment longer in the
absence of non-standard PTACs and
PTHPs.
Although DOE acknowledges GE’s
and ACEEE’s concern about the
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potential loophole in the definition,
DOE believes that the effects of this
loophole will be reduced due to the
labeling requirements specified in
Addendum t. DOE is not adopting the
labeling requirement set forth in
Addendum t, but believes that nonstandard manufacturers will still be
required to use this labeling through
some of their State building code
regulations, which require the use of
such labels on PTAC and PTHP
equipment. DOE believes ASHRAE’s
labeling requirement will deter less
efficient equipment from entering into
newly constructed buildings.
Additionally, DOE agrees with AHRI’s
assertion that if manufacturers wanted
to introduce less standard size
equipment with wall sleeve dimensions
just shy of the standard size limitations
they could have done this in today’s
market. DOE believes the market forces
surrounding the standardized sleeve
size have deterred standard size
manufacturers from producing this type
of equipment because of the unique
non-standard size industry and the cost
implications of producing customized
equipment. Further, DOE believes these
market forces will continue to deter
standard size manufacturers from taking
advantage of this potential loophole
after the adoption of the delineations in
Addendum t to ASHRAE Standard
90.1–2007.
In today’s final rule, DOE incorporates
the following definitions of standard
size and non-standard size PTACs and
PTHPs as presented in Addendum t to
ASHRAE Standard 90.1-2007:
• Standard size refers to a PTAC or a
PTHP with wall sleeve dimensions
having an external wall opening of
greater than or equal to 16 inches high
or greater than or equal to 42 inches
wide, and having a cross-sectional area
greater than or equal to 670 square
inches.
• Non-standard size refers to a PTAC
or a PTHP with existing wall sleeve
dimensions having an external wall
opening of less than 16 inches high or
less than 42 inches wide, and having a
cross-sectional area less than 670 square
inches.
DOE added these two definitions of
standard size and non-standard size to
be codified at 10 CFR 431.2. Consistent
with the definitions, DOE has defined
the equipment classes for today’s final
rule for PTACs and PTHPs (as shown in
Table IV.1).
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58783
TABLE IV.1—EQUIPMENT CLASSES FOR PTACS AND PTHPS IF ASHRAE ADOPTS ADDENDUM TO ASHRAE STANDARD
90.1–2007
Equipment class
Cooling capacity
(Btu/h)
Equipment
Category
PTAC ....................................................................................
Standard Size * ....................................................................
<7,000
7,000–15,000
>15,000
Non-Standard Size ** ..........................................................
<7,000
7,000–15,000
>15,000
Standard Size * ....................................................................
<7,000
7,000–15,000
>15,000
Non-Standard Size ** ..........................................................
<7,000
7,000–15,000
>15,000
PTHP ....................................................................................
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* Standard size refers to PTAC or PTHP equipment with wall sleevedimensions having an external wall opening of greater than or equal to 16
inches high or greater than or equal to 42 inches wide, and having a cross-sectional area greater than or equal to 670 square inches.
** Non-standard size refers to PTAC or PTHP equipment with existing wall sleeve dimensions having an external wall opening of less than 16
inches high or less than 42 inches wide, and having a cross-sectional area less than 670 square inches.
B. Screening Analysis
The purpose of the screening analysis
is to evaluate the technologies that
improve equipment efficiency, to
determine which technologies to
consider further, and which to screen
out. In developing the screening
analysis for the NOPR, DOE consulted
with a range of parties, including
industry, technical experts, and others
to develop a list of technologies for
consideration. DOE then applied the
four screening criteria to determine
which technologies are unsuitable for
further consideration in the rulemaking
(10 CFR part 430, subpart C, appendix
A4.(a)(4) and 5.(b)). DOE presented its
results of the screening analysis in the
NOPR and in Chapter 4 of the NOPR
TSD. In response to the NOPR, DOE
received one comment about the
technology options that it considered in
the screening analysis.
ACEEE commented that DOE should
not have screened out some of the
technology options. Instead, DOE
should have further considered these
options in the engineering analysis.
(Public Meeting Transcript, No. 12 at
pp. 49–52, 64–65) ACEEE stated that
DOE neglected to examine other types of
compressors (such as scroll
compressors), electronically
commutated motor (ECM) fans, clutched
fan motors, micro-channel heat
exchangers, and thermostatic expansion
valves (TXVs). According to ACEEE, the
compressor choices for PTACs should
not be different from those used for
residential refrigerators because the
loads are similar. ACEEE added that
micro-channel heat exchangers
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allegedly cost less to implement, require
less refrigerant and space, and have
been used in air conditioning
applications within automobiles.
(Public Meeting Transcript, No. 12 at
pp. 50–51)
1. Scroll Compressors
As presented in Chapter 4 of the
NOPR TSD, scroll compressors are an
alternative to rotary compressors in airconditioning applications. Scroll
compressors are more efficient than
rotary compressors at higher cooling
capacities than are typically found in
packaged terminal equipment. Whereas
rotary compressors use a rotating
motion to compress refrigerant gases,
scroll compressors use two nutating
spirals—one fixed and the other
rotating. Although scroll compressors
can be more efficient than rotary
compressors, they typically are more
expensive, heavier, and larger than
rotary compressors of the same cooling
capacities.
After reviewing publicly available
equipment literature and specifications
for scroll compressors currently
available on the market, DOE
determined that manufacturers typically
produce scroll compressors with cooling
capacities of approximately 20,000
Btu/h or higher, and that the majority of
equipment using scroll compressors is
typically rated at capacities higher than
40,000 Btu/h. Manufacturers also
produce scroll compressors with
housings larger than those used for
compressors found in PTACs and
PTHPs. DOE found that scroll
compressors are typically built to be 16
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inches or higher in height and that
capacity ratings do not impact scroll
compressor heights significantly. For
example, DOE found that the height of
a scroll compressor only decreases by
approximately 1.5 inches when capacity
decreases from 80,000 to 20,000 Btu/h.
However, significant improvements in
efficiency, when compared to rotary
compressors, are generally achieved
with higher capacity models. DOE’s
market review also found that scroll
compressors weigh more than PTAC
and PTHP compressors. Scroll
compressors typically weigh 50 pounds
or more, compared with the 25 to 30
pounds for a PTAC/PTHP rotary
compressor found in PTACs and PTHPs.
Ultimately, DOE screened out scroll
compressors as a viable design option.
As stated in the NOPR and subsequently
confirmed by DOE using updated data,
manufacturers do not produce scroll
compressors for PTAC and PTHP
applications, making it unlikely that
this technology option could be readily
applied to these products. DOE also
screened out scroll compressors because
their manufacturers have yet to produce
a full line of scroll compressors that
meet the size limitations, capacity
requirements, and voltage requirements
of packaged terminal equipment. The
size limitation is particularly
problematic when given the installation
limitations of the sleeve sizes for PTACs
and PTHPs.
2. ECM Motors
As presented in Chapter 4 of the
NOPR TSD, there are multiple types of
electric fan motors that manufacturers
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can choose from to blow air over the
condenser and evaporator coils. Since
the PTAC and PTHP industries have a
relatively small number of annual
shipments, manufacturers typically
have to choose their motors from
existing motor lines, rather than having
motors customized for their specific
needs. The type of motor and its power
rating are typically indicative of its
efficiency. For example, shaded pole
motors are generally the lowest
efficiency motors that are available,
particularly at very low power levels. By
contrast, the electronically commutated
motors (ECM) or brushless permanent
magnet motors (BPMs) are typically the
most efficient motors for the low power
levels.
DOE determined that the PTAC and
PTHP industries have not adopted
ECMs or similar high efficiency motors
due to size and weight constraints. The
size limitation is particularly
problematic when given the installation
limitations of the sleeve sizes for PTACs
and PTHPs, particularly for nonstandard PTACs. Ultimately, DOE
screened out high efficiency motors as
a viable design option. As stated in the
NOPR and subsequently confirmed by
DOE using updated data and through
discussions with industry experts, DOE
found high efficiency motors are not
available in the full ranges of sizes
needed for the PTAC and PTHP
industries making it unlikely that this
technology option could be readily
applied to these products. DOE believes
that, given these circumstances, it
would not be practical to manufacture,
install, and service this technology on
the scale necessary to serve the relevant
market at the time of the effective date
of an amended standard.
3. Fan Motors
ACEEE commented on clutched fan
motors, but DOE did not consider this
technology. Although the automotive
industry uses clutched fans to engage
and disengage a vehicle’s cooling fan
from the belt driven by the engine, using
a clutched fan would not provide
appreciable benefits within the energy
efficiency context. In theory, these
devices would work with PTACs and
PTHPs to reduce the load on a single fan
motor used to drive both the evaporator
and the condenser fan blades when the
refrigerating system is not operating by
disengaging the condenser fan. In this
way, power input could be reduced
during times when only the indoor
blower is running to recirculate air, or
when electric resistance heating is being
provided. However, the measure of
energy use for PTACs in cooling mode
is based on full cooling operation, in
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which both the indoor blower and the
condenser fan must operate. Hence,
including a clutched condenser fan
would not provide measurable energy
efficiency benefits.
4. Micro-Channel Heat Exchangers
As presented in Chapter 4 of the
NOPR TSD, micro-channel heat
exchangers have a rectangular
aluminum cross-section containing
several small channels through which
refrigerant passes. Aluminum fins with
a corrugated shape are brazed at a 90degree angle between the rectangular
tubes. Micro-channel heat exchanger
designs provide more heat transfer per
volume of heat exchanger core and can
provide more heat transfer per unit of
face area. In addition, these designs
have lower airside pressure drop than
similarly performing conventional coils,
which reduces the fan power
requirement. The small size and lower
airside pressure drop that results from
micro-channel heat exchangers provide
opportunities to reduce the size and
weight of the heat exchanger. This
explains the frequent use of microchannel heat exchangers in automobile
air-conditioning systems, where their
small size and high performance allow
car designers to minimize air resistance
by lowering the leading edge of the car.
As stated in the NOPR TSD, DOE
screened out micro-channel heat
exchangers from the engineering
analysis. 73 FR 18869–70. Through
review of publicly available literature,
product specifications, and discussions
with manufacturers, DOE determined
that micro-channel heat exchangers
have inherent problems with
performance and condensate removal
when installed in PTAC equipment. In
particular, manufacturers observed that
the smaller airflow passages between
plate fins are subject to clogging in
installations where debris is present,
which can affect both the heat
exchanger and fan motor performance.
Additionally, for PTACs and PTHPs
operating in cooling mode, condensate
buildup on the evaporator of the
installation may result in icing, which is
harder to remove from small horizontal
micro-channel heat exchanger passages
than from the vertical fins found in the
currently used tube and fin heat
exchangers.
For the reasons stated above,
manufacturers have chosen not to install
micro-channel heat exchangers in PTAC
and PTHP designs. DOE determined that
this technology has not yet penetrated
the PTAC and PTHP industry and that
design challenges still exist. At this
time, DOE believes microchannel heat
exchangers are technologically
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infeasible in PTAC and PTHP
applications. DOE understands that
manufacturers are conducting research
into the use of micro-channel heat
exchangers in their PTACs and PTHP
design at this time. However, DOE does
not have definite knowledge of whether
their research efforts will be successful,
of when mirco-channel heat exchangers
could appear in either prototypes or
equipment designs, and what the cost
implications would be and the
contribution to system performance
would be. Because this technology is in
the research stage for the PTAC
industry, it is also not possible to assess
whether it will have any adverse
impacts on equipment utility to
customers or equipment availability, or
on customer health or safety.
5. Thermal Expansion Valves
Regarding ACEEE’s comments about
TXVs, DOE did not consider this
technology for PTACs or PTHPs. TXVs
are expansion devices that meter the
flow of refrigerant from the condenser to
the evaporator at a rate equivalent to the
amount of refrigerant being boiled off in
the evaporator. For example, when the
evaporator is exposed to high
temperatures, the TXV will open to
allow faster flow of refrigerant to match
the higher boiling rate caused by higher
temperatures. Alternatively, for lower
temperatures, the TXV will reduce the
flow rate to match the lower boiling rate
caused by cooler temperatures.
Typically, TXVs are installed in central
air conditioning applications where
equipment is rated with the seasonal
energy efficiency ratio (SEER) metric
and testing occurs at various operating
conditions and temperatures. In
contrast, PTACs and PTHPs are
measured using the EER metric, with
testing occurring at a constant
temperature of 95 degrees F. Therefore,
the energy efficiency benefits of a TXV
will not affect the EER rating of a PTAC
because the orifice of the TXV and the
flow of refrigerant would remain
constant during testing. Therefore, DOE
does not consider TXVs to be a
technology for improving the EER of
PTACs and PTHPs.
C. Engineering Analysis
The purpose of the engineering
analysis is to establish the relationship
between the cost and efficiency of
PTACs and PTHPs and to show the
manufacturing costs required to achieve
that increased efficiency level. As
detailed in the NOPR, DOE’s
engineering analysis for PTACs and
PTHPs estimated the baseline
manufacturer cost, as well as the
incremental cost for equipment at
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efficiency levels above the baseline. 73
FR 18870–74. DOE presented its
engineering analysis in the NOPR,
which included a discussion on the
approach, the equipment classes
analyzed, the cost model, the baseline
equipment, the alternative refrigerant
analysis, the cost efficiency results, and
mappings of the EER and COP values.
In response to DOE’s presentation of the
engineering analysis in the NOPR, DOE
received comments on the following
topics: Standard size equipment
performance in systems using R–410A
refrigerant, max-tech efficiency levels
analyzed for standard size equipment,
energy-efficiency equations for standard
size equipment, max-tech efficiency
levels analyzed for non-standard size
equipment, energy-efficiency for nonstandard size equipment, compressor
availability, and the manufacturer
production cost increases with the
introduction and use of R–410A. DOE
discusses each of these topics and the
updates to the cost model for the final
rule in the subsections below.
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1. Material Prices for the Cost Model
In the NOPR analyses, DOE used fiveyear average material prices from years
2002 through 2006. 73 FR 18871. For
the final rule, DOE updated the five-year
averages to include material price data
from 2007 and 2008. DOE uses a fiveyear span to normalize the fluctuating
prices experienced in the commodities
market to screen out temporary dips or
spikes. DOE believes a five-year span is
the longest span that would still provide
appropriate weighting to current prices
experienced in the market.
DOE basis for its belief relies on
updated commodity pricing data, which
point to continued increases. For
example, the 5-year time period ending
in mid-2008 has higher commodity
indices than a 5-year ending in mid2006 by 10 percent, 28 percent, and 45
percent for All Commodities, Steel, and
Copper, respectively.9 Considering the
significant amount of steel and copper
in each PTAC or PTHP, incorporating
commodity prices that reflect 5-year
average prices as close to the current
conditions best reflect the market
conditions. DOE believes it is
appropriate to use prices from 2007 and
2008 in the data span because it more
closely represents current PTAC and
PTHP material prices and
manufacturing conditions. DOE
calculated a new five-year average
9 Bureau of Labor Statistics (BLS) for Copper
(WPU102502), Cold Rolled Steel (WPU101707), and
All Commodities (WPU00000000) as tracked in the
Producer Price Index (PPI) database of the BLS. To
download the data or to discover how it is gathered,
please see https://www.bls.gov.
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materials price for cold rolled steel,
aluminized steel, galvanized steel,
painted cold rolled steel, and stainless
steel. DOE used the U.S. Department of
Labor’s Bureau of Labor Statistics (BLS)
Producer Price Indices (PPIs) for various
materials from 2004 to 2008 to calculate
new averages, which incorporate the
changes within each material industry
and inflation. Finally, DOE adjusted all
averages to 2007$ using the grossdomestic-product implicit-price
deflator.
As was the case for the NOPR, DOE
developed a material-price-sensitivity
analysis. DOE used the annual average
price for each of the raw materials from
2008 to calculate the current
manufacturing product costs (MPCs).
DOE expressed the material price
sensitivity results in 2007$. The results
for the material-price-sensitivity
analysis are presented in Chapter 5 of
the final rule TSD.
2. Impacts of the Refrigerant Phaseout
on PTAC and PTHP Equipment
Performance
a. Standard Size Equipment
Performance in Systems Using R–410A
Refrigerant
GE commented that R–410A
refrigerant has been in use for years by
the air conditioning industry. Even
though GE believes switching to R–
410A refrigerant in PTAC and PTHP
equipment will have a negative impact
on system efficiency, GE believes the
difference can be made up with a
combination of higher efficiency
compressors, motors, as well as
increases in heat exchanger size. GE
stated that manufacturers have been
aware of the future requirements and
should be far along with developments
and designs to meet both amended
energy conservation standards and R–
410A requirements. GE also pointed out
that one manufacturer has produced an
R–410A PTHP that exceeds the
proposed energy conservation standard
level in the NOPR (i.e., 11.5 EER for
standard equipment) and is currently
available on the market. (GE, No. 20 at
pp. 2–3; Public Meeting Transcript, No.
12 at pp. 17–18, 66) GE noted that it is
finishing the design and test phase for
several models and is confident that it
can manufacture standard size R–410A
PTACs and PTHPs at TSL 4 efficiency
levels (i.e., the proposed energy
conservation standards for PTHPs in the
NOPR). GE added that achieving an
efficiency level that is 10 percent higher
than the proposed standard for a
potential ENERGY STAR category is
also possible with existing technology.
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(GE, No. 20 at p. 3; Public Meeting
Transcript, No. 12 at p. 66)
In addition to comments from
manufacturers of standard size PTACs
and PTHPs, DOE also received
confidential performance test data that
characterizes the equipment
performance degradations in standard
size PTACs and PTHPs using R–410A
refrigerant. The confidential data DOE
received regarding standard size
equipment performance suggests the
performance degradation can vary
greatly depending upon the cooling
capacity of the equipment. DOE further
addresses comments from interested
parties and its analysis of the variation
in standard size equipment performance
with changes in cooling capacity in
DOE’s discussion of the energyefficiency equations, below.
DOE reviewed the data submitted by
manufacturers and comments from
interested parties and found, in general,
the system performance degradations for
PTAC and PTHP equipment with R–
410A, as described in the NOPR, were
in the middle of the range of the
submitted data. For today’s final rule,
DOE used the same system performance
degradations for PTAC and PTHP
equipment with R–410A refrigerants as
described in the NOPR. 73 FR 18873.
Because standard size PTAC and PTHP
equipment utilizing R–22 refrigerants
exists at efficiency levels well above the
efficiency levels in ASHRAE Standard
90.1–1999, DOE believes that
manufacturers will be able to produce
equipment utilizing R–410A at
efficiency levels specified by ASHRAE
Standard 90.1–1999 and higher
efficiency levels in 2012. As GE noted,
one standard size manufacturer is
already producing R–410A equipment at
efficiency levels above ASHRAE
Standard 90.1–1999 efficiency levels.
Lastly, the comments submitted by GE
establishes that PTAC and PTHP
prototypes utilizing R–410A refrigerant
have been developed and will be able to
meet the proposed efficiency levels, i.e.,
TSL 4, for standard size PTACs and
PTHPs.
As DOE reviewed the data submitted
by interested parties, DOE generally
found larger performance degradations
at higher cooling capacities for standard
size equipment. As a PTAC or PTHP
increases in capacity, manufacturers
typically increase the surface area or
add a row to the heat exchanger in order
to increase unit capacity. Even at larger
cooling capacities, manufacturers have
to maintain the same physical box
sleeve, leaving little space for additional
efficiency modifications (e.g., adding
heat exchanger area). DOE considered
the effects of the R–410A refrigerant
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phaseout on the entire range of cooling
capacities as part of the generation of
the energy-efficiency equations that
translates the results for the
representative cooling capacities to the
entire cooling capacity range. See
section IV.C.2.c for additional details on
how DOE extended the results for the
representative cooling capacities to the
full range of cooling capacities for
standard size PTACs and PTHPs.
b. ‘‘Max-Tech’’ Efficiency Levels
Analyzed for Standard Size Equipment
AHRI and the People’s Republic of
China, through its WTO/TBT National
Notification and Enquiry Center (PRC),
commented that the max-tech levels are
inaccurate because they are based on R–
22 refrigerant and there is no equipment
in the 2008 AHRI Directory of Certified
Product Performance (AHRI Certified
Directory) 10 operating with R–410A
refrigerant. AHRI and the PRC also
commented about the difficulty in
reaching the max-tech efficiency levels
with R–410A refrigerant and assert that
attaining those efficiency levels is not
possible at this time. (Public Meeting
Transcript, No. 12 at pp. 168–169; PRC,
No. 17 at p. 3)
DOE agrees that with the prohibition
on R–22 refrigerant, and the expected
use of R–410A refrigerant as the most
likely alternative, system performance
will decline. The max-tech efficiency
level should be based on the most likely
refrigerant, which is R–410A.
Accordingly, DOE revised the max-tech
efficiency levels for standard size
PTACs and PTHPs in the final rule
analysis. DOE applied the system
performance degradations described in
the NOPR to the AHRI certified market
data for standard size equipment. (See
graphs in Chapter 5 of the final rule
TSD.) DOE used the modified market
data to estimate the max-tech efficiency
levels corresponding to current models
utilizing R–410A and has identified
these efficiency levels in section III.B for
the representative cooling capacities.
DOE estimates that these performance
degradations will fall within five to
eight percent depending on cooling
capacity when compared to an R–22
baseline.
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c. Energy-Efficiency Equations for
Standard Size Equipment
In response to the NOPR, DOE also
received a comment on its approach for
calculating the energy efficiency
10 The
Air-Conditioning, Heating and
Refrigerating Institute, Directory of Certified
Product Performance for Packaged Terminal Air
Conditioners and Packaged Terminal Heat Pumps.
2008. .
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equations for standard size PTACs and
PTHPs. Carrier commented that the
engineering extrapolations might not
provide an accurate view of the maxtech efficiency levels for larger size
equipment. In particular, Carrier
commented that the PTAC efficiency
levels proposed in the NOPR are
achievable, but the PTHP proposed
efficiency levels in the NOPR may be
unachievable in equipment with a
cooling capacity of 12 kBtu/h and
above. (Carrier, No. 16 at p. 2)
DOE further considered the effects of
R–410A on system performance for
larger cooling capacities in the
engineering analysis. DOE found that as
a standard size PTAC or PTHP increases
in capacity, manufacturers typically
increase the coil surface area or add a
coil row to the heat exchanger in order
to increase unit capacity. Manufacturers
of standard size PTACs and PTHPs
maintain the same physical box sleeve
(i.e., 42 inches by 16 inches) across all
models regardless of cooling capacity.
This sleeve size is an established
common sleeve size that allows
standardization across the industry.
This common sleeve size allows endusers to simply slide replacement units
into existing wall sleeve openings.
However, the standard size wall sleeve
imposes a limitation on the total volume
available into which all components
must fit. Manufacturers add heat
exchanger coil area or coil volume to
either increase the cooling capacity or to
obtain higher efficiencies. This fixed
volume limits the size of the box into
which the unit’s components must fit.
In turn, this fixed volume limits the size
of heat exchangers and other
components that can be used to increase
efficiency and there are accompanying
decreases in thermodynamic returns
when making such changes. Thus,
higher capacity units often have lower
energy efficiency potentials due to the
size constraints of the box sleeve.
In order to consider the effects of the
refrigerant phaseout on larger capacity
units, DOE reviewed the market data for
standard size equipment in the AHRI
Certified Directory. DOE applied the
efficiency degradations distinguished by
cooling capacity ranges estimated in the
engineering analysis to each of the
models in the AHRI Certified Directory.
DOE used these data to estimate the
overall system performance of the
models in the AHRI Certified Directory
utilizing R–410A refrigerant. From these
data, DOE plotted each TSL it
considered as part of the final rule to see
if there were models in the full range of
cooling capacity with estimated
performance utilizing R–410A
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refrigerant that would meet the TSL
being considered.
For TSL A, which is the amended
standard level for standard size PTACs
and PTHPs, DOE adjusted the slope of
the energy-efficiency equation from the
revised slopes calculated in the NOPR
for TSLs 1 through 7. This adjustment
was based on manufacturer comment
and DOE data pointing to the reduced
opportunities for achieving greater
efficiencies for larger capacity PTAC
and PTHP equipment. By revising the
slope in this manner, DOE could create
and ultimately, adopt, a standard level
that is more stringent for lower cooling
capacities, where manufacturers have
additional physical space to add
efficiency improvements, but is less
stringent for higher cooling capacities,
where manufacturers are physically
constrained by the physical dimensions
of the box sleeve and less able to
introduce efficiency improvements. See
Chapter 9 of the final rule TSD for
additional details and graphic
demonstrations of the energy-efficiency
equations for each TSL, including
today’s amended energy conservation
standard for standard size PTACs and
PTHPs.
d. Efficiency Levels Analyzed for NonStandard Size Equipment
In the NOPR, DOE explicitly analyzed
one cooling capacity of non-standard
equipment (i.e., 11,000 Btu/h). Based
upon this cooling capacity, DOE
demonstrated a typical design option
pathway a manufacturer could use to
increase the efficiency of its nonstandard PTAC and PTHP equipment.
To account for the potential loss of
system efficiency as a result of the R–
22 refrigerant phaseout, DOE applied an
overall system degradation of 6.8
percent, which effectively shifted the
cost-efficiency curve to the left (in the
direction of decreasing efficiency for the
same cost). Thus, for any given
efficiency level, the MPC increase will
be greater when R–410A refrigerants are
used. By degrading expected system
performance, DOE accounts for the shift
in the baseline performance that a
system converted to R–410A use
typically exhibits. Using the design
option pathway described in the
engineering analysis, the maximum
efficiency level analyzed is 10.0 EER for
non-standard equipment with a cooling
capacity of 11,000 Btu/h using R–410A.
e. Energy-Efficiency Equations for NonStandard Size Equipment
In response to the NOPR, DOE
received several comments on its
approach for calculating the energyefficiency equations for non-standard
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size PTACs and PTHPs. Specifically,
DOE retained the ASHRAE Standard
90.1–1999 slope from the energyefficiency equation, which characterizes
the relationship between EER and
cooling capacity for non-standard
PTACs and PTHPs in the NOPR. 73 FR
18890–91.
ECR and AHRI commented that they
are particularly concerned about
reaching the efficiency levels for the
larger capacity, non-standard size
equipment. (AHRI, No. 23 at pp. 4–5;
Public Meeting Transcript (ECR), No. 12
at p. 170) ECR specifically commented
that it is concerned about the
methodology DOE used to develop the
energy-efficiency equations for nonstandard equipment. (ECR, No. 15 at p.
2) ECR and Ice Air commented that the
proposed energy conservation standard
for non-standard PTHPs is too high for
all capacities considering the system
performance degradations from
switching to R–410A refrigerant. (Public
Meeting Transcript, No. 12 at pp. 56–60;
Ice Air, No. 25 at p. 2)
DOE further considered the effects of
R–410A on system performance in the
engineering analysis for larger cooling
capacities of non-standard PTACs and
PTHPs. As explained above, DOE found
that as a non-standard size PTAC or
PTHP increases in capacity,
manufacturers typically increase the
coil surface area or add a coil row to the
heat exchanger in order to increase unit
capacity. The fixed volume of the box
sleeve imposes a physical limit on the
size of heat exchangers and other unit
components that can be used to increase
efficiency. Thus, higher capacity units
often have lower energy efficiency
potential due to the size constraints of
the box.
In order to consider the effects on
larger capacity units, DOE reviewed the
market data for non-standard size
equipment in manufacturer equipment
catalogs. DOE applied the efficiency
degradations distinguished by cooling
capacity ranges estimated in the
engineering analysis to each of the nonstandard models offered for sale and
described in manufacturer equipment
catalogs. DOE used this data to estimate
the overall system performance of the
models on the market utilizing R–410A
refrigerant. DOE was able to plot each of
the TSLs it considered as part of the
final rule (i.e., TSL 1 through 5) to see
if there were models in the full range of
cooling capacities with estimated
performance utilizing R–410A
refrigerant that would meet the TSL
being considered. These plots
demonstrated the specific cooling
capacities where the TSL or amended
standard would be eliminating all of the
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models from the market using the
estimated R–410A performance. See
Chapter 9 of the final rule TSD for
additional details and graphic
demonstrations of the energy-efficiency
equations for each TSL, including
today’s amended energy conservation
standard for non-standard size PTACs
and PTHPs.
DOE further considered the effects of
the refrigerant phaseout on larger
cooling capacities when weighing the
benefits and the burdens for nonstandard equipment. See section V.D for
additional information.
f. Compressor Availability
AHRI, Carrier, Ice Air, ECR, and
Goodman stated that the true impact on
PTAC and PTHP equipment efficiency
levels cannot currently be assessed
because the lack of available
components across the range of
equipment capacities prevents
comprehensive equipment testing.
These manufacturers also stated that R–
410A compressors are not available in
all required capacities and voltages.
Further, compressor manufacturers have
not committed to improving compressor
performance of rotary compressors.
(Public Meeting Transcript (ECR), No.
12 at p. 68–69; Public Meeting
Transcript (Goodman), No. 12 at p. 174;
AHRI, No. 23 at p. 4; Carrier, No. 16 at
p. 5; Ice Air, No. 25 at pp. 1–2)
As DOE presented in the NOPR, DOE
found the availability of R–410A
compressors in a wide range of
efficiencies and voltages remains
uncertain. Several compressor
manufacturers make R–22 PTAC and
PTHP compressors of different
capacities, voltages, and efficiencies for
standard and non-standard equipment.
As the market transitions to the use of
R–410A, manufacturers may only
develop and offer one line of
compressors for PTACs and PTHPs. In
engineering interviews conducted for
the NOPR, compressor manufacturers
commented on the uncertainties
surrounding R–410A compressors and
their performance characteristics when
compared to R–22 compressors. 73 FR
18874. DOE noted in the NOPR that
compressor manufacturers stated in
interviews that they expect to offer R–
410A compressors at only one efficiency
level in the initial stages of the R–22
refrigerant phaseout, which could
further reduce compressor options for
PTAC and PTHP manufacturers. Id.
In response to comments and the
uncertainty surrounding compressor
options for manufacturers, DOE gave
particular attention to the PTAC and
PTHP efficiency levels that cannot be
met with current technologies and
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58787
practices with R–410A in weighing the
benefits and burdens of the various
TSLs. However, DOE notes that GE
stated its working prototypes have
experienced significantly less
performance degradation due to R–410A
conversion than was modeled in the
engineering analysis. (GE, No. 20 at p.
2) Based on manufacturer feedback
during interviews and historic
precedent in other air-conditioning
markets where similar refrigerant
transitions have taken place, DOE
acknowledges that the R–410A
compressors available for use in PTAC
and PTHP equipment could be less
efficient than similar compressors that
use R–22 refrigerant at the time of the
R–22 phaseout. Even though DOE
received comments during engineering
interviews stating compressor
manufacturers may only offer one rotary
compressor line when the refrigerant
phaseout occurs, DOE believes
compressor manufacturers will continue
their development efforts and
eventually offer compressors in the full
range of cooling capacities, voltages,
and efficiencies as they do today.
Similar market transformations have
occurred in other industries and while
the initial set of compressors were less
efficient, the markets eventually
matured to offer manufacturers a variety
of compressors. See Chapter 5 of the
TSD for additional information. In
addition, DOE believes the amended
energy conservation standards being
adopted in today’s final rule will aid the
PTAC and PTHP industry and provide
compressor manufacturers with target
efficiencies for which they can
concentrate their research and
development efforts.
3. Manufacturer Production Cost
Increases With R–410A
Goodman stated that DOE’s estimate
of a two percent manufacturing cost
increase for converting standard size
PTAC and PTHP equipment to utilize
R–410A refrigerant is too low. (Public
Meeting Transcript, No. 12 at pp. 46–47,
74)
Goodman misstates DOE’s estimate.
DOE did not use a two percent cost
increase. To derive the baseline MPCs
for the R–410A PTACs and PTHPs used
in the NOPR, DOE estimated the
R–410A refrigerant pricing, R–410A
compressor pricing, as well as other
design changes necessary to
accommodate the alternative refrigerant,
and incorporated them into the same
cost model used for the R–22
engineering analysis. Based on technical
journals and manufacturer interviews,
DOE increased the tube wall thicknesses
of all heat exchangers by 25 percent to
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account for the higher pressures
associated with R–410A refrigerant.
DOE also used a refrigerant price for
R–410A based upon cost estimates from
refrigerant suppliers and engineering
interviews with manufacturers. During
engineering interviews, PTAC and
PTHP equipment and component
manufacturers stated that compressor
prices would increase between 10
percent and 20 percent from current
R–22 compressor prices. To incorporate
manufacturers’ comments, DOE
estimated that compressor costs would
increase by 15 percent. Using the above
estimates, DOE calculated the baseline
manufacturer selling price (MSPs) 11 of
R–410 standard size equipment to be at
least 10 percent more than its’ R–22
counterpart, on average. See Chapter 5
of the final rule TSD for additional
details of the R–410A analysis and
results. See TSD, Chapter 5, Section 5.8
(detailing representative capacities of
standard size equipment using R–410A).
Accordingly, DOE believes
Goodman’s statement mischaracterizes
the estimated manufacturing cost
increases in the NOPR. DOE has
continued to use the same methodology
as presented in the NOPR to develop the
R–410A manufacturer production costs
for both standard size and non-standard
size equipment. After DOE revised the
cost model in response to comments
from interested parties, DOE calculated
the baseline MSPs to be at least 15
percent more than its R–22 counterpart,
on average, for standard size PTAC and
PTHP equipment. Additional details
and results can be found in section 5.8
of Chapter 5 of the final rule TSD.
D. Energy Use Characterization
The building energy use
characterization analysis assessed the
energy savings potential of PTAC and
PTHP equipment at different efficiency
levels. The analysis estimates the energy
use of PTACs and PTHPs at specified
energy efficiency levels through energy
use simulations for key commercial
building types across a range of climate
zones. The energy simulations yielded
hourly estimates of building energy
consumption, including lighting, plug
loads, and air-conditioning and heating
equipment. The analysis extracted the
annual energy consumption of the
PTACs and PTHPs for use in subsequent
analyses, including the LCC, PBP, and
NES.
DOE did not consider a rebound effect
in the final rule analysis when
determining the reduction in energy
consumption of PTAC and PTHP
equipment due to increased efficiency.
The rebound effect occurs when a piece
of equipment is made more efficient
such that the operating costs come
down to a point that either the use of
the product increases or the market
increases, resulting in lower than
expected energy savings. Because the
user of the equipment (e.g., the
customer in a hotel room) does not pay
the utility bill, DOE assumed that
increasing the efficiency of the
equipment will not affect the usage or
market for the equipment and, as a
result, no rebound effect would occur.
DOE requested comment on this
assumption in the NOPR. 73 FR 18876.
The commenters all agreed that there
would be no rebound effect for PTACs
and PTHPs. (Public Meeting Transcript
(ECR), No. 12 at p. 138, GE, No. 8 at p.
2, Carrier, No. 16 at p. 2) Based on the
above, DOE did not incorporate a
rebound effect into the final rule
analysis.
E. Life-Cycle Cost Analysis
For each efficiency level analyzed, the
LCC analysis requires input data for the
total installed cost of the equipment, its
operating cost, and the discount rate.
Table IV.2 summarizes the inputs and
key assumptions used to calculate the
customer economic impacts of all
energy efficiency levels analyzed in this
rulemaking. DOE also calculated the
PBP of the TSLs relative to a baseline
efficiency level. The PBP measures the
amount of time it takes the commercial
customer to recover the assumed higher
purchase expense of more energy
efficient equipment through lower
operating costs. Similar to the LCC, the
PBP is based on the total installed cost
and operating expenses, and is
calculated as a range of payback periods
depending on the probability
distributions of the two key inputs (i.e.,
the supply chain markups and where
the unit is likely to be shipped). Unlike
its calculation of the LCC, DOE’s
calculation of the PBP considered only
the first year’s operating expenses.
Because the PBP does not account for
changes in operating expense over time
or the time value of money, it is also
referred to as a simple payback period.
Aside from the installation cost, the
primary change for the final rule
analysis affecting PBP is the electricity
price forecasted for 2012 based on the
2007 EIA State energy price data and the
AEO2008 electricity price forecasts.
Chapter 8 of the TSD discusses the PBP
calculation in more detail.
TABLE IV.2—FINAL RULE INPUTS AND KEY ASSUMPTIONS USED IN THE LCC AND PBP ANALYSES
Inputs
NOPR description
Changes for final rule
Overall
LCC Reporting .....................
All cost inputs and LCC analysis and reporting done in
2006 dollars (2006$).
Updated cost inputs and LCC reporting to 2007 dollars
(2007$).
Affecting Total Installed Cost
Derived by multiplying MSP (from the engineering analysis) by wholesaler markups and contractor markups
plus sales tax (from markups analysis). Used the
probability distribution for the different markups to describe their variability.
Installation Cost ...................
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Equipment Price ...................
Includes installation labor, installer overhead, and any
miscellaneous materials and parts, derived from RS
Means CostWorks 2007.
All MSPs updated to 2007. Updated wholesaler markup
to use 2007 industry (Heating, Airconditioning and
Refrigeration Distributors International (HARDI)) data.
Sales tax data updated to 2008. Used State population
weights to determine distribution of sales updated to
2007 census data.
Used RS Means CostWorks 2008 data to update installation costs.
11 This is the price at which the manufacturer can
recover both production and non-production costs
and earns a profit.
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58789
TABLE IV.2—FINAL RULE INPUTS AND KEY ASSUMPTIONS USED IN THE LCC AND PBP ANALYSES
Inputs
NOPR description
Changes for final rule
Affecting Operating Cost
Annual Energy Use ..............
Electricity Price ....................
Maintenance Cost ................
Repair Cost ..........................
Derived from whole-building hourly energy use simulation for PTACs or PTHPs in a representative hotel/
motel building in various climate locations (from energy use characterization analysis). Used annual
electricity use per unit. Used the probability distribution to account for which State a unit will be shipped
to, which in turn affects the annual energy use.
Calculated average commercial electricity price in each
State, as determined from DOE Energy Information
Administration (EIA) data for 2006. Used the
AEO2007 forecasts to estimate the future electricity
prices. Used the probability distribution for the electricity price.
Annual maintenance cost did not vary as a function of
efficiency.
Estimated the annualized repair cost for baseline efficiency PTAC and PTHP equipment as $15, based on
costs of extended warranty contracts for PTACs and
PTHPs (Chapter 8 of the TSD). Assumed that repair
costs would vary in direct proportion with the MSP at
higher efficiency levels because it generally costs
more to replace components that are more efficient.
No change.
Used EIA data for 2007 to update the analysis for average electricity price by state. Used the AEO2008
electricity price forecasts to calculate future prices.
Annual maintenance costs updated to use RS Means
CostWorks 2008 data.
No change.
Affecting Present Value of Annual Operating Cost Savings
Equipment Lifetime ..............
Discount Rate ......................
Date Standards Become Effective.
Used the probability distribution of lifetimes, with mean
lifetime for each of four equipment classes assumed
to be 10 years based on literature reviews and consultation with industry experts.
Mean real discount rates ranging from 5.7% for owners
of health care facilities to 8.2% for independent hotel/
motel owners. Used the probability distribution for the
discount rate.
September 30, 2012 (4 years after the publication of
the final rule).
No change.
Used 2008 financial data discount rate calculations to
update discount rates.
Mean real discount rates ranging from 5.53% for owners of large motel/hotel chains to 8.14% for offices.
No change.
Analyzed Efficiency Levels
Analyzed Efficiency Levels ..
Baseline efficiency levels (ASHRAE Standard 90.1–
1999) and five higher efficiency levels above the
baseline for six equipment classes. (DOE also considered levels that were combinations of efficiency
levels for PTACs and PTHPs.)
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For this final rule, DOE did not
introduce changes to the life-cycle cost
methodology described in the NOPR.
However, as the following sections
discuss in more detail, DOE revised the
inputs to the LCC analysis.
1. Equipment Prices
The price of a PTAC or PTHP reflects
the application of distribution channel
markups and the addition of sales tax to
the MSP as described in the NOPR.
Modifications made for the final rule
include using the latest MSP data in
2007$ and incorporating changes to the
material prices discussed previously,
updating the wholesale markups to use
2007 data available from the HARDI
2007 Profit Report, updating State sales
tax data to 2008 data from the Sales Tax
Clearing House Web site, and updating
State population data (used for
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No change for standard size PTAC and PTHP equipment classes.
Only three efficiency levels above the baseline analyzed for non-standard size equipment classes.
allocating national shipments to Statelevel shipments) to use 2007
information from the U.S. Census
Bureau.
2. Installation Costs
For the NOPR, DOE derived
installation costs for PTACs and PTHPs
from data provided in RS Means
CostWorks 2007 (RS Means).12 For the
final rule, DOE updated the installation
costs using the RS Means CostWorks
2008 data. Several commenters gave
their views on whether higher
installation costs should be assumed for
PTHP equipment compared with PTAC
equipment. Goodman commented that
drain systems for PTHP installations as
required by several of the building
12 R.S. Means Company, Inc. 2007. RS Means
CostWorks 2007. Kingston, Massachusetts.
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codes might be fairly expensive,
resulting in higher installation costs for
PTHP compared to PTAC equipment.
Goodman pointed out that the odds of
replacing a PTAC with a PTHP are low
because of the additional cost to add
drains during equipment replacement.
(Goodman, No 8.4 at p. 116) GE
commented that DOE does not need to
include a significant cost in the LCC for
a drainage system because several
manufacturers offer low cost kits and
special models that remove moisture
without the use of a drainage system.
(GE, No. 20 at p. 3) Since there was
differing opinion with regard to whether
higher installation costs would be
required for PTHP equipment and since
these installation costs were held
constant for all efficiency levels and
would not affect the LCC savings or
NPV figures calculated for higher
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efficiency PTHP or PTAC standards,
DOE did not further modify the
installation costs beyond what was
reflected in the RS Means CostWorks
data.
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3. Annual Energy Use
DOE estimated the electricity
consumed in kilowatt hours per year
(kWh/year) by the PTAC and PTHP
equipment based on the whole-building
energy use characterization as described
in the NOPR. 73 FR 18876. DOE also
used the same energy use data and
characterization developed for the
NOPR analysis in the final rule. See
Chapter 7 of the NOPR and FR TSDs for
additional information.
4. Electricity Prices
Electricity prices are needed to
convert the electric energy savings into
energy cost savings. DOE updated the
State-by-State average electricity price
information for the commercial sector to
reflect 2007 data available from EIA.
DOE further adjusted these prices to
reflect average electricity prices for the
four types of businesses DOE identified
that use PTAC and PTHP equipment.
DOE identified these businesses using
Commercial Buildings Energy
Consumption Survey (CBECS) 2003
data,13 as described in the NOPR. To
develop the LCC distributions, DOE
continued to use a probability
distribution to determine not only
which State received the shipment of
equipment, but also which business
types would purchase the equipment
and what electricity price they would
pay. State populations formed the basis
for allocating the equipment shipment
distribution to different States. DOE
updated these State-by-State population
data with 2007 data published by the
U.S. Census. The State-average effective
prices (2007$) range from approximately
5.1 cents per kWh to approximately 28.0
cents per kWh. Chapter 8 of the TSD
details the development and use of
State-average electricity prices by
business type.
The electricity price trend provides
the relative change in electricity prices
for future years to 2042. DOE applied
the AEO2008 reference case as the
default scenario and extrapolated the
trend in values from 2020 to 2030 of the
forecast to establish prices for 2030 to
2042, as in the NOPR. DOE provided a
sensitivity analysis of the LCC savings
and PBP results to future electricity
price scenarios. Because EIA did not
publish its high- and low-growth
forecasts in time for incorporation into
13 EIA’s CBECS 2003 is the most recent version
of this data set.
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this final rule, DOE developed high- and
low-growth electricity forecasts
corresponding to the AEO2008
forecasts. DOE calculated the ratio of the
AEO2007 high- or low-growth
forecasted electricity price to the
AEO2007 reference case forecast for
each year. DOE then applied those
ratios, respectively, to the AEO2008
reference case prices.
5. Maintenance Costs
Maintenance costs are the customer’s
costs to keep equipment in top
operating condition. For the NOPR, DOE
estimated annual routine maintenance
costs for PTAC and PTHP equipment at
$50 per year per unit. DOE explained
that this estimate was based on
statements made during informational
interviews with manufacturers. Because
data were not available to indicate how
maintenance costs vary with equipment
efficiency, DOE thus determined to use
this preventative maintenance costs that
remain constant as equipment efficiency
is increased. 73 FR 18879. For the final
rule, DOE updated the maintenance
costs to reflect data for packaged
terminal equipment available in RS
Means Costworks 2008.
In the NOPR, DOE specifically
requested comments on its estimate for
maintenance costs and whether the
assumptions made would be the same
under R–410A. GE commented that
repair and maintenance costs (primarily
cleaning) would be fixed costs and
handled either in house or contracted
out. GE’s experience working with their
customers is that maintenance costs are
not a function of equipment efficiency,
even though GE equipment efficiencies
have increased nearly 10% in the past
5 years. (Public Meeting Transcript, No.
12 at p. 99) Goodman commented that
third-party servicers or hoteliers
themselves may be better sources of
maintenance cost data than
manufacturers. (Public Meeting
Transcript, No. 12 at pp. 111–112) AHRI
commented that maintenance costs will
increase with heat exchanger surface
area that is commensurate with higher
efficiency equipment. (Public Meeting
Transcript, No. 12 at pp. 97–98)
Goodman expressed concerns over
condenser maintenance if
manufacturers use closer fin spacing or
three or four row coils due to the slinger
ring throwing water on the coil and dirt
buildup. Goodman also pointed out that
dirty condensers can degrade
compressors through overheating. This
compressor degradation is a long-term
impact not improved by coil cleaning.
(Public Meeting Transcript, No. 12 at
pp. 111–112) ACEEE commented that
equipment redesigns are likely to result
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in reduced repair costs, which would
offset any additional maintenance costs.
(Public Meeting Transcript, No. 12 at p.
98)
Although opinions were expressed
that maintenance costs might increase
as a function of efficiency level, this
appears not to be the case in GE’s
experience. Accordingly, DOE decided
to use the Means CostWorks 2008
estimate of preventive maintenance
costs, which remain constant as
equipment efficiency increases.
6. Repair Costs
The repair cost is the customer’s cost
of replacing or repairing components
that have failed in the PTAC and PTHP
equipment. DOE estimated annual
repair costs for the final rule in the same
way that it estimated annual repair costs
for the NOPR. DOE estimated the
annualized repair cost for baseline
efficiency PTAC and PTHP equipment
at $15, based on costs of extended
warranty contracts for PTACs and
PTHPs. After analyzing these data, DOE
determined that repair costs would
increase in direct proportion with
increases in equipment prices. See
Chapter 8 of the TSD for additional
details.
In the NOPR, DOE specifically
requested comment on its estimation for
repair costs, as well as installation and
maintenance costs. The comments DOE
received addressed several areas. GE
commented that it does not expect the
compressor service call rate to increase
for higher efficiency equipment because
GE already has rotary compressors in
service. (GE, No. 20 at p. 2) Carrier
stated that it would expect to see
slightly higher repair costs overall for
R–410A refrigerant equipment because
of the more hygroscopic nature of R–
410A. (Carrier, No. 16 at p. 3) ECR
warned that if efficiency standards are
set too high, existing R–22 refrigerant
equipment may be kept in place longer,
which may result in increased repair
costs. Although DOE recognizes that
overall repair costs may increase under
R–410A, commenters provided no data
to refine DOE’s repair cost estimate for
equipment using R–410A refrigerant.
Because no commenter expressed
disagreement with DOE’s methodology
of scaling repair costs with efficiency
level, DOE continued to use the same
approach in the final rule. DOE
recognizes that the extension of life for
R–22 equipment is possible under any
scenario, but has no data with which to
refine its shipment or repair cost
analysis. DOE believes that the impact
of life extension for R–22 equipment
would, if it occurs, primarily affect the
energy savings estimate. However,
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because extension of life generally
increases the period over which a
purchased product can provide services
regardless of efficiency level or
refrigerant, DOE does not expect a
significant impact on the economics of
higher-efficiency PTAC and PTHP
equipment to the Nation.
7. Equipment Lifetime
DOE defines equipment lifetime as
the age when a PTAC or PTHP unit is
retired from service. For the NOPR, DOE
used a typical lifetime of 10 years after
reviewing available data sources and
concluding that a 10-year life is
appropriate for PTAC and PTHP
equipment. DOE incorporated
variability in lifetime in its LCC analysis
using a Weibull 14 statistical distribution
with an average lifetime of 10 years and
a maximum lifetime of 20 years. In
response to the NOPR, DOE received no
comments on the lifetime assumptions
for new equipment purchases that
would affect the LCC analysis. DOE,
therefore, retained the same lifetime
assumptions and methodologies
developed for the NOPR in the final rule
analysis. See Chapter 8 of the TSD for
additional information.
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8. Discount Rate
The discount rate is the rate at which
future expenditures are discounted to
establish their present value. DOE
estimated the discount rate by
estimating the weighted average cost of
capital (WACC) for purchasers of PTAC
and PTHP equipment based on
weighting the cost of both debt and
equity capital used to fund investments.
For the NOPR, DOE used financial
information from a sample of
companies, including large hotel/motel
chains and health-care chains drawn
from a database of U.S. companies on
the Damodaran Online Web site. See
https://pages.stern.nyu.edu/~adamodar.
The NOPR used the data available in
2007. The final rule’s analysis relies on
the same data source to develop
discount rates, but was updated to
reflect the data available in January
2008.
DOE calculated the weighted average
after-tax discount rate for PTAC and
PTHP purchases, adjusted for inflation,
as 5.53 percent for large hotel chains
and 5.64 percent for health care
institutions (nursing homes and assisted
living facilities). The cost of capital for
14 The Weibull distribution is a continuous
probability distribution used to understand the
failure and durability of equipment. It is popular
because it is extremely flexible and can accurately
model various types of failure processes. A twoparameter version of the Weibull was used and is
described in chapter 8 of the TSD,
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independent hoteliers and small office
companies is more difficult to
determine because these business types
are not explicitly identified in the
Damodaran data. For the final rule, DOE
used the same methodology that it used
to determine the discount rates for these
business types in the NOPR.
Specifically, DOE developed an 8.03
percent after-tax discount rate for
independent hoteliers and an 8.14
percent after-tax rate for small offices.
These values vary only slightly from
those presented in the NOPR. Chapter 8
of the TSD provides more detail on the
calculation of discount rates.
F. National Impact Analysis—National
Energy Savings and Net Present Value
Analysis
The National Impact Analysis (NIA)
evaluates the impact of an amended
energy conservation standard from a
national perspective rather than from
the customer perspective, which is
represented by the LCC. This analysis
assesses the NES and the NPV (future
amounts discounted to the present) of
total commercial customer costs and
savings, which are expected to result
from amended energy conservation
standards for PTACs and PTHPs at
specific efficiency levels. DOE followed
the same analysis approach for the NIA
as it used for the NOPR analysis, using
a Microsoft Excel spreadsheet model to
calculate the energy savings and the
national economic costs and savings
from amended energy conservation
standards. Unlike the LCC analysis, the
NES spreadsheet does not use
distributions for inputs or outputs. DOE
examined sensitivities by applying
different scenarios. DOE used the NES
spreadsheet to perform calculations of
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, equipment
costs, and NPV of benefits for each TSL
from 2012 through 2042. The forecasts
provided annual and cumulative values
for all four output parameters.
For each TSL, DOE calculated the
NES and NPV as the difference between
a base case forecast (without amended
standards) and the standards case (with
amended standards). The NES refers to
cumulative energy savings from 2012
through 2042. The NPV refers to
cumulative monetary savings. DOE
calculated net monetary savings in each
year relative to the base case as the
difference between total operating cost
savings and increases in total installed
equipment cost. Cumulative savings are
the sum of the annual NPV over the
specified period. DOE accounted for
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58791
operating cost savings until 2062 (i.e.,
until all the equipment installed
through 2042 is retired).
DOE built up the NES analysis from
a combination of unit energy savings for
each class of PTAC or PTHP equipment
analyzed and estimated shipments of
units in this class at each efficiency
level from 2012 through 2042. Unit
energy savings for each equipment class
are the weighted-average values
calculated in the LCC and PBP
spreadsheet. These calculations
involved multiple steps. First, DOE
calculated the national site energy
consumption (i.e., the energy directly
consumed by the units of equipment in
operation) for PTACs or PTHPs for each
year, beginning with the expected
effective date of the standards (2012) for
the base-case forecast and the standards
case forecast. Second, DOE determined
the annual site energy savings,
consisting of the difference in site
energy consumption between the base
case and the standards case. Third, DOE
converted the annual site energy savings
into the annual amount of energy saved
at the source of electricity generation
(the source energy). DOE used a site-tosource conversion factor developed
from an analysis of the marginal impacts
of changes in PTAC and PTHP energy
use on the energy source energy inputs
in DOE’s Utility Impacts analysis.
Finally, DOE summed the annual source
energy savings from 2012 to 2042 to
calculate the total NES for that period.
DOE performed these calculations for
each TSL and equipment class
considered in this rulemaking.
Changes in inputs to the analyses and
reporting drove the modifications to the
NIA analyses and results. Changes to the
NES results between the NOPR and final
rule were due to a reduction in the TSL
levels considered for non-standard
PTAC and PTHP equipment classes and
a change in the mix of equipment
efficiencies used in the base case and
standards case equipment efficiency
forecasts. Although DOE used the same
economic model for predicting the
distribution of equipment efficiencies in
both the final rule and the NOPR, these
changes in the installed equipment
prices and the lower R–410A max tech
efficiency levels resulted in slight shifts
to the overall efficiency distributions for
each equipment class. In addition, the
site-to-source energy conversion factor
developed for the final rule used EIA’s
NEMS model consistent with AEO2008.
The calculated conversion factors in the
final rule differed from that calculated
for the NOPR, which relied on EIA’s
AEO2007.
To estimate NPV, DOE calculated the
net impact as the difference between
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total operating cost savings (including
electricity, repair, and maintenance cost
savings) and increases in total installed
costs (including MSP, sales taxes,
distribution chain markups, and
installation cost). DOE calculated the
NPV of each TSL over the life of the
equipment by determining: (1) The
difference between the equipment costs
under the TSL case and the base case in
order to obtain the net equipment cost
increase resulting from the TSL; (2) the
difference between the base case
operating costs and the TSL operating
costs in order to obtain the net operating
cost savings from the TSL; and (3) the
difference between the net operating
cost savings and the net equipment cost
increase in order to obtain the net
savings (or expense) for each year. DOE
then discounted the annual net savings
(or expenses) to 2008 for PTACs and
PTHPs bought between 2012 and 2042,
and summed the discounted values to
provide the NPV of a TSL. DOE used
discount rates of 7 percent and 3
percent in accordance with Office of
Management and Budget (OMB)
guidance to evaluate the impacts of
regulations. An NPV greater than zero
shows net savings (i.e., the TSL would
reduce customer expenditures relative
to the base case in present value terms).
An NPV less than zero indicates that the
TSL would result in a net increase in
customer expenditures in present value
terms.
Changes in inputs to the analyses and
reporting drove modifications to the
NPV analyses and results. Changes to
the NES results were due to (1) a
reduction in the number of TSL levels
considered for non-standard PTAC and
PTHP equipment classes, (2) a change in
the mix of equipment efficiencies used
in the base case and standards case
equipment efficiency forecasts, and (3)
the use of electricity price forecasts from
the AEO 2008 reference case. As with
the LCC analysis, DOE analyzed highand low-growth energy price forecasts.
Because EIA had not published actual
high- and low-growth forecasts in time
for the final rule analysis, DOE
developed high- and low-growth
scenarios based on the AEO2008
reference case forecast. DOE applied the
ratio of the year-by-year energy prices
from the AEO2007 high- and lowgrowth price forecasts, respectively, to
the AEO2007 reference case forecast.
Chapter 10 of the TSD provides a full
discussion of the NIA. Table IV.3
summarizes the inputs and key
assumptions used to calculate the
national energy savings and national
economic impacts of all energy
efficiency levels analyzed in this
rulemaking.
TABLE IV.3—SUMMARY OF NES AND NPV MODEL INPUTS
Inputs
NOPR description
Shipments ............................
Annual shipments from shipments model (Chapter 10
of the TSD).
September 2012 ..............................................................
Distribution of base case shipments by efficiency level
Effective Date of Standard ...
Base Case Efficiencies ........
Standard Case Efficiencies ..
Annual Energy Use per Unit
Total Installed Cost per Unit
Repair Cost per Unit ............
Maintenance Cost per Unit ..
Escalation of Electricity
Prices.
Electricity Site-to-Source
Conversion Factor.
Discount Rate ......................
Present Year ........................
Changes for final rule
Distribution of shipments by efficiency level for each
standards case. Standards case annual shipmentweighted market shares remain the same as in the
base case and each standard level for all efficiencies
above the TSL. All other shipments are at the TSL
efficiency.
Annual national weighted-average values are a function
of efficiency level.
Annual weighted-average values are a function of efficiency level.
Annual weighted-average values increase with manufacturer’s cost level.
Annual weighted-average value equals $50 (Chapter 8
of the TSD).
2007 EIA AEO forecasts (to 2030) and extrapolation
beyond 2030.
Conversion factor varies yearly and is generated by
EIA’s NEMS * model for AEO2007. Includes the impact of electric generation, transmission, and distribution losses.
3% and 7% real ..............................................................
Future costs are discounted to year 2008 ......................
No change.
No change.
Equipment costs and economic benefits for each TSL
level come from final rule LCC analysis.
Equipment costs and economic benefits for each TSL
level come from final rule LCC analysis.
Only three TSL levels considered for non-standard
PTAC and PTHP equipment.
No change.
Updated with values from final rule LCC analysis.
Updated with values from final rule LCC analysis.
Updated with values from final rule LCC analysis.
2008 EIA AEO forecasts (to 2030) and extrapolation for
beyond 2030.
Developed conversion factor using EIA’s NEMS model
for AEO 2008.
No change.
No change.
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* Chapter 14 on the utility impact analysis provides more detail on NEMS model.
1. Shipments Analysis
DOE developed shipments projections
under a base case and each of the
standards cases using the identical
shipments model used in the NOPR
analysis. The NOPR and Chapter 10 of
the TSD describe this model in more
detail.
The NES spreadsheet model contains
a provision for a change in projected
shipments in response to efficiency
level increases, but DOE has no
information with which to calibrate
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such a relationship. For the NOPR
analysis, DOE assumed that the
shipments do not change in response to
the changing TSLs. ECR and Cold Point
commented that if DOE sets a high or
unrealistic efficiency level for nonstandard PTAC or PTHP equipment,
customers might choose to extend the
life of existing equipment that uses
R–22 refrigerant. (Public Meeting
Transcript (ECR), No. 12 at pp. 100–101,
Cold Point, No. 18 at p. 2) However,
commenters provided no data to suggest
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specific changes that DOE could make
to its shipments analysis to account for
this possible impact. For the final rule
analysis, DOE presumed that projected
industry shipments by product class do
not change in response to changing
TSLs. See discussion of equipment
lifetime in section IV.E.7.
GE, ECR, and Carrier commented that
it was possible that customers could
switch to a less efficient class of HVAC
equipment than a packaged terminal
unit, such as a through-the-wall air
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conditioner or a window air
conditioner, which does not have a heat
pump option for providing space heat.
Carrier elaborated that this kind of
equipment switch would occur mostly
in small, independent, motel markets.
(Public Meeting Transcript (GE), No. 12
at p. 141; Public Meeting Transcript
(ECR), No. 12 at p. 141–141; Public
Meeting Transcript (Carrier), No. 12 at
p. 143)
Several interested parties commented
that DOE’s proposed standard level in
the NOPR, TSL 4, had higher cooling
efficiency requirements for PTHP
equipment compared with PTAC
equipment of the same capacity. This
difference would mean higher
proportional costs for PTHP equipment
under the new energy conservation
standard compared with PTAC
equipment, and is likely to result in
some current or future PTHP customers
choosing to purchase PTAC equipment.
If this occurs, there would be a decrease
in overall equipment efficiency due to
the much lower heating efficiency of
PTAC compared with PTHP equipment.
Several manufacturers expressed
concern that people would be forced by
cost or lack of products at the proposed
standard levels to shift from PTHP to
PTAC—forcing people into a less
efficient product and negating much of
the energy savings from the rule. (Public
Meeting Transcript (ECR), No. 12 at pp.
141–142; ECR, No. 15 at p. 3; Ice Air,
No. 25 at pp. 3–4; Public Meeting
Transcript (Goodman), No. 12 at p. 142)
AHRI and Carrier both agreed that
higher efficiency levels for PTHPs will
cause a shift to less efficient PTACs.
(AHRI, No. 23 at p. 8; Carrier, No. 16 at
p. 5)
In contrast, GE stated that the
probability of users shifting to other
product classes would be remote. GE
pointed out that the case for a heat
pump is compelling when the cost
differential is $50. In almost all cases,
the payback for choosing a heat pump
is less than 1 year. In most cases, GE
said, its customer base is composed of
astute business people who are
concerned about operating costs and
efficiencies. (Public Meeting Transcript,
No. 12 at pp. 145–146) AHRI questioned
GE’s assertion, given that the current
market is almost evenly split between
PTAC and PTHP equipment. (Public
Meeting Transcript, No. 12 at p. 144)
To address concerns about equipment
switching, DOE performed a sensitivity
analysis on the possible impact on
energy savings due to customers
switching from PTACs to PTHPs for a
case where a combined TSL resulted in
a higher cooling efficiency (EER) might
be set for PTHPs compared to PTACs of
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the same capacity. This sensitivity
analysis examined what fraction of the
future projected PTHP market would
need to switch from PTHPs to PTACs
with electric resistance heat to offset the
energy savings from increased efficiency
requirements for PTHPs relative to
PTACs at TSLs 2, 4, and A. It also
estimated the change in payback period
for purchasers of PTHP versus PTAC
equipment at the TSLs. DOE concluded
that based on this analysis the increase
in PTHP cost and the resulting change
in PBP for these TSLs were both small
and that it was unlikely that the savings
from higher PTHP standards under
these TSLs would be offset by customers
switching to PTAC equipment. Section
V.B. discusses the results of this
sensitivity analysis.
2. Base Case and Standards Case
Forecasted Distribution of Efficiencies
The annual energy consumption of a
PTAC or PTHP unit relates directly to
the efficiency of the unit. For the final
rule, DOE used the same methodology
that was used in the NOPR analysis to
develop base case and standards case
efficiency distributions for shipments.
DOE developed shipment-weighted
average equipment efficiency forecasts
that enabled a determination of the
shipment-weighted annual energy
consumption values for the base case
and each TSL analyzed by equipment
class. DOE developed shipment
estimates by converting the 2005 PTAC
and PTHP equipment shipments by
equipment class into market shares by
equipment class. DOE then adapted a
cost-based method used in the NEMS to
estimate market shares for each
equipment class by TSL. DOE used
those market shares and projections of
shipments by equipment class to
determine future equipment efficiency
forecasts both for a base case scenario
and standards case scenarios. The
difference in equipment efficiency
between the base case and standards
cases was the basis for determining the
reduction in per-unit annual energy
consumption that could result from
amended energy conservation
standards. Although the methodology
DOE used was identical to that in the
NOPR, differences in equipment price
and annual energy consumption
established in the LCC analysis resulted
in slight shifts in the estimated
shipments by efficiency level.
For each standards case, DOE
assumed that shipments at efficiencies
below the projected minimum standard
levels were most likely to roll up to
those efficiency levels in response to an
increase in energy conservation
standards. The market shares for
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equipment at higher efficiency levels
were assumed not to be affected as the
market already has a choice of that
equipment. DOE, thus, assumed that the
new standard would not affect the
relative attractiveness of equipment
with efficiencies higher than the
standard. For further discussion, see
Chapter 11 of the TSD.
G. Manufacturer Impact Analysis
In determining whether a standard for
a covered product is economically
justified, the Secretary of Energy 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)) EPCA also
requires for an assessment of the impact
of any lessening of competition as
determined by the Attorney General. (42
U.S.C. 6295(o)(2)(B)(i)(V)) DOE
performed the MIA to estimate the
financial impact of energy conservation
standards on the standard size and nonstandard size PTAC and PTHP
industries, and to assess the impact of
such standards on employment and
manufacturing capacity. DOE published
the results in the NOPR. 73 FR 18883–
87, 18893–99. For this final rule, while
DOE did not introduce changes to the
methodology described in the NOPR, it
updated the R–410A-shipment forecast
distribution of shipments based on the
updated NIA results. (See TSD Chapter
13.) In response to DOE’s NOPR
presentation, interested parties provided
comments on the cumulative regulatory
burden, small business impacts, and
employment.
1. GRIM Input Updates
The GRIM inputs consists of
information regarding the standard size
and non-standard size PTAC and PTHP
industries’ cost structure, shipments,
and revenues. This includes information
from many of the analyses described
above, such as manufacturing costs and
prices from the engineering analysis and
shipments forecasts. In response to the
presentation of the MIA analysis in the
NOPR, DOE revised several key inputs
to the GRIM based on more recent
sources of data for both standard and
non-standard size PTAC and PTHP
industries.
a. Manufacturing Production Costs
The GRIM uses cost-efficiency curves
derived in the engineering analysis to
calculate the MPCs for each equipment
class at each TSL. By multiplying
different sets of markups with the
MPCs, DOE derives the manufacturing
selling prices (MSP) used to calculate
industry revenues. For this final rule,
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conservation standards. See Chapter 13
of the TSD for additional details of the
markup scenarios.
b. Shipments and Distributions of
Efficiencies in the Base Case
The GRIM estimates manufacturer
revenues based on total-unit-shipment
forecasts and the distribution of these
values by EER. Changes in the efficiency
mix at each standard level are a key
driver of manufacturer finances. For the
final rule analysis, DOE used only the
NES shipments forecasts and the
distribution of efficiencies in the base
case for both standard size and nonstandard size PTACs and PTHPs from
2007 to 2042. DOE continued to allocate
the closest representative cooling
capacity, within the appropriate
equipment class, to any shipments
forecasted by the NES of equipment that
was not within one of the representative
cooling capacities. For example, the
total PTAC or PTHP shipments with a
cooling capacity less than 10,000 Btu/h
for standard size equipment are
included with the 9,000 Btu/h
representative cooling capacity. (See
Chapter 13 of the final rule TSD.)
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DOE used the MPCs from the final rule
engineering analysis as described in
Chapter 5 of the TSD.
d. Capital and Equipment Conversion
Expenses
Energy conservation standards
typically cause manufacturers to incur
one-time conversion costs to bring their
production facilities and equipment
designs into compliance with the
amended standards. For the purpose of
the MIA, DOE classified these one-time
conversion costs into two major groups:
equipment conversion and capital
conversion costs. Equipment conversion
expenses are one-time investments in
research, development, testing, and
marketing that are focused on making
equipment designs comply with the
new energy conservation standard.
Capital conversion expenditures are
one-time investments in property, plant,
and equipment to adapt or change
existing production facilities so that
new equipment designs can be
fabricated and assembled.
For this final rule, DOE used the same
capital expenses as presented in the
NOPR calculated in 2007$ for both
standard and non-standard size PTAC
and PTHP industries. For equipment
conversion expenses for the standard
size PTAC and PTHP industry, DOE also
used the same product expenses as
presented in the NOPR calculated in
2007$. For equipment conversion
expenses for the non-standard size
PTAC and PTHP industry, DOE revised
figures based on comments from
interested parties on the NOPR. For
more information on DOE’s revision to
the equipment conversion expenses for
the non-standard size PTAC and PTHP
industry, see section V.C. and Chapter
13 of the TSD.
c. R–410A Base Case and Amended
Energy Conservation Standards Markup
Scenarios
The PTAC and PTHP manufacturer
impact analysis is explicitly structured
to account for the cumulative burden of
sequential refrigerant and amended
energy conservation standards. In the
NOPR, DOE described the two markup
scenarios used to calculate the base case
INPV after implementation of the R–22
refrigerant phaseout, and the standards
case INPV at each TSL. (See Chapter 13
of the NOPR TSD.) For the final rule,
DOE continued to analyze two distinct
R–410A base case and amended energy
conservation standards markup
scenarios: (1) The flat markup scenario,
and (2) the partial cost recovery markup
scenario. Under the flat markup
scenario, DOE applied a single uniform
‘‘gross margin percentage’’ markup
across all TSLs that DOE believes
represents the current markup for
manufacturers in the standard and nonstandard size PTAC and PTHP
industries. The ‘‘partial cost recovery’’
scenario implicitly assumes that the
industries can pass-through only part of
their regulatory-driven increases in
production costs to consumers in the
form of higher prices. As presented in
the NOPR, these markup scenarios
characterize the markup conditions
described by manufacturers, and reflect
the range of market responses
manufacturers expect as a result of the
R–22 phaseout and the amended energy
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2. Cumulative Regulatory Burden
As discussed in the NOPR, one aspect
of manufacturer burden is the
cumulative impact of multiple DOE
standards and other regulatory actions
that affect the manufacture of the same
covered equipment. All PTAC and
PTHP manufacturers believe that the
EPA-mandated refrigerant phaseout will
be the largest external burden on PTAC
and PTHP manufacturers. DOE
addressed the cumulative regulatory
burden affecting manufacturers of
PTACs and PTHPs as a result of the
refrigerant phaseout by first examining
impacts on INPV arising from
converting R–22 to R–410A equipment
production. DOE then examined the
possible impacts of amended energy
conservation standards on the R–410A
base case. Thus, DOE examined the
cumulative impacts of both R–410A
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conversion and compliance with the
proposed energy conservation
standards. (See Chapter 13 of the TSD.)
73 FR 18897–98.
In response to DOE’s NOPR, ECR
stated that manufacturers are forced to
consider both the refrigerant phaseout
and energy conservation standard levels
due to the timing of the regulations.
According to ECR, it is difficult to work
on designs using R–410A knowing that
the 2012 efficiency levels are not final
and the efficiency levels proposed in the
NOPR may change. (Public Meeting
Transcript, No. 12 at pp. 63–64)
Similarly, Ice Air stated its concern
about the cumulative regulatory burden
placed on manufacturers by the
refrigerant phaseout and the amended
energy conservation standards. Ice Air
warned that the burdens to comply with
both of these regulatory actions could
cause manufacturers of non-standard
size equipment to go out of business and
could also severely affect the standard
size industry. (Ice Air, No. 25 at p. 2)
To assess the impacts on INPV due to
both refrigerant phaseout and energy
conservation standards, DOE first
examined the changes in industry cash
flows from 2007 to 2010 using only
equipment with R–22 refrigerant (i.e.,
before the refrigerant phaseout). DOE
then examined the changes in industry
cash flows from 2010 through 2042
using only equipment with R–410A
refrigerant (i.e., after the refrigerant
phaseout). The sum of the cash flows
discounted to the current year equates
to the INPV used to quantify the impacts
on the industries. DOE included
equipment prices using both R–22 and
R–410A refrigerant estimated in the
engineering analysis and equipment
conversion and capital conversion
expenses related to both energy
conservation standards and refrigerant
phaseout in its manufacturer impact
analysis. Investment estimates used in
the analysis can be found in the NOPR,
73 FR 18893–96, and in Chapter 13 of
the TSD. Although investments needed
to meet the proposed energy
conservation standards and refrigerant
phaseout requirements could vary
among manufacturers, the values DOE
used in its analysis are an aggregate of
information manufacturers provided.
Given these variations in investment
within the industry, DOE believes that
the MIA captures the potential range of
costs, investments, and impacts on
manufacturers due to both energy
conservation standards and the
refrigerant phaseout.
AHRI commented that DOE did not
account for the costs to phase out
HCFCs from other air-conditioning
equipment or to comply with other
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energy conservation standards produced
by PTAC and PTHP manufacturers.
(AHRI, No. 23 at p. 5)
For the NOPR, DOE examined other
Federal regulations that could affect
manufacturers of standard and nonstandard size PTACs and PTHPs.
Chapter 13 of the TSD presents DOE’s
findings. 73 FR 18897–98. These
findings generally indicated that the
refrigerant phaseout is the most
significant other Federal regulation
impending in the industry at this time.
For this final rule, DOE also identified
the other DOE regulations standard size
and non-standard size PTAC and PTHP
manufacturers are facing for other
equipment they manufacture within
three prior and three years after the
effective date of the amended energy
conservation standards for PTACs and
PTHPs. DOE identified the costs of
additional regulations when these
estimates were available from other DOE
rulemakings. Chapter 13 of the TSD
presents additional information
regarding the cumulative regulatory
burden analysis.
3. Employment Impacts
In response to DOE’s presentation of
the direct employment impacts
characterized in the MIA and presented
in the NOPR TSD, EarthJustice
commented that DOE’s projection of
employment impacts of standards on
the regulated industry demonstrates an
economic benefit in the form of
increased employment on a global scale.
Specifically, EarthJustice comments that
the benefits from an increase in
employment would be principally to
other countries and that DOE does not
take this into consideration in its
analysis. (EarthJustice, No. 22 at p. 5)
DOE believes EarthJustice’s assertion
that DOE only considered the direct
employment impacts on international
manufacturers is incorrect. DOE
calculated the total labor expenditures
for the industry using the unit labor
costs from the engineering analysis and
the total industry shipments from the
NES. DOE translated the total labor
expenditures for the industry to the total
number of jobs using the average labor
rate for the industry and the annual
worker hours. Finally, DOE multiplied
the total number of jobs by the domestic
market share to derive the domestic
number of jobs for the base case and
each TSL. The direct employment
results characterized by the MIA
represent U.S. production workers are
impacted by this rulemaking in the
standard and non-standard size PTAC
and PTHP manufacturing industries.
See section V.C.2 for the results of the
direct employment impact analysis.
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Accordingly, DOE has considered all
employment impacts in weighing the
benefits and the burdens, including
direct (as calculated by the MIA) and
indirect (as calculated by the
employment impact analysis).
In response to the increase in direct
employment characterized by the MIA,
ECR, a domestic manufacturer of nonstandard size equipment, and McQuay,
a domestic manufacturer of both
standard and non-standard size
equipment, commented that the
adoption of the proposed amended
energy conservation standards would
have adverse impacts on employment
and their businesses. Specifically, ECR
commented that adopting TSL 4 from
the NOPR might have an adverse impact
on employment and customers in New
York, where a large volume of
equipment is produced and shipped.
(ECR, No. 15 at p. 3; see also Public
Meeting Transcript, No. 12 at p. 184)
Similarly, McQuay stated that unlike
the standard size equipment that is built
overseas, the non-standard size
equipment is unique because it is
developed, manufactured, and
supported by domestic facilities mainly
located in the state of New York. Any
impacts on its non-standard size
equipment business would have an
economic impact on McQuay. (Public
Meeting Transcript, No. 12 at p. 184)
DOE calculated the potential impacts
of amended energy conservation
standards on domestic production
employment for the non-standard
industry by bounding the range of
potential impacts. For the upper bound,
the direct employment impact analysis
conducted as part of the MIA estimates
the number of U.S. production workers
who are impacted by this rulemaking in
the non-standard size PTAC and PTHP
manufacturing industries, assuming that
shipment levels and product availability
remain at current levels. In this best
case scenario, where shipments do not
decrease and higher efficiency products
require more labor, the direct
employment impact analysis shows a
net increase in the number of domestic
jobs for the non-standard size
industries. It is reasonable to assume
that shipments and product availability
will continue because consumers will
continue to demand non-standard
PTACs and PTHPs for their replacement
needs. For these customers,
modifications to their buildings to
accommodate standard size PTACs and
PTHPs is a large cost they will try to
prevent. However, at higher standard
levels, the product development costs
are prohibitive for the small domestic
manufacturers that produce PTACs and
PTHPs. These domestic manufacturers
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may exit the industry rather than invest
in new designs. This would result in a
loss of domestic employment at these
firms. The unmet demand could be
satisfied by new domestic
manufacturers or foreign manufacturers.
To calculate the lower bound of the
range of potential impacts, DOE
developed a scenario where either
shipments drop or manufacturers
respond to higher labor requirements by
shifting production to lower-labor-cost
countries. For the non-standard
industry, DOE believes this scenario is
a possibility because DOE noticed that
the non-standard market currently offers
over approximately 40 different
equipment platforms, many of which
are built in very low volumes. As a
result, the non-standard market will
incur a much higher impact due to fixed
costs on a per unit basis. Since the nonstandard PTAC and PTHP industry is
composed chiefly of small businesses,
any energy conservation standard for
non-standard PTACs and PTHPs will
impact mostly small businesses, which
might choose to exit this industry rather
than invest the necessary resources to
convert existing equipment lines.
Alternatively, manufacturers could
choose to move their manufacturing
facilities overseas as a method of
reducing costs. Consequently, DOE
assumed that the greater labor
requirements displace all U.S.
production workers in the non-standard
industry and used this condition as a
lower bound to the potential impacts of
standards on domestic production
employment.
H. Employment Impact Analysis
When developing a standard for
adoption, DOE considers its
employment impact. Direct employment
impacts are any changes in the number
of employees for PTAC and PTHP
manufacturers, their suppliers, and
related service firms. Indirect 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 PTAC and PTHP
equipment. The MIA in this rulemaking
addresses the employment impacts on
manufacturers of PTACs and PTHPs
(i.e., the direct employment impacts)
(Chapter 13 of the TSD). This section
describes other, primarily indirect,
employment impacts.
Indirect employment impacts from
PTAC and PTHP standards consist of
the net jobs created or eliminated in the
national economy, other than in the
manufacturing sector being regulated, as
a consequence of (1) reduced spending
by end users on energy (electricity,
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gas—including liquefied petroleum
gas—and oil); (2) reduced spending on
new energy supply by the utility
industry; (3) increased spending on the
purchase price of new PTACs and
PTHPs; 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.
DOE estimated indirect national
employment impacts using an input/
output model of the U.S. economy
called Impact of Sector Energy
Technologies (ImSET). Developed by
DOE’s Building Technologies Program,
the ImSET model estimates changes in
employment, industry output, and wage
income in the overall U.S. economy
resulting from changes in expenditures
in the various sectors of the economy.
DOE estimated changes in expenditures
using the NES spreadsheet. ImSET then
estimated the net national indirect
employment impacts of potential PTAC
and PTHP equipment efficiency
standards on employment by sector.
DOE received no comments on the
employment analysis during the NOPR,
so it made no changes to the analysis
and methodology in the final rule.
The ImSET input/output model
suggests that the amended PTAC and
PTHP efficiency standards could
increase the net demand for labor in the
economy as the net monetary savings
from standards are redirected to other
forms of economic activity. The gains
would most likely be small relative to
total national employment, primarily
due to the small net monetary savings
from amended PTAC and PTHP energy
conservation standards available for
transfer to other sectors, relative to the
economy as a whole. Chapter 15 of the
TSD provides more details on the
employment impact analysis.
I. Utility Impact Analysis
The utility impact analysis estimates
the effects of reduced energy
consumption due to improved
equipment efficiency on the utility
industry. This utility analysis consists
of a comparison between forecast results
for a case comparable to the AEO2008
Reference Case and forecasts for policy
cases incorporating each of the PTAC
and PTHP TSLs.
DOE analyzed the effects of amended
standards on electric utility industry
generation capacity and fuel
consumption using a variant of the
EIA’s NEMS. NEMS, which is available
in the public domain, is a large,
multisectoral, partial-equilibrium model
of the U.S. energy sector. EIA uses
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NEMS to produce its AEO, a widely
recognized baseline energy forecast for
the United States. DOE used a variant of
NEMS, referred to as NEMS–BT, to
clarify that NEMS has been modified to
take into account the energy savings
from standards for PTAC and PTHP at
different TSL levels.
DOE conducted the utility analysis as
policy deviations from the AEO2008,
applying the same basic set of
assumptions. The NEMS–BT is run
similarly to the AEO2008 NEMS, except
that PTAC and PTHP energy usage is
reduced by the amount of energy (by
fuel type) saved due to the TSLs. DOE
obtained the inputs of national energy
savings from the NES spreadsheet
model. Using these inputs, the utility
analysis reported the changes in
installed capacity and generation (by
fuel type) that result for each TSL, as
well as changes in end-use electricity
sales. Aside from the use of the
AEO2008, DOE made no other changes
to the methodology used for the utility
impact analysis from the NOPR. Chapter
14 of the TSD provides details of the
utility analysis methods and results.
J. Environmental Analysis
DOE has prepared a draft
environmental assessment (EA)
pursuant to the National Environmental
Policy Act and the requirements under
42 U.S.C. 6295(o)(2)(B)(i)(VI) and
6316(a), to determine the environmental
impacts of the amended standards.
Specifically, DOE estimated the
reduction in total emissions of carbon
dioxide (CO2) using the NEMS–BT
computer model. DOE calculated a
range of estimates for reduction in NOX
emissions and Hg emissions using
current power sector emission rates.
However, the Environmental
Assessment (see Chapter 16 of the FR
TSD accompanying this notice) does not
include the estimated reduction in
power sector impacts of sulfur dioxide
(SO2), because DOE has determined that
due to the presence of national caps on
SO2 emissions as addressed below, any
such reduction resulting from an energy
conservation standard would not affect
the overall level of SO2 emissions in the
United States.
The NEMS–BT is run similarly to the
AEO2008 NEMS, except the energy use
is reduced by the amount of energy
saved due to the TSLs. DOE obtained
the inputs of national energy savings
from the NIA spreadsheet model. For
the Environmental Assessment, the
output is the forecasted physical
emissions. The net benefit of the
standard is the difference between
emissions estimated by NEMS–BT and
the AEO2008 Reference Case. The
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NEMS–BT tracks CO2 emissions using a
detailed module that provides results
with a broad coverage of all sectors and
inclusion of interactive effects.
The Clean Air Act Amendments of
1990 set an emissions cap on SO2 all
power generation. The attainment of
this target, however, is flexible among
generators and is enforced through the
use of emissions allowances and
tradable permits. Because SO2 emissions
allowances have value, they will almost
certainly be used by generators,
although not necessarily immediately or
in the same year with and without a
standard in place. In other words, with
or without a standard, total cumulative
SO2 emissions will always be at or near
the ceiling, while there may be some
timing differences between year-by-year
forecasts. Thus, it is unlikely that there
will be an SO2 environmental benefit
from electricity savings as long as there
is enforcement of the emissions ceilings.
Although there may not be an actual
reduction in SO2 emissions from
electricity savings, there still may be an
economic benefit from reduced demand
for SO2 emission allowances. Electricity
savings decrease the generation of SO2
emissions from power production,
which can decrease the need to
purchase or generate SO2 emissions
allowance credits, and decrease the
costs of complying with regulatory caps
on emissions.
Like SO2, future emissions of NOX
and Hg would have been subject to
emissions caps under the Clean Air
Interstate Act (CAIR) and Clean Air
Mercury Rule (CAMR). As discussed
later in section V.C.6, these rules have
been vacated by a Federal court. But the
NEMS–BT model used for today’s final
rule assumed that both NOX and Hg
emissions would be subject to CAIR and
CAMR emissions caps. In the case of
NOX emissions, CAIR would have
permanently capped emissions in 28
eastern States and the District of
Columbia. Because the NEMS–BT
modeling assumed NOX emissions
would be subject to CAIR, DOE
established a range of NOX reductions
based on the use of a NOX low and high
emissions rates (in metric kilotons (kt)
of NOX emitted per terawatt-hours
(TWh) of electricity generated) derived
from the AEO2008. To estimate the
reduction in NOX emissions, DOE
multiplied these emission rates by the
reduction in electricity generation due
to the standards considered. For
mercury, because the emissions caps
specified by CAMR would have applied
to the entire country, DOE was unable
to use NEMS–BT model to estimate the
physical quantity changes in mercury
emissions due to energy conservation
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standards. To estimate mercury
emission reductions due to standards,
DOE used an Hg emission rate (in metric
tons of Hg per energy produced) based
on AEO2008. Because virtually all
mercury emitted from electricity
generation is from coal-fired power
plants, DOE based the emission rate on
the metric tons of mercury emitted per
TWh of coal-generated electricity. To
estimate the reduction in mercury
emissions, DOE multiplied the emission
rate by the reduction in coal-generated
electricity associated with standards
considered.
In comments on the NOPR, NRDC
asked if the monetization of carbon
should have been included in the LCC
and the NPV analyses and questioned
DOE’s selection of the $0 to $14 range
for carbon prices in the NOPR analysis.
The group recommended that DOE use
new cost figures for monetizing carbon
from the new EIA report. (Public
Meeting Transcript No. 12 at pp. 110–
111, 192–194) AHRI by contrast
commented that DOE is acting
appropriately by not speculating on
carbon emission pricing. (AHRI, No. 23
at p. 9) EarthJustice stated that EPCA
mandates that DOE consider the need
for national energy conservation and
determine whether a standard is
‘‘economically justified’’ require DOE to
factor economic benefits that are shared
by the nation as a whole, not just those
benefits that accrue to PTAC and PTHP
customers. EarthJustice commented that
in the case of SO2 emissions and NOX
emissions in states covered by the Clean
Air Interstate Rule (CAIR)15, DOE
should monetize the values of total
change in the value of the allowance
credits for these emissions and
incorporate this amount into the NPV
analysis. In the case of CO2, NOX in
non-CAIR states, and Hg, EarthJustice
stated that DOE must consider the value
of the environmental benefit resulting
from reduced emissions of these
pollutants in the NPV analysis. Finally,
EarthJustice questioned the range of
valuations for CO2 emissions used in the
NOPR, pointing out that the high end
valuation used by DOE was consistent
with the average value from the IPCC
source cited by DOE. (EarthJustice, No.
22 at pp. 4–5)
DOE has made several additions to its
monetization of environmental
emissions reductions in today’s rule,
which are discussed in Section V.C.6,
but has chosen to continue to report
these benefits separately from the net
benefits of energy savings. Nothing in
EPCA, nor in the National
Environmental Policy Act, requires that
15 See
https://www.epa.gov/cleanairinterstaterule/.
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the economic value of emissions
reduction be incorporated in the net
present value analysis of the value of
energy savings. Unlike energy savings,
the economic value of emissions
reduction is not priced in the
marketplace.
SO2 emissions, which, as discussed
previously are not impacted by this
rulemaking, have markets for emissions
allowances. The market clearing price of
SO2 emissions is roughly the marginal
cost of meeting the regulatory cap, not
the marginal value of the cap itself.
Further, because SO2 (for the nation) is
regulated by a cap and trade system, the
effect of the need to meet these caps is
already included in the price of energy
or energy savings. With a cap on SO2,
the value of energy savings already
includes the value of SO2 control for
those consumers experiencing energy
savings. The economic cost savings
associated with SO2 emissions caps is
approximately equal to the change in
the price of traded allowances resulting
from energy savings multiplied by the
number of allowances that would be
issued each year. That calculation is
uncertain because the energy savings for
PTAC and PTHP equipment are so small
relative to the entire electricity
generation market that the resulting
emissions savings would have almost no
impact on price formation in the
allowances market and likely would be
outweighed by uncertainties in the
marginal costs of compliance with the
SO2 emissions caps.
For those emissions currently not
priced (CO2, Hg, and NOX), only a range
of estimated economic values based on
environmental damage studies of
varying quality and applicability is
available. Consequently, DOE is
reporting and weighing these values
separately and is not including them in
the NPV analysis.
K. Other Comments
1. Burdens on Small, Non-Standard Size
PTAC and PTHP Manufacturers
In the MIA conducted for the NOPR,
DOE determined the impacts on the
non-standard size PTAC and PTHP
industry separately from the standard
size PTAC and PTHP industry due to
their differences in equipment classes,
shipment volumes, and equipment
prices. DOE took into consideration the
size, location, and specialization of the
non-standard size PTAC and PTHP
industry when calculating production
costs (see Chapter 5 of the NOPR TSD)
and capital and equipment conversion
expenses (see Chapter 13 of the NOPR
TSD) required to meet the proposed
amended energy conservation
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58797
standards. Due to the limited number of
publicly owned manufacturers of nonstandard equipment (i.e., the majority of
non-standard equipment manufacturers
are privately held companies), DOE
relied on information provided by
manufacturers during interviews for the
NOPR MIA. DOE estimated the industry
research and development (R&D)
expenses needed to achieve each trial
standard level. Details of the R&D
expenses by equipment class are
presented in Chapter 13 of the NOPR
TSD. The TSD generally indicates that
these equipment conversion expenses
would be over 20 million dollars for the
non-standard size industry to transform
their equipment lines at TSL 1 and
higher TSLs. In addition, the NOPR
interviews suggested the kinds of
impacts imposed by amended energy
conservation standards on small
businesses would not largely differ from
impacts on larger companies within the
non-standard size equipment industry.
In response to the presentation of the
potential impacts on non-standard size
manufacturers that DOE described in
the NOPR, AHRI, Ice Air, and ECR each
provided comments and public
statements regarding this issue. AHRI
commented that the relative impacts on
non-standard size equipment
manufacturers are greater than the
impacts on standard size equipment
manufacturers. (AHRI, No. 23 at p. 5) Ice
Air commented that the non-standard
size PTAC and PTHP industry is
comprised of five or six smaller
businesses (mainly located in New York
State) that cannot afford to match the
R&D spending of large, multi-national
companies making standard PTACs and
PTHPs at much higher volumes. Ice Air,
being one of the smallest manufacturers,
stated that smaller companies would be
adversely impacted, with some
companies forced to go out of business.
Similarly, Ice Air stated that the
proposed standards could potentially
eliminate the ‘‘non-standard’’ segment
of the industry, including a significant
portion of its own product offerings of
non-standard size PTACs and PTHPs.
Ice Air also stated that the possible
elimination of non-standard size
equipment manufacturers may lead to a
lessening of the competition and limit
consumers’ choices to the offerings of
the larger size equipment
manufacturers. (Ice Air, No. 25 at p.
2–4) ECR commented that small
manufacturers of non-standard size
PTAC and PTHP equipment would be
negatively impacted at TSL 4 and that
this proposed standard could impact the
availability of products for its
customers, particularly in concentrated
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areas like New York City that have large
shipments of non-standard equipment.
(ECR, No. 15 at p. 3)
In response to comments from
interested parties, DOE further reviewed
the non-standard size PTAC and PTHP
industry, the data gathered during
manufacturing interviews, and
manufacturer literature to determine if
the amended energy conservation
standards would disproportionately
harm the small, non-standard
manufacturers.
a. Non-Standard PTAC and PTHP
Industry Characteristics
The non-standard PTAC and PTHP
equipment industry is characterized by
a wide scope of products being
manufactured at low production rates.
Most non-standard units are built-toorder and are commonly customized by
the manufacturer to accommodate
specific building requirements. DOE
review of the non-standard PTAC and
PTHP market suggests that the nonstandard PTAC and PTHP industry
supports nearly one hundred different
legacy models that were formerly made
under over 30 different brand names.
The six remaining manufacturers of
non-standard PTACs and PTHPs
manufacture approximately 40 different
replacement model platforms (as
determined by sleeve size and other
equipment design requirements to allow
them to be drop-in replacements) and
100 models between them in total. Most
non-standard units are built-to-order
and are commonly customized by the
manufacturer to accommodate specific
building requirements. The number of
equipment families offered by a
particular company ranges from seven
to 40 units, though customization
subsequently leads to thousands of
stock-keeping-units (SKUs).
The wide range of non-standard
sleeve sizes is the legacy of the early
PTAC and PTHP industry when over 30
competitors made these units to suit the
specific needs and different wall sleeve
dimensions. Industry consolidation has
reduced the number of competitors to
six, though the scope of non-standard
equipment for sale has not lessened
significantly. The number of equipment
platforms offered by any particular nonstandard PTAC and PTHP manufacturer
ranges from seven to 40 units, though
multiple capacities per equipment
platform and any customization options
subsequently generates thousands of
SKUs.
b. Non-Standard PTAC and PTHP
Market Review
DOE conducted a market review and
created a list of every manufacturer that
produces standard and non-standard
size PTACs and PTHPs for sale in the
United States using manufacturer
catalogs. During interviews and at the
public meeting, DOE asked interested
parties and industry representatives if
they were aware of any other nonstandard manufacturers. DOE reviewed
publicly available data such as Dun and
Bradstreet reports and contacted
manufacturers, where needed, to
determine whether they meet the SBA’s
definition of a small business in the
PTAC and PTHP industry. Table IV.4
lists the number of all manufacturers
that supply PTACs and PTHPs in
standard and/or non-standard sizes, as
well as the number of small businesses
in each category.
TABLE IV.4—PTAC AND PTHP MANUFACTURER CHARACTERISTICS
Total number of
manufacturers in
each market
segment
Market served
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Standard ......................................................................................................................................................
Non-Standard ...............................................................................................................................................
Both Standard and Non-Standard ...............................................................................................................
As Table IV.4 illustrates, there is a
greater proportion of small businesses
serving the non-standard market than
the standard market. The standard
market is characterized by high unit
volumes and a significant degree of
commoditization. The non-standard
market offers significantly more sleeve
sizes and/or equipment platforms to
choose from, most of which are made to
order for specific customers. The
discrepancy between unit shipments
and the number of platforms requiring
significant product development to meet
upcoming efficiency standards is the
main reason that the non-standard
PTAC and PTHP industry is expected to
experience a greater relative impact for
any given efficiency level than the
standard PTAC and PTHP industry.
DOE found that most small businesses
in the PTAC and PTHP industries focus
primarily on manufacturing customized
and/or non-standard equipment. For
example, standard size units offered by
manufacturers of both kinds of
equipment feature customization
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features such as hydronic coil heating
that differentiate them from common
standard PTAC and PTHPs made by
higher-volume competitors. According
to interviewees, the higher value that
customers associate with customized
and/or non-standard equipment allows
them to charge higher prices, which in
turn makes their (higher cost) lowvolume operations viable.
The much lower volumes and the
greater number of equipment platforms
distinguishes the standard from the nonstandard PTAC and PTHP market.
Whereas standard PTAC and PTHP
manufacturers only have to modify one
equipment platform to meet regulatory
standards, non-standard manufacturers
may have to update as many as 40
different equipment platforms in their
portfolio. Many equipment development
costs (such as testing, certification, etc.)
are somewhat fixed, making
manufacturing scale an important
consideration in determining whether
the equipment development
investments are economically justified.
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9
2
4
Total number of
small businesses
in each market
segment
1
2
3
Similarly, any capital expenditures,
such as upgrading manufacturing and
fabrication lines can be spread across
much higher unit volumes by highvolume manufacturers. Due to the
concentration of small businesses in the
non-standard PTAC and PTHP industry,
that particular industry segment is more
vulnerable to impacts from amended
energy conservation standards. For
further illustration of the economic
issues, please refer to the GRIM analysis
in Chapter 13 of the final rule TSD.
c. Impacts on Small Businesses in the
Non-Standard Size PTAC and PTHP
Industry
The phaseout of R–22 refrigerant use
in 2010 adds a two-fold fixed-cost
burden on all manufacturers: (1)
Equipment, manufacturing lines, and
fabrication centers have to be converted
to R–410A refrigerant use; and (2) all
equipment platforms will have to
undergo equipment development,
testing, and certification. Achieving
even baseline ASHRAE Standard 90.1–
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extensive redesign to achieve the
baseline standard level once
manufacturers switch from R–22 to
alternate refrigerants. Table IV.5
illustrates the various nominal EERs
that non-standard PTACs and PTHPs
have to achieve and what percentage of
the current models are projected to
achieve that level despite efficiency
losses due to a R–410A conversion. This
table also includes the equipment
1999 efficiency levels for all extant
products is likely to be beyond the reach
of some manufacturers since they lack
the scale to maintain engineering
departments with the time, equipment,
and budget to address multiple
equipment platform conversions.
DOE reviewed published efficiency
ratings for non-standard PTACs and
PTHPs to estimate the percentage of the
units on the market that would require
58799
conversion costs for standard PTAC and
PTHP units made by manufacturers that
build primarily non-standard equipment
because these units share more
characteristics with non-standard
equipment (such as very low production
volumes, extensive customization, etc.)
than with the mass-market standard
PTACs and PTHPs manufactured by
high-volume manufacturers.
TABLE IV.5—CUMULATIVE EQUIPMENT DEVELOPMENT COST ESTIMATES FOR THE NON-STANDARD SIZE PTAC AND PTHP
INDUSTRY
Equipment class
Baseline
Minimum EER for Non-Standard
PTACs ......................................
Minimum EER for Non-Standard
PTHPs ......................................
Percentage of Equipment Families to At or Above TSL Efficiency Levels ............................
Number of Equipment Families
Requiring Significant Equipment Development to Meet
Standards .................................
Aggregated Industry Burden * ......
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
8.6
9.4
9.4
9.7
9.4
10.0
8.5
9.4
9.7
9.7
10.0
10.0
73%
25%
29
7.25
23%
82
20.50
84
21.00
23%
13%
84
21.00
95
23.75
13%
95
23.75
pwalker on PROD1PC71 with RULES3
* Millions of dollars.
As noted in Table IV.5, DOE
identified six manufacturers of nonstandard PTACs and PTHPs. DOE
grouped equipment offered by
manufacturers into platforms, reflecting
how some equipment chassis’ are sold
with minimal modifications under
different product names. Altogether,
these six non-standard manufacturers
offer over 100 different PTAC and PTHP
equipment model families for sale,
which represent approximately 40
different equipment platforms. In
determining whether equipment
platforms would be likely to require
significant equipment development,
DOE’s estimates accounted for
published EERs for equipment
platforms, equipment capacity, and
anticipated degradation factors as a
result of adopting R–410A refrigerants.
DOE took published EER ratings and
degraded them according to factors from
the engineering analysis. If one or more
capacities within an equipment
platform fell below the EER levels
prescribed by a TSL (either for PTACs
or PTHPs), then the equipment platform
was marked for redesign. Accordingly,
non-standard platforms that currently
claim very high EERs are not expected
to require extensive redesign except at
very high TSLs.
During interviews with
manufacturers, none of the nonstandard PTAC and PTHP
manufacturers were able to give
estimates for their total equipment
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conversion costs by efficiency level. As
a result, DOE estimated the investment
requirements to upgrade an existing
equipment platform for optimal R–410A
operation on the basis of its more
numerous standard size manufacturer
responses and its own estimates.
Even in a best-case scenario ($0.25
million per equipment platform,
regardless of efficiency level, based on
feedback from engineering interview),
the non-standard PTAC and PTHP
industry would have great difficulty
meeting any standards level above
baseline. As Table IV.5 illustrates, the
industry burden to upgrade its
equipment families to meet TSL 1
would exceed $20 million or
approximately 40 percent of its total
annual revenue. Higher TSL levels
would impose even greater economic
burdens. However unsustainable this
impact is in the aggregate, the impact on
individual businesses could be even
greater.
For example, based on Dun &
Bradstreet reports, one small
manufacturer of non-standard PTACs
and PTHPs is estimated to have sales of
less than $5 million per year and
currently ships approximately 12
different non-standard equipment
platforms. DOE estimates that the
company would have to spend
approximately $3 million to meet any
efficiency level (including baseline)
using R–410A refrigerants. A $3 million
equipment development expense
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translates into more than 60 percent of
annual revenues or about 35 years worth
of equipment development budget for
this manufacturer, assuming it spends
the industry average of 1.6 percent of
revenues on research and development.
DOE estimates that on average, small
manufacturers of non-standard PTACs
and PTHPs require 25 years worth of
equipment development budget to reach
any efficiency level above baseline
(which in itself will require about 14
years worth of equipment development
budget). Because small businesses lack
the scale to afford the required
investments for R–410A conversion,
certification requirements, and the
equipment development required for
energy conservation standards, adopting
an efficiency standard above baseline is
likely to cause some small businesses to
exit the market. This situation suggests
that the non-standard industry would
reduce the number of equipment
families and capacities even at baseline
efficiency levels to keep equipment
development expenses within
manageable limits.
Table IV.6 describes DOE estimates
regarding the average equipment
development cost per unit by
manufacturing scale and equipment
lifetime. Manufacturing scale was
roughly defined as small vs. large
businesses whereas equipment lifetime
defines the number of years that a
specific equipment platform will stay in
production without major changes or
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
revisions. In the standard PTAC and
PTHP industry, the impact on the major
manufacturers is relatively minor,
regardless of whether they are small
businesses or not, due to the scale at
which they manufacture and because
they only have one equipment platform
to upgrade. However, in the nonstandard industry the impact of scale
and the number of equipment platforms
is quite evident. The only large business
operating in the non-standard industry
segment offers fewer equipment
platforms than any of its small business
competitors, yet operates at a higher
overall production volume than most of
them. As a result, the per-unit
conversion costs for the large business
are significantly lower than those of its
smaller competitors.
TABLE IV.6—IMPACT OF MANUFACTURING SCALE ON PER UNIT EQUIPMENT DEVELOPMENT COST
Per unit equipment development cost by industry segment versus
equipment lifetime (years)
Standard PTAC and PTHP ...............
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Non-Standard PTAC and PTHP .......
Small Business .................................
Large Business Average ..................
Small Business Average ..................
Large Business ................................
The current wide scope of equipment
families offered by the non-standard
industry (over 100 equipment families
from six manufacturers with thousands
of SKUs) is thus likely to shrink
dramatically in response to amended
energy conservation standards by DOE.
In particular, higher capacity units will
be vulnerable for elimination since
cabinet constraints may make required
improvements to units infeasible to
implement. Equipment manufacturers
would be expected to cut their least
popular equipment classes first,
potentially eliminating multiple extant
equipment platforms from the market
altogether. However, cutting equipment
classes by itself is difficult, since every
equipment class (and its resultant
enhancement and diversification of the
revenue stream) adds some necessary
manufacturing scale to the
manufacturer. Once enough equipment
classes are removed from its equipment
offering, the manufacturer may lack the
scale to operate.
A likely result of these market
dynamics is that some manufacturers of
non-standard PTACs and PTHPs will
exit the market or consolidate with
other small business manufacturers to
meet even baseline efficiency
requirements. At least in the initial
years after the implementation date of
the energy conservation standard, DOE
estimates that most non-standard PTAC
and PTHP equipment manufacturers
will reduce their scope of equipment
platforms by 50 percent or more in order
to bring the required equipment
development expenses down to more
sustainable levels, which will be likely
to affect consumer choices in the near
term.
Whereas current equipment buyers
benefit from being able to source nonstandard equipment families from
multiple manufacturers, the number of
manufacturers for a specific type of nonstandard PTAC or PTHP is likely to
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$6
7
136
45
shrink as manufacturers cut back the
equipment families they offer as a result
of the R–410A conversion, certification
requirements, and efficiency standards.
Limited monopolistic or oligopolistic
market conditions may result—limited
only because consumers always have
the option of modifying their building to
allow the use of alternative cooling and
heating equipment. Manufacturers also
expect consumers to prolong the life of
existing units via repairs and
remanufacturing—and reduce demand
for replacement units—if compliance
with energy conservation standards
results in higher replacement costs or
the complete unavailability of
replacement units.
2. PTAC and PTHP Labeling
In the NOPR, DOE stated that it
believes that a label on PTAC and PTHP
equipment that identifies the equipment
class would be useful in enforcing both
the energy conservation standards as
well as the building codes and would
assist States and other interested parties
in determining which application
correlates to a given PTAC or PTHP
(based upon size). DOE invited public
comment on the type of information and
other requirements or factors, including
format, it should consider in developing
a proposed labeling rule for PTACs and
PTHPs.
AHRI commented that it continues to
support the ASHRAE Standard 90.1–
1999 labeling requirements and believes
that a label on the equipment
identifying the equipment class would
be useful. AHRI stated that it does not
support a label similar to the
EnergyGuide label used on consumer
products and that such a label will do
nothing to help commercial customers
in making purchasing decisions. It
asserted that product literature such as
fact sheets and the AHRI Certified
Directory are more effective in
providing customers with energy
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10
$4
5
97
32
20
$3
3
68
22
$1
2
34
11
efficiency information they need before
purchasing PTACs and PTHPs. (AHRI,
No. 23 at p. 7)
Carrier stated that the inclusion of an
energy use information label for
customers of PTAC and PTHP
equipment would have little or no value
since the purchasing entity will rely on
the advice of the contractor or literature,
not on ‘‘labels’’. The nameplates also
provide an avenue for the performance
information as necessary to confirm that
they received what was requested.
(Carrier, No. 16 at p. 6)
ACEEE and NRDC also commented
that with regard to non-standard
equipment, the path to a loophole-free
standard requires adoption of labeling,
code, and/or equivalent measures to
prevent installation of non-standard
PTAC and PTHP equipment in new
construction. (ACEEE and NRDC, No. 26
at p. 3)
In developing the final rule, DOE
considered the information identified by
interested parties on the types of energy
use or efficiency information
commercial customers and owners of
PTACs and PTHPs would find useful in
making purchasing decisions. Before
DOE can establish labeling rules, it must
first ascertain whether the criteria
outlined in the NOPR are met. 73 FR
18888–89. DOE will work with the
Federal Trade Commission and other
interested parties to determine the types
of information and the forms (e.g.,
labels, fact sheets, or directories) that
would be most useful for commercial
customers and owners of PTACs and
PTHPs. DOE continues to believe that a
label on PTAC and PTHP equipment
identifying the equipment class and
efficiency level would be useful for
enforcement of both the energy
conservation standards as well as the
building codes and would assist States
and other interested parties in
determining which application
correlates to a given PTAC or PTHP
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(based upon size) because it would help
commercial customers identify the
efficiency associated with the PTAC and
PTHP equipment being placed into
commercial buildings. As DOE stated in
the NOPR, DOE anticipates proposing
labeling requirements for PTAC and
PTHP equipment in a separate
rulemaking and is not incorporating a
labeling requirement as part of today’s
final rule. 73 FR 18889.
V. Analytical Results and Conclusions
A. Trial Standard Levels
In the NOPR, DOE examined seven
TSLs for standard size and non-standard
58801
today’s final rule. TSL A combines the
efficiency levels in TSL 3 and TSL 1 for
standard size PTACs at the
representative cooling capacities and
the efficiency levels in TSL 5 and TSL
3 for standard size PTHPs at the
representative cooling capacities. DOE’s
inclusion of TSL A recognizes the
challenge manufacturers encounter
when increasing the efficiency of larger
cooling capacity equipment. Table V.1
presents the TSLs analyzed for standard
size PTACs and PTHPs in today’s final
rule and the efficiency levels within
each TSL for each class and size of
equipment analyzed.
size PTACs and PTHPs at the
representative cooling capacities. 73 FR
18889. Each TSL represented a set of
efficiency levels that describe a possible
amended energy conservation standard
for each equipment class. For the final
rule, DOE did not consider TSL 7 for
standard size equipment (see section
IV.C) because DOE determined that TSL
7 represented an efficiency level that
potentially could not be attained in the
full range of cooling capacities for
standard size equipment utilizing R–
410A. In addition, DOE analyzed a new
TSL for standard size PTACs and
PTHPs—TSL A—which is adopted in
TABLE V.1—STANDARD SIZE PTACS AND PTHPS BASELINE EFFICIENCY LEVELS AND TSLS
Equipment class (cooling capacity)
Standard Size PTAC, 9,000 Btu/h ....
Standard Size PTAC, 12,000 Btu/h ..
Standard Size PTHP, 9,000 Btu/h ....
Standard Size PTHP, 12,000 Btu/h ..
Efficiency metric
EER
EER
EER
COP
EER
COP
Baseline
(ASHRAE
standard
90.1–1999)
TSL 1
TSL 2
TSL 3
TSL A
TSL 4
TSL 5
TSL 6
(Max-Tech)
10.6
9.9
10.4
3.0
9.7
2.9
10.9
10.2
10.9
3.1
10.2
3.0
10.9
10.2
11.1
3.2
10.4
3.1
11.1
10.4
11.1
3.2
10.4
3.1
11.1
10.2
11.3
3.3
10.4
3.1
10.9
10.2
11.3
3.3
10.6
3.1
11.3
10.6
11.3
3.3
10.6
3.1
11.5
10.8
11.5
3.3
10.8
3.1
..................
..................
..................
..................
..................
..................
Table V.2 presents the TSLs analyzed
for non-standard size PTACs and PTHPs
in today’s final rule and the efficiency
levels within each TSL for each class
and size of equipment analyzed.
TABLE V.2—NON-STANDARD SIZE PTACS AND PTHPS BASELINE EFFICIENCY LEVELS AND TSLS
Baseline
(ASHRAE
standard
90.1–1999)
Efficiency metric
Non-Standard Size PTAC, 11,000 Btu/h ..........
Non-Standard Size PTHP, 11,000 Btu/h ..........
EER ..........................
EER ..........................
As stated in the engineering analysis
(Chapter 5 of the final rule TSD), current
Federal energy conservation standards
and the efficiency levels specified by
ASHRAE Standard 90.1–1999 for PTACs
and PTHPs are a function of the
equipment’s cooling capacity. Both the
Federal energy conservation standards
and the efficiency standards in ASHRAE
Standard 90.1–1999 are based on
equations that calculate the efficiency
levels for PTACs and PTHPs with a
cooling capacity greater than or equal to
7,000 Btu/h and less than or equal to
15,000 Btu/h for each equipment class
(see Table II.1). For the NOPR, DOE
pwalker on PROD1PC71 with RULES3
Equipment class (cooling capacity)
derived the proposed standards (i.e.,
efficiency level as a function of cooling
capacity) by plotting the representative
cooling capacities and the
corresponding efficiency levels for each
TSL. DOE then calculated the equation
of the line passing through the EER
values for 9,000 Btu/h and 12,000
Btu/h for standard size PTACs and
PTHPs. Chapter 9 of the NOPR TSD
describes in detail how DOE determined
the energy-efficiency equations for each
TSL.
For the final rule, DOE used the
energy-efficiency equations derived
from the NOPR for TSLs 1, 2, 3, 4, 5,
8.6
8.5
2.6
TSL 1
TSL 2
9.4
9.4
2.8
TSL 3
9.4
9.7
2.8
9.7
9.7
2.8
TSL 4
TSL 5
(Max-Tech)
9.4
10.0
2.9
10.0
10.0
2.9
and 6 to extend the results from the
representative cooling capacities to the
entire range of cooling capacities of
standard size PTACs and PTHPs. For
TSL A, DOE calculated a new slope of
the energy-efficiency equations using
the methodology from the NOPR.
Specifically, DOE calculated the
equation of the line passing through the
EER values for 9,000 Btu/h and 12,000
Btu/h for standard size PTACs and
PTHPs. Table V.3 and Table V.4 identify
the energy-efficiency equations for each
TSL for standard size PTACs and
PTHPs.
TABLE V.3—ENERGY-EFFICIENCY EQUATIONS (EER AS A FUNCTION OF COOLING CAPACITY) BY TSL FOR STANDARD SIZE
PTACS
Standard size ** PTACs
Energy-efficiency equation *
Baseline ASHRAE Standard 90.1–1999 ....................................................................................................
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EER = 12.5 ¥ (0.213 × Cap†/1000)
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
TABLE V.3—ENERGY-EFFICIENCY EQUATIONS (EER AS A FUNCTION OF COOLING CAPACITY) BY TSL FOR STANDARD SIZE
PTACS—Continued
Standard size ** PTACs
TSL
TSL
TSL
TSL
TSL
TSL
TSL
1
2
3
A
4
5
6
Energy-efficiency equation *
..........................................................................................................................................................
..........................................................................................................................................................
..........................................................................................................................................................
..........................................................................................................................................................
..........................................................................................................................................................
..........................................................................................................................................................
..........................................................................................................................................................
EER
EER
EER
EER
EER
EER
EER
=
=
=
=
=
=
=
13.0
13.0
13.2
13.8
13.0
13.4
13.6
¥
¥
¥
¥
¥
¥
¥
(0.233
(0.233
(0.233
(0.300
(0.233
(0.233
(0.233
×
×
×
×
×
×
×
Cap †/1000)
Cap †/1000)
Cap †/1000)
Cap †/1000)
Cap †/1000)
Cap †/1000)
Cap †/1000)
* For equipment rated according to the DOE test procedure, all EER values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled
products and evaporatively cooled products, and at 85 °F entering water temperature for water-cooled products.
** Standard size refers to PTAC or PTHP equipment with wall sleeve dimensions having an external wall opening greater than or equal to 16
inches high or greater than or equal to 42 inches wide, and a cross-sectional area greater than or equal to 670 square inches.
† Cap means cooling capacity in Btu/h at 95 °F outdoor dry-bulb temperature.
TABLE V.4—ENERGY-EFFICIENCY EQUATIONS (EER AS A FUNCTION OF COOLING CAPACITY) BY TSL FOR STANDARD SIZE
PTHPS
Standard size ** PTHPs
Energy-efficiency equation *
Baseline ASHRAE Standard 90.1–1999 ....................................................................................................
TSL 1 ..........................................................................................................................................................
TSL 2 ..........................................................................................................................................................
TSL 3 ..........................................................................................................................................................
TSL A ..........................................................................................................................................................
TSL 4 ..........................................................................................................................................................
TSL 5 ..........................................................................................................................................................
TSL 6 ..........................................................................................................................................................
EER = 12.3 ¥ (0.213 × Cap†/1000)
COP = 3.2 ¥ (0.026 × Cap †/1000)
EER = 13.0 ¥ (0.233 × Cap †/1000)
COP = 3.6 ¥ (0.046 × Cap †/1000)
EER = 13.2 ¥ (0.233 × Cap †/1000)
COP = 3.6 ¥ (0.044 × Cap †/1000)
EER = 13.2 ¥ (0.233 × Cap †/1000)
COP = 3.6 ¥ (0.044 × Cap †/1000)
EER = 14.0 ¥ (0.300 × Cap †/1000)
COP = 3.7 ¥ (0.052 × Cap †/1000)
EER = 13.4 ¥ (0.233 × Cap †/1000)
COP = 3.7 ¥ (0.053 × Cap †/1000)
EER = 13.4 ¥ (0.233 × Cap †/1000)
COP = 3.7 ¥ (0.053 × Cap †/1000)
EER = 13.6 ¥ (0.233 × Cap †/1000)
COP = 3.8 ¥ (0.053 × Cap †/1000)
* For equipment rated according to the DOE test procedure, all EER values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled
and evaporatively cooled products, and at 85 °F entering water temperature for water-cooled products. All COP values must be rated at 47 °F
outdoor dry-bulb temperature for air-cooled products, and at 70 °F entering water temperature for water-source heat pumps.
** Standard size refers to PTAC or PTHP equipment with wall sleeve dimensions having an external wall opening greater than or equal to 16
inches high or greater than or equal to 42 inches wide, and a cross-sectional area greater than or equal to 670 square inches.
† Cap means cooling capacity in Btu/h at 95 °F outdoor dry-bulb temperature.
For non-standard size PTACs and
PTHPs, DOE used the ASHRAE
Standard 90.1–1999 equation slope and
the representative cooling capacity (i.e.,
11,000 Btu/h cooling capacity) to
determine the energy-efficiency
equations corresponding to each TSL in
the NOPR. Chapter 9 of the NOPR TSD
details how DOE determined the energyefficiency equations for each TSL. For
the final rule, DOE used the energyefficiency equations presented in the
NOPR for TSLs 1 through 5 to extend
the results from the representative
cooling capacities to the entire range of
cooling capacities of non-standard size
PTACs and PTHPs. Table V.5 and Table
V.6 identify the energy-efficiency
equations for each TSL for non-standard
size PTAC and PTHP.
TABLE V.5—ENERGY-EFFICIENCY EQUATIONS (EER AS A FUNCTION OF COOLING CAPACITY) BY TSL FOR NON-STANDARD
SIZE PTACS
Non-standard size ** PTACs
Energy-efficiency equation *
pwalker on PROD1PC71 with RULES3
Baseline ASHRAE Standard 90.1¥1999 ...................................................................................................
TSL 1 ..........................................................................................................................................................
TSL 2 ..........................................................................................................................................................
TSL 3 ..........................................................................................................................................................
TSL 4 ..........................................................................................................................................................
TSL 5 ..........................................................................................................................................................
EER
EER
EER
EER
EER
EER
=
=
=
=
=
=
10.9
11.7
11.7
12.0
11.7
12.3
¥
¥
¥
¥
¥
¥
(0.213
(0.213
(0.213
(0.213
(0.213
(0.213
×
×
×
×
×
×
Cap†/1000)
Cap †/1000)
Cap †/1000)
Cap †/1000)
Cap †/1000)
Cap †/1000)
* For equipment rated according to the DOE test procedure, all EER values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled
and evaporatively cooled products, and at 85 °F entering water temperature for water-cooled products.
** Non-standard size refers to PTAC or PTHP equipment with existing wall sleeve dimensions having an external wall opening of less than 16
inches high or less than 42 inches wide, and a cross-sectional area less than 670 square inches.
† Cap means cooling capacity in Btu/h at 95 °F outdoor dry-bulb temperature.
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58803
TABLE V.6—ENERGY-EFFICIENCY EQUATIONS (EER AS A FUNCTION OF COOLING CAPACITY) BY TSL FOR NON-STANDARD
SIZE PTHPS
Non-standard size ** PTHPs
Energy-efficiency equation *
Baseline ASHRAE Standard 90.1–1999 ....................................................................................................
EER = 10.8¥(0.213 × Cap †/1000)
COP = 2.9¥(0.026 × Cap †/1000)
TSL 1 ..........................................................................................................................................................
EER = 11.7¥(0.213 × Cap †/1000)
COP = 3.1¥(0.026 × Cap †/1000)
EER = 12.0¥(0.213 × Cap †/1000)
COP = 3.1¥(0.026 × Cap †/1000)
EER = 12.0¥(0.213 × Cap †/1000)
COP = 3.1¥(0.026 × Cap †/1000)
EER = 12.3¥(0.213 × Cap †/1000)
COP = 3.1¥(0.026 × Cap †/1000)
EER = 12.3¥(0.213 × Cap †/1000)
COP = 3.1¥(0.026 × Cap †/1000)
TSL 2 ..........................................................................................................................................................
TSL 3 ..........................................................................................................................................................
TSL 4 ..........................................................................................................................................................
TSL 5 ..........................................................................................................................................................
* For equipment rated according to the DOE test procedure, all EER values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled
and evaporatively cooled products, and at 85 °F entering water temperature for water-cooled products. All COP values must be rated at 47 °F
outdoor dry-bulb temperature for air-cooled products, and at 70 °F entering water temperature for water-source heat pumps.
** Non-standard size refers to PTAC or PTHP equipment with existing wall sleeve dimensions having an eternal wall opening of less than 16
inches high or less than 42 inches wide, and a cross-sectional area less than 670 square inches.
† Cap means cooling capacity in Btu/h at 95 °F outdoor dry-bulb temperature.
For PTACs and PTHPs with a cooling
capacity of less than 7,000 Btu/h, DOE
determined the EERs using a cooling
capacity of 7,000 Btu/h in the energyefficiency equations. For PTACs and
PTHPs with a cooling capacity greater
than 15,000 Btu/h cooling capacity,
DOE determined the EERs using a
cooling capacity of 15,000 Btu/h in the
energy-efficiency equations. This is the
same method established in the Energy
Policy Act of 1992 and provided in
ASHRAE Standard 90.1–1999 for
calculating the EER and COP of
equipment with cooling capacities less
than 7,000 Btu/h and greater than
15,000 Btu/h.
undiscounted and discounted values of
energy savings from 2012 through 2042.
Discounted energy savings at rates of 7
percent and 3 percent represent a policy
perspective where energy savings
farther in the future are less significant
than energy savings closer to the
present. Each TSL that is more stringent
than the corresponding level in
ASHRAE Standard 90.1–1999 results in
additional energy savings, ranging from
0.015 quads to 0.068 quads for TSLs 1
through 6 for standard size PTAC and
PTHP equipment classes, and from
0.004 to 0.009 quads for TSLs 1 through
5 for non-standard size PTAC and PTHP
equipment classes.
B. Significance of Energy Savings
To estimate the energy savings
through 2042 due to amended
standards, DOE compared the energy
consumption of packaged terminal
equipment under the base case
(standards at the levels in ASHRAE
Standard 90.1–1999) to energy
consumption of this equipment under
each standards case (i.e., each TSL, or
set of amended standards, that DOE has
considered). Table V.7 and Table V.8
summarize DOE’s NES estimates, which
are based on the AEO2008 energy price
forecast, for each TSL. Chapter 11 of the
TSD describes these estimates in more
detail. The tables provide both
TABLE V.7—SUMMARY OF CUMULATIVE NATIONAL ENERGY SAVINGS FOR STANDARD SIZE PTACS AND PTHPS
[Energy savings for units sold from 2012 to 2042]
Trial standard level
Primary national energy savings (quads)
(sum of all equipment classes)
1
2
3
A
4
5
6
3%
Discounted
Undiscounted
...................................................................................................................................................
...................................................................................................................................................
...................................................................................................................................................
...................................................................................................................................................
...................................................................................................................................................
...................................................................................................................................................
...................................................................................................................................................
0.015
0.024
0.031
0.032
0.033
0.049
0.068
0.007
0.012
0.016
0.016
0.017
0.025
0.035
7%
Discounted
0.003
0.006
0.007
0.007
0.008
0.011
0.015
TABLE V.8—SUMMARY OF CUMULATIVE NATIONAL ENERGY SAVINGS FOR NON-STANDARD SIZE PTACS AND PTHPS
[Energy savings for units sold from 2012 to 2042]
Trial standard level
pwalker on PROD1PC71 with RULES3
Primary national energy savings (quads)
(sum of all equipment classes)
1
2
3
4
Undiscounted
...................................................................................................................................................
...................................................................................................................................................
...................................................................................................................................................
...................................................................................................................................................
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0.004
0.004
0.005
0.006
07OCR3
3%
Discounted
0.002
0.002
0.003
0.003
7%
Discounted
0.001
0.001
0.001
0.001
58804
Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
TABLE V.8—SUMMARY OF CUMULATIVE NATIONAL ENERGY SAVINGS FOR NON-STANDARD SIZE PTACS AND PTHPS—
Continued
[Energy savings for units sold from 2012 to 2042]
Trial standard level
Primary national energy savings (quads)
(sum of all equipment classes)
Undiscounted
pwalker on PROD1PC71 with RULES3
5 ...................................................................................................................................................
Several commenters noted the
potential for equipment switching
where TSLs resulted in higher cooling
efficiency requirements for PTHP and
PTAC of the same cooling capacity.
Higher cooling efficiency requirements
would result in an increase in the price
differential of minimum efficiency
PTHP and PTAC equipment, causing
some PTHP customers to shift to a
PTAC with electric resistance heat.
From the perspective of assessing the
energy savings achieved by a standard at
a defined TSL, the primary concern
from this anticipated equipment
switching is the loss in energy savings
that could result if some fraction of the
PTHP market switches to the use of
PTAC with electric resistance heat.
While DOE recognizes that some PTHP
customers might also switch to the use
of fossil fuel (e.g. hydronic) heating, the
relatively small fraction of the existing
PTAC customers who currently use
hydronic heat for the spaces served by
PTAC (estimated at less than 1%), and
the difficulty of retrofitting hydronic
heating into buildings that do not use it
suggests that the total fraction of the
market that would opt for PTAC with
hydronic heating is small. The majority
of the total packaged terminal
equipment market (PTAC and PTHP)
currently uses PTAC with electric
resistance heat, which supports the
possibility that some purchasers would
choose to switch from PTHPs to PTACs.
DOE did not have the information
with which to assess the elasticity of the
PTHP market with regards to this
switching between PTHP and PTAC. To
assess the significance of a shift from
PTHP to PTAC purchases, DOE
calculated the total fraction of the heat
pump market that would need to shift
to the purchase of PTAC equipment to
negate the energy savings from
increasing the PTHP cooling efficiency
above that of the PTAC equipment. Two
TSLs were first examined, TSL 2, and
TSL 4. For standard size PTAC and
PTHP equipment, TSL 2 has the same
EER requirements for PTAC as TSL 1
but has a 0.2 EER increase for PTHP
equipment as compared with TSL 1. For
TSL 2, DOE calculated that a shift of 2.0
percent of the heat pump market to the
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use of PTAC with electric resistance
would be sufficient to offset the energy
savings difference between TSL 1 and
TSL 2. If PTAC and PTHP standards
were set at TSL 2, the purchase price
differential between the two would
increase on the order of $11, which
would represent an increase of
approximately 9.4 percent increase in
the purchase price differential between
PTAC and PTHP over TSL 1. This
increase in the purchase price
differential results from the increased
PTHP efficiency at TSL 2. At TSL 1, the
average annual payback in 2012 for a
PTHP over a PTAC was calculated at
approximately 2.10 years. At TSL 2, the
average annual payback for a PTHP over
a PTAC was 2.18 years. The average PBP
for purchase of a PTHP over a PTAC
increased 3.7 percent between TSL 1
and TSL 2.
Similarly, for TSL 4, DOE calculated
that a shift of 3.8 percent of the heat
pump market to the use of PTAC with
electric resistance would offset the
energy savings difference between TSL
1 and TSL 4. If PTAC and PTHP
standards were set at TSL 4, the
purchase price differential between the
two would increase on the order of $22,
or an 18.8 percent increase in the
purchase price differential compared to
that at TSL 1. This increase in price
reflects the higher efficiency of the
PTHP equipment at TSL 2 and TSL 4.
At TSL 4, the average annual payback
for purchase of a PTHP over a PTAC
was 2.29 years. The average PBP for
purchase of a PTHP over a PTAC
increased approximately 9.2 percent
between TSL 1 and TSL 4.
DOE also examined TSL A in light of
potential equipment switching. In the
case of TSL A, there is no comparable
TSL considered by DOE that had a
PTAC cooling efficiency level identical
to TSL A but with PTHP cooling
efficiencies at the same efficiency level.
However, the nominal difference
between PTHP and PTAC EER levels at
TSL A, 0.2 EER, is identical to the
nominal difference in EER levels at TSL
2 for all capacities. The difference in
equipment price between a PTHP and
PTAC at TSL A is $127 for a 9,000
Btu/h unit and $129 for a 12,000
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0.009
3%
Discounted
7%
Discounted
0.004
0.002
Btu/h unit, which is virtually identical
to the price differential at TSL 2, and
represents a 9.2 percent increase in
differential purchase price compared
with TSL 1. DOE examined the energy
savings at TSL A and TSL 1 for standard
size PTAC and PTHP equipment only,
and determined that under TSL A, it
would take approximately 4.0 percent of
standard size PTHP users to switch to a
PTAC to negate the energy savings for
TSL A over TSL 1. At TSL A, the
estimated PBP for purchase of a PTHP
over a PTAC under average use
conditions was estimated at 2.15 years.
Given the very small increase in
differential purchase price between
PTAC and PTHP at TSL A compared
with standards set at identical efficiency
levels (TSL 1) and the minimal
difference in payback period at TSL A
compared to TSL 1, DOE concludes that
it is unlikely that an efficiency Standard
set at TSL A would result in a
significant number of standard size
PTHP customers opting to instead
purchase PTAC equipment with electric
resistance heat.
C. Economic Justification
1. Economic Impact on Commercial
Consumers
a. Life-Cycle Costs and Payback Period
Commercial consumers will be
affected by the standards because they
will experience higher purchase prices
and lower operating costs. Generally,
these impacts are best captured by
changes in life-cycle costs and payback
period. To determine these impacts,
DOE calculated the LCC and PBP for the
standard levels considered in this
proceeding. DOE’s LCC and PBP
analyses provided five key outputs for
each TSL, which are reported in Table
V.9 through Table V.14. The first three
outputs in each table are the proportion
of PTAC or PTHP purchases in which
the purchase of a design that complies
with the TSL would create a net lifecycle cost, no impact, or a net life-cycle
cost savings for the consumer. The
fourth output is the average net lifecycle savings from purchasing a
complying design compared with
purchasing baseline equipment.
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
The fifth output is the average PBP for
the consumer purchasing a design that
complies with the TSL compared with
purchasing baseline equipment. The
PBP is the number of years it would take
for the customer to recover, as a result
of energy savings, the increased costs of
higher-efficiency equipment based on
the operating cost savings from the first
year of ownership. The PBP is an
58805
economic benefit-cost measure that uses
benefits and costs without discounting.
TSD Chapter 8 details the LCC and PBP
analyses.
TABLE V.9—SUMMARY LCC AND PBP RESULTS FOR STANDARD SIZE PTAC WITH A COOLING CAPACITY OF
9,000 BTU/H
Trial standard level *
1
EER ......................................................................................
PTAC with Net LCC Increase (%) .......................................
PTAC with No Change in LCC (%) .....................................
PTAC with Net LCC Savings (%) ........................................
Mean LCC Savings (2007$) ................................................
Mean Payback Period (years) .............................................
2
3
A
4
5
6
10.9
15
77
7
(1)
13.0
10.9
15
77
7
(1)
13.0
11.1
30
56
14
(3)
13.7
11.1
30
56
14
(3)
13.7
10.9
15
77
7
(1)
13.0
11.3
46
37
17
(6)
14.5
11.5
62
18
21
(10)
15.2
* Numbers in parentheses indicate negative LCC savings, i.e., an increase in LCC. Detailed percentage changes may not sum to 100% due to
rounding.
TABLE V.10—SUMMARY LCC AND PBP RESULTS FOR STANDARD SIZE PTHP WITH A COOLING CAPACITY OF
9,000 BTU/H
Trial standard level *
1
EER ......................................................................................
PTHP with Net LCC Increase (%) .......................................
PTHP with No Change in LCC (%) .....................................
PTHP with Net LCC Savings (%) ........................................
Mean LCC Savings (2007$) ................................................
Mean Payback Period (years) .............................................
2
10.9
7
78
16
11
5.1
3
11.1
10
57
33
20
4.5
A
11.1
10
57
33
20
4.5
4
11.3
13
37
50
28
4.4
5
11.3
13
37
50
28
4.4
6
11.3
13
37
50
28
4.4
11.5
24
18
58
24
5.1
* Numbers in parentheses indicate negative LCC savings, i.e., an increase in LCC. Detailed percentage changes may not sum to 100% due to
rounding.
TABLE V.11—SUMMARY LCC AND PBP RESULTS FOR STANDARD SIZE PTAC WITH A COOLING CAPACITY OF
12,000 BTU/H
Trial standard level *
1
EER ......................................................................................
PTAC with Net LCC Increase (%) .......................................
PTAC with No Change in LCC (%) .....................................
PTAC with Net LCC Savings (%) ........................................
Mean LCC Savings * (2007$) ..............................................
Mean PBP (years) ...............................................................
2
3
A
4
5
6
10.2
16
77
7
(2)
13.1
10.2
16
77
7
(2)
13.1
10.4
31
56
13
(5)
14.0
10.2
16
77
7
(2)
13.1
10.2
16
77
7
(2)
13.1
10.6
48
36
16
(10)
14.9
10.8
65
18
17
(15)
15.9
* Numbers in parentheses indicate negative savings, i.e., an increase in LCC. Detailed percentage changes may not sum to 100% due to
rounding.
TABLE V.12—SUMMARY LCC AND PBP RESULTS FOR STANDARD SIZE PTHP WITH A COOLING CAPACITY OF
12,000 BTU/H
Trial standard level *
pwalker on PROD1PC71 with RULES3
1
EER ......................................................................................
PTHP with Net LCC Increase (%) .......................................
PTHP with No Change in LCC (%) .....................................
PTHP with Net LCC Savings (%) ........................................
Mean LCC Savings (2007$) ................................................
Mean PBP (years) ...............................................................
2
10.2
7
77
16
13
5.1
3
10.4
10
57
33
24
4.6
A
10.4
10
57
33
24
4.6
4
10.4
10
57
33
24
4.6
5
10.6
21
37
42
20
5.5
6
10.6
21
37
42
20
5.5
10.8
35
18
47
14
6.4
* Numbers in parentheses indicate negative savings, i.e., an increase in LCC. Detailed percentage changes may not sum to 100% due to
rounding.
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
TABLE V.13—SUMMARY LCC AND PBP RESULTS FOR NON-STANDARD SIZE PTACS WITH A COOLING CAPACITY OF
11,000 BTU/H
Trial standard level *
1
EER ..............................................................................................................................
PTAC with Net LCC Increase (%) ...............................................................................
PTAC with No Change in LCC (%) .............................................................................
PTAC with Net LCC Savings (%) ................................................................................
Mean LCC Savings (2007$) ........................................................................................
Mean PBP (years) .......................................................................................................
2
9.4
6
73
22
26
4.4
3
9.4
6
73
22
26
4.4
4
9.7
14
47
39
30
5.1
5
9.4
6
73
22
26
4.4
10.0
25
23
52
31
5.9
* Numbers in parentheses indicate negative savings, i.e., an increase in LCC. Detailed percentage changes may not sum to 100% due to
rounding.
TABLE V.14—SUMMARY LCC AND PBP RESULTS FOR NON-STANDARD SIZE PTHPS WITH A COOLING CAPACITY OF
11,000 BTU/H
Trial standard level *
1
EER ..............................................................................................................................
PTHP with Net LCC Increase (%) ...............................................................................
PTHP with No Change in LCC (%) .............................................................................
PTAC with Net LCC Savings (%) ................................................................................
Mean LCC Savings (2007$) ........................................................................................
Mean PBP (years) .......................................................................................................
2
9.4
1
73
27
62
2.2
3
9.7
3
47
50
66
2.8
4
9.7
3
47
50
66
2.8
5
10.0
5
23
72
80
3.0
10.0
5
23
72
80
3.0
* Numbers in parentheses indicate negative savings, i.e., an increase in LCC. Detailed percentage changes may not sum to 100% due to
rounding.
For PTACs and PTHPs with a cooling
capacity of less than 7,000 Btu/h, DOE
established the energy conservation
standards using a cooling capacity of
7,000 Btu/h in the efficiency-capacity
equation (see section VI.A). The LCC
and PBP impacts for equipment in this
category will be similar to the impacts
for the 9,000 Btu/h units because the
MSP and usage characteristics are in a
similar range. Similarly, for PTACs and
PTHPs with a cooling capacity greater
than 15,000 Btu/h, DOE established the
energy conservation standards using a
cooling capacity of 15,000 Btu/h in the
efficiency-capacity equation. Further,
for PTACs and PTHPs with a cooling
capacity greater than 15,000 Btu/h, DOE
established that the impacts will be
similar for units with a cooling capacity
of 12,000 Btu/h. Section V.A of today’s
final rule provides more details on how
DOE developed the energy-efficiency
equations based on the analysis results
for the representative cooling capacities.
b. Commercial Consumer Subgroup
Analysis
DOE estimated commercial consumer
subgroup impacts by determining the
LCC impacts at each TSL on small
businesses, such as small independent
hotels and motels. Table V.15 shows the
mean LCC savings from the final energy
conservation standards; Table V.16
shows the mean payback period (in
years) for this subgroup of commercial
consumers. DOE’s analysis using the
LCC spreadsheet model indicated that
the LCC and PBP impacts on the small
independent hotels and motels were
similar to the corresponding impacts on
the larger population of the commercial
consumers. Chapter 12 of the TSD
explains DOE’s method for conducting
the consumer subgroup analysis and
presents the detailed results of that
analysis.
TABLE V.15—MEAN LIFE-CYCLE COST SAVINGS FOR PTAC OR PTHP EQUIPMENT PURCHASED BY LCC SUBGROUPS
(2007$)
Equipment class (cooling capacity)
Trial standard level
Standard Size
Standard
Standard
Standard
Standard
Size
Size
Size
Size
PTAC
PTHP
PTAC
PTHP
TSL 1
TSL 3
TSL A
TSL 4
TSL 5
TSL 6
(2)
8
(4)
10
(2)
16
(4)
18
(5)
16
(7)
18
(5)
22
(4)
18
(2)
22
(4)
13
(9)
22
(13)
13
(13)
17
(19)
7
(9,000 Btu/h) .................................................................
(9,000 Btu/h) .................................................................
(12,000 Btu/h) ...............................................................
(12,000 Btu/h) ...............................................................
Non-Standard Size
pwalker on PROD1PC71 with RULES3
TSL 2
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
22
54
22
56
24
56
22
68
23
68
Non-Standard Size PTAC ................................................................................
Non-Standard Size PTHP ................................................................................
* Numbers in parentheses indicate negative savings.
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TABLE V.16—MEAN PAYBACK PERIOD FOR PTAC OR PTHP EQUIPMENT PURCHASED BY LCC SUBGROUPS (YEARS)
Equipment class (cooling capacity)
Trial standard level
Standard Size
Standard
Standard
Standard
Standard
Size
Size
Size
Size
PTAC
PTHP
PTAC
PTHP
TSL 1
Non-Standard Size
Non-Standard Size PTAC ..............................................................................................
Non-Standard Size PTHP ..............................................................................................
2. Economic Impact on Manufacturers
DOE described the qualitative
economic impacts of today’s standard
on manufacturers in the NOPR. 73 FR
18893–99. This analysis is described in
greater detail in Chapter 13 of the TSD.
As part of its NOPR analysis, DOE
analyzed two distinct markup scenarios:
(1) The flat markup scenario, and (2) the
partial cost recovery markup scenario.
73 FR 18886. The flat markup scenario
can also be characterized as the
‘‘preservation of gross margin
percentage’’ scenario. Under this
scenario, DOE applied, across all TSLs,
a single uniform ‘‘gross margin
percentage’’ markup that DOE believes
represents the current markup for
manufacturers in the PTAC and PTHP
industry. This flat markup scenario
implies that, as production costs
increase with efficiency, the absolute
dollar markup will also increase. DOE
calculated that the non-production cost
markup, which consists of SG&A
expenses, R&D expenses, interest, and
profit, is 1.29. This markup is consistent
with the one DOE used in its
engineering and GRIM analyses for the
base case.
TSL 3
TSL A
TSL 4
TSL 5
TSL 6
13.0
5.0
13.1
5.1
13.0
4.5
13.1
4.6
13.6
4.5
13.9
4.6
13.6
4.4
13.1
4.6
13.0
4.4
13.1
5.5
14.4
4.4
14.8
5.5
15.1
5.1
15.8
6.3
TSL 1
(9,000 Btu/h) ...............................................................................
(9,000 Btu/h) ...............................................................................
(12,000 Btu/h) .............................................................................
(12,000 Btu/h) .............................................................................
TSL 2
TSL 2
TSL 3
TSL 4
TSL 5
4.4
2.2
4.4
2.8
5.1
2.8
4.4
2.9
5.9
2.9
The implicit assumption behind the
‘‘partial cost recovery’’ scenario is that
the industry can pass-through only part
of its regulatory-driven increases in
production costs to consumers in the
form of higher prices. DOE implemented
this markup scenario in the GRIM by
setting the non-production cost markups
at each TSL to yield an increase in MSP
equal to half the increase in production
cost.
Together, these two markup scenarios
characterize the markup conditions
described by manufacturers, and reflect
the range of market responses
manufacturers expect as a result of the
R–22 phaseout and the amended energy
conservation standards (See Chapter 13
of the TSD for additional details of the
markup scenarios.). For this final rule,
DOE also examined both of these
scenarios.
a. Industry Cash-Flow Analysis Results
Using the two different markup
scenarios described above, DOE
estimated the impact of amended
standards for PTACs and PTHPs on the
INPV of the package terminal equipment
industry. See 73 FR 18886–87 and
18893–94. The impact of new standards
on INPV consists of the difference
between the INPV in the base case and
the INPV in the standards case. INPV is
the primary metric used in the MIA, and
represents one measure of the fair value
of the industry in today’s dollars. DOE
calculated the INPV by summing all of
the net cash flows, discounted at the
industry’s cost of capital or discount
rate.
Table V.17 through Table V.20 show
the estimated changes in INPV for
manufacturers of standard size packaged
terminal equipment and non-standard
size packaged terminal equipment,
respectively, that would result from the
TSLs DOE considered for this final rule.
The tables also present the equipment
conversion expenses and capital
investments that the industry would
incur at each TSL. Equipment
conversion expenses include
engineering, prototyping, testing, and
marketing expenses incurred by a
manufacturer as it prepares to comply
with a standard. Capital investments are
the one-time outlays for equipment and
buildings required for the industry to
comply (i.e., conversion capital
expenditures).
TABLE V.17—MANUFACTURER IMPACT ANALYSIS RESULTS, INCLUDING INPV ESTIMATES, FOR STANDARD SIZE PTACS
AND PTHPS UNDER THE FLAT MARKUP SCENARIO
R–410A full cost recovery with amended energy standards full recovery of increased cost
Base
case
Units
pwalker on PROD1PC71 with RULES3
INPV ..........................
Change in INPV ........
Amended Energy
Conservation
Standards Equipment Conversion
Expenses.
Amended Energy
Conservation
Standards Capital
Conversion Expenses.
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Trial standard level
1
2
3
A
4
5
6
(2007$ millions) ........
(2007$ millions) ........
(%) ............................
(2007$ millions) ........
427
................
................
................
424
¥3
¥0.8
4.5
421
¥6
¥1.4
7.4
424
¥3
¥0.8
6.3
419
¥8
¥1.9
9.1
419
¥8
¥1.9
10.6
426
¥1
¥0.2
7.2
423
¥4
¥0.9
13.5
(2007$ millions) ........
................
3.5
5.7
4.9
8.2
8.2
5.6
10.4
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TABLE V.17—MANUFACTURER IMPACT ANALYSIS RESULTS, INCLUDING INPV ESTIMATES, FOR STANDARD SIZE PTACS
AND PTHPS UNDER THE FLAT MARKUP SCENARIO—Continued
R–410A full cost recovery with amended energy standards full recovery of increased cost
Base
case
Units
Total Energy Conservation Standards
Investment Required.
(2007$ millions) ........
Trial standard level
1
................
2
8.0
3
13.2
A
11.2
4
17.3
5
18.7
6
12.8
23.9
TABLE V.18—MANUFACTURER IMPACT ANALYSIS RESULTS, INCLUDING INPV ESTIMATES, FOR STANDARD SIZE PTACS
AND PTHPS UNDER THE PARTIAL COST RECOVERY MARKUP SCENARIO
R–410A base case full cost recovery with amended energy standards partial cost recovery
Base
case
Units
INPV ...........................
Change in INPV .........
(2007$ millions) .........
(2007$ millions) .........
(%) .............................
(2007$ millions) .........
Amended Energy Conservation Standards
Equipment Conversion Expenses.
Amended Energy Con- (2007$ millions) .........
servation Standards
Capital Conversion
Expenses.
Total Energy Con(2007$ millions) .........
servation Standards
Investment Required.
Trial standard level
1
2
3
A
4
5
6
427
..............
..............
..............
399
¥28
¥6.6
4.5
382
¥45
¥10.7
7.4
367
¥60
¥14.0
6.3
366
¥61
¥14.3
9.1
359
¥68
¥16.0
10.6
325
¥103
¥24.0
7.2
263
¥164
¥38.3
13.5
..............
3.5
5.7
4.9
8.2
8.2
5.6
10.4
..............
8.0
13.2
11.2
17.3
18.7
12.8
23.9
TABLE V.19—MANUFACTURER IMPACT ANALYSIS RESULTS, INCLUDING INPV ESTIMATES, FOR NON-STANDARD SIZE
PTACS AND PTHPS UNDER THE FLAT MARKUP SCENARIO
R–410A full cost recovery with amended energy standards full recovery of increased cost
Base
case
Units
INPV ...............................................
Change in INPV .............................
Amended Energy Conservation
Standards Equipment Conversion Expenses.
Amended Energy Conservation
Standards Capital Conversion
Expenses.
Total Energy Conservation Standards Investment Required.
Trial standard level
1
2
3
4
5
(2007$ millions) .............................
(2007$ millions) .............................
(%) .................................................
(2007$ millions) .............................
30
..............
..............
..............
14
¥16
¥53.6
20.5
13
¥17
¥57.6
21.0
13
¥17
¥56.3
21.0
9
¥21
¥68.5
23.8
11
¥20
¥64.8
23.8
(2007$ millions) .............................
..............
1.3
2.3
2.0
3.6
2.6
(2007$ millions) .............................
..............
21.8
23.3
23.0
27.3
26.4
TABLE V.20—MANUFACTURER IMPACT ANALYSIS RESULTS, INCLUDING INPV ESTIMATES, FOR NON-STANDARD SIZE
PTACS AND PTHPS UNDER THE PARTIAL COST RECOVERY MARKUP SCENARIO
R–410A base case full cost recovery with amended energy standards partial cost recovery
Base
case
pwalker on PROD1PC71 with RULES3
Units
INPV ...............................................
Change in INPV .............................
Amended Energy Conservation
Standards Equipment Conversion Expenses.
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(2007$ millions) .............................
(%) .................................................
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..............
..............
..............
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1
13
¥17
¥57.8
20.5
2
3
11
¥19
¥63.8
21.0
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¥65.4
21.0
4
7
¥23
¥78.0
23.8
5
6
¥24
¥81.2
23.8
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TABLE V.20—MANUFACTURER IMPACT ANALYSIS RESULTS, INCLUDING INPV ESTIMATES, FOR NON-STANDARD SIZE
PTACS AND PTHPS UNDER THE PARTIAL COST RECOVERY MARKUP SCENARIO—Continued
R–410A base case full cost recovery with amended energy standards partial cost recovery
Amended Energy Conservation
Standards Capital Conversion
Expenses.
Total Energy Conservation Standards Investment Required.
Trial standard level
Base
case
Units
1
2
3
4
5
(2007$ millions) .............................
..............
1.3
2.3
2.0
3.6
2.6
(2007$ millions) .............................
..............
21.8
23.3
23.0
27.3
26.4
The NOPR provides a discussion of
the estimated impact of amended PTAC
and PTHP standards on INPV for each
equipment class. 73 FR 18893–97. This
qualitative discussion on the estimated
impacts of amended PTAC and PTHP
standards in INPV for each equipment
class for the final rule can be found in
Chapter 13 of the TSD.
b. Impacts on Employment
As discussed in the NOPR, DOE
expects no significant, discernable
direct employment impacts on both
standard size and non-standard size
PTAC and PTHP manufacturers under
today’s standards compared to the base
case, or under any of the TSLs
considered for today’s rule. 73 FR
18898. Today’s notice estimates the
impacts on U.S. production workers in
the standard size and non-standard size
PTAC and PTHP industry impacted by
the final rule. The estimated impacts are
shown in Table V.21. For the standard
size PTAC and PTHP industry, DOE
does not expect negative direct
employment impacts because the labor
content of each unit produced is
expected to be slightly higher and the
total number of units produced is
expected to be the same. Furthermore,
based on interviews with domestic
manufacturers, DOE expects the
proportion of units produced
domestically to remain unchanged.
Therefore, DOE presents a scenario
where employment increases as a
function of increasing production costs.
For the non-standard size PTAC and
PTHP industry, DOE reports a range of
possible domestic employment impacts.
Assuming shipment levels and product
availability remain at the levels
experienced in the current market, DOE
expects a slight increase in domestic
employment as characterized by the
high-bound scenario. However, if either
shipments drop or if manufacturers
respond to higher labor requirements by
shifting production to lower-labor-cost
countries, DOE expects that there could
be reductions in total domestic
employment as characterized by the
low-bound scenario. Further support for
these conclusions is set forth in Chapter
13 of the final rule TSD.
TABLE V.21—CHANGE IN TOTAL NUMBER OF DOMESTIC PRODUCTION EMPLOYEES IN 2012 IN THE STANDARD SIZE AND
NON-STANDARD SIZE PTAC AND PTHP MANUFACTURING INDUSTRY *
Standard size PTAC and PTHP manufacturing industry
TSL 1
Change in Total Number of Domestic
Production Employees in 2012 ............
TSL 2
1
TSL 3
2
TSL A
3
TSL 4
3
TSL 5
3
TSL 6
6
9
Non-standard size PTAC and PTHP manufacturing industry
TSL 1
Change in Total Number of Domestic Production Employees in 2012 ..
TSL 2
TSL 3
TSL 4
TSL 5
(106)—1
(106)—1
(107)—1
(107)—1
(108)—2
* Numbers in parentheses indicate a loss in domestic employment.
3. National Net Present Value and Net
National Employment
The NPV analysis estimates the
cumulative benefits or costs to the
Nation that would result from particular
standard levels. While the NES analysis
estimates the energy savings from each
standard level DOE considers, relative
to the base case, the NPV analysis
estimates the national economic impacts
of each such level relative to the base
case. Table V.22 and Table V.23 provide
an overview of the NPV results for
PTACs and PTHPs, respectively, using
both a 7-percent and a 3-percent real
discount rate. See TSD Chapter 11 for
more detailed NPV results.
TABLE V.22—SUMMARY OF CUMULATIVE NET PRESENT VALUE FOR STANDARD SIZE PTACS AND PTHPS
pwalker on PROD1PC71 with RULES3
PTAC NPV *
(million 2007$)
PTHP NPV *
(million 2007$)
PTAC and PTHP
NPV * (million 2007$)
Trial standard level
7% Discount
rate
1 ...................................................
2 ...................................................
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($3)
(3)
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rate
($1)
(1)
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rate
$4
12
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rate
$18
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8
3% Discount
rate
$17
43
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TABLE V.22—SUMMARY OF CUMULATIVE NET PRESENT VALUE FOR STANDARD SIZE PTACS AND PTHPS—Continued
PTAC NPV *
(million 2007$)
PTHP NPV *
(million 2007$)
PTAC and PTHP
NPV * (million 2007$)
Trial standard level
7% Discount
rate
3
A
4
5
6
...................................................
...................................................
...................................................
...................................................
...................................................
3% Discount
rate
(9)
(5)
(3)
(20)
(38)
7% Discount
rate
(6)
(3)
(1)
(20)
(43)
3% Discount
rate
12
15
10
10
(3)
7% Discount
rate
44
57
50
50
34
3% Discount
rate
2
10
6
(11)
(41)
38
54
49
31
(10)
* Numbers in parentheses indicate negative NPV, i.e., a net cost. Detail may not appear to sum to total due to rounding.
TABLE V.23—SUMMARY OF CUMULATIVE NET PRESENT VALUE FOR NON-STANDARD SIZE PTACS AND PTHPS
PTAC NPV *
(million 2007$)
PTHP NPV *
(million 2007$)
PTAC and PTHP
NPV* (million 2007$)
Trial standard level
7% Discount
rate
1
2
3
4
5
...................................................
...................................................
...................................................
...................................................
...................................................
3% Discount
rate
$2
2
3
2
4
7% Discount
rate
$6
6
8
6
11
3% Discount
rate
$3
4
4
6
6
7% Discount
rate
$8
10
10
17
17
$5
6
7
8
10
3% Discount
rate
$14
16
19
23
29
pwalker on PROD1PC71 with RULES3
* Numbers in parentheses indicate negative NPV, i.e., a net cost. Detail may not appear to sum to total due to rounding.
Using a 3-percent discount rate
increases the present value of future
equipment purchase costs and operating
cost savings. Because annual operating
cost savings in later years grow at a
faster rate than annual equipment
purchase costs, using a 3-percent
discount rate increases the NPV at most
TSLs. (See TSD Chapter 11.)
DOE also estimated the national
employment impacts that would result
from each TSL. As discussed in the
NOPR, 73 FR 18887, 18899–900, 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.
As Table V.24 and Table V.25 illustrate,
DOE estimates net indirect employment
impacts—those changes of employment
in the larger economy (other than in the
manufacturing sector being regulated)—
from PTAC and PTHP energy
conservation standards to be positive
but very small relative to total national
employment, primarily due to the small
net monetary savings from PTAC and
PTHP standards available for transfer to
other sectors, relative to the economy as
a whole. This increase would likely be
sufficient to fully offset any adverse
impacts on employment that might
occur in the packaged terminal
equipment industry. For details on the
employment impact analysis methods
and results, see TSD Chapter 15.
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TABLE V.24—NET NATIONAL CHANGE 4. Impact on Utility or Performance of
IN INDIRECT EMPLOYMENT, JOBS IN Equipment
2042, STANDARD SIZE PTACS AND
DOE believes that the standards it is
PTHPS
adopting today will not lessen the
utility or performance of any PTAC or
PTHP because of the steps DOE has
taken to establish product classes and
Trial standard level
evaluate design options and the impact
of potential standard levels, as indicated
PTACs PTHPs in section V.B.4 of the NOPR. 73 FR
18900. DOE stated in the NOPR, it was
1 ........................................
14
27 concerned about the potential
2 ........................................
14
56 misclassification of a portion of the non3 ........................................
31
56 standard size market if the delineations
A .......................................
20
71 within ASHRAE Standard 90.1–1999
4 ........................................
14
82 were adopted by DOE. 73 FR 18865.
5 ........................................
56
82 DOE has mitigated non-standard
6 ........................................
86
104
manufacturers’ concerns by adopting
the delineations within Addendum t to
TABLE V.25—NET NATIONAL CHANGE ASHRAE Standard 90.1–2007 for
IN INDIRECT EMPLOYMENT, JOBS IN distinguishing various sleeve size
2042, NON-STANDARD SIZE PTACS equipment.
5. Impact of Any Lessening of
AND PTHPS
Competition
Net national
change in jobs
(number of
jobs)
Net national
change in jobs
(number of
jobs)
Trial standard level
PTACs
1
2
3
4
5
PTHPs
3
3
6
3
9
5
6
6
11
11
........................................
........................................
........................................
........................................
........................................
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As discussed in the NOPR, 73 FR
18865, 18900, and in section III.D.5 of
this notice, DOE considered any
lessening of competition likely to result
from standards. The Attorney General
determines the impact of any such
lessening of competition.
In its comment on the NOPR, DOJ
expressed concerns about whether the
proposed standards would adversely
affect competition. In particular, DOJ
stated its belief that the efficiency levels
for non-standard size PTACs and PTHPs
in the NOPR may create a risk that is too
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
strict for the manufacturers to satisfy
given the state of the technology. DOJ
further commented that non-standard
customers could face the choice of
incurring capital expenditures to alter
the size of the wall opening to
accommodate standard size PTACs and
PTHPs if non-standard size units
become unavailable. DOJ also stated its
concerns regarding the efficiency levels
for standard size PTHPs proposed in the
NOPR, arguing the proposed levels
would be too stringent for the
manufacturers to achieve. (DOJ, No. 21
at p. 1–2) The Attorney General’s
response is reprinted at the end of
today’s rulemaking.
6. Need of the Nation To Conserve
Energy
An improvement in the energy
efficiency of PTACs and PTHPs, where
economically justified, is likely to
improve the security of the Nation’s
energy system by reducing overall
demand for energy, and thus, reducing
the Nation’s reliance on foreign sources
of energy. Reduced demand is also
likely to improve the reliability of the
electricity system, particularly during
peak-load periods. As a measure of this
reduced demand, DOE expects the
amended standards covered under this
rulemaking to eliminate the need for
construction of between approximately
40 megawatts and 196 megawatts of new
power by 2042.
58811
Enhanced energy efficiency also
produces environmental benefits. The
expected energy savings from higher
standards for the products covered by
this rulemaking will reduce the
emissions of air pollutants and
greenhouse gases associated with energy
production and building use of fossil
fuels. Table V.26 and Table V.27 show
cumulative CO2, NOX, and Hg emissions
reductions for standard size and nonstandard size PTACs and PTHPs by TSL
over the rulemaking period. The
expected energy savings from amended
standards will reduce the emissions of
greenhouse gases associated with energy
production, and may reduce the cost of
maintaining nationwide emissions
standards and constraints.
TABLE V.26—SUMMARY OF EMISSIONS REDUCTIONS FOR STANDARD SIZE PTACS AND PTHPS (CUMULATIVE
REDUCTIONS FOR EQUIPMENT SOLD FROM 2012 TO 2042)
Trial standard levels
TSL 1
TSL 2
TSL 3
TSL A
TSL 4
TSL 5
TSL 6
0.20 .................
0.01 to 0.31 .....
0 to 0.007 ........
0.79 .................
0.05 to 1.23 .....
0 to 0.028 ........
1.22.
0.08 to 1.88.
0 to 0.043.
0.88 .................
0.08 to 1.94 .....
0 to 0.031 ........
0.88 .................
0.08 to 1.94 .....
0 to 0.031 ........
1.12.
0.10 to 2.46.
0 to 0.039.
1.68 .................
0.13 to 3.17 .....
0 to 0.059 ........
2.34.
0.18 to 4.34.
0 to 0.082.
Emissions Reductions for PTACs *
CO2 (Mt) ...........
NOX (kt) ............
Hg (t) .................
0.20 .................
0.01 to 0.31 .....
0 to 0.007 ........
0.20 .................
0.01 to 0.31 .....
0 to 0.007 ........
0.45 .................
0.03 to 0.69 .....
0 to 0.016 ........
0.29 .................
0.02 to 0.45 .....
0 to 0.010 ........
Emissions Reductions for PTHPs *
CO2 (Mt) ...........
NOX (kt) ............
Hg (t) .................
0.29 .................
0.03 to 0.63 .....
0 to 0.010 ........
0.61 .................
0.05 to 1.33 .....
0 to 0.021 ........
0.61 .................
0.05 to 1.33 .....
0 to 0.021 ........
0.77 .................
0.07 to 1.68 .....
0 to 0.027 ........
Emissions Reductions for PTACs and PTHPs *
CO2 (Mt) ...........
NOX (kt) ............
Hg (t) .................
0.49 .................
0.04 to 0.94 .....
0 to 0.017 ........
0.81 .................
0.07 to 1.64 .....
0 to 0.028 ........
1.05 .................
0.08 to 2.02 .....
0 to 0.037 ........
1.06 .................
0.09 to 2.13 .....
0 to 0.037 ........
1.09 .................
0.09 to 2.25 .....
0 to 0.038 ........
* Negative values indicate emission increases. Detail may not appear to sum to total due to rounding.
TABLE V.27—SUMMARY OF EMISSIONS REDUCTIONS FOR NON-STANDARD SIZE PTACS AND PTHPS (CUMULATIVE
REDUCTIONS FOR EQUIPMENT SOLD FROM 2012 TO 2042)
Trial standard levels
TSL 1
TSL 2
TSL 3
TSL 4
TSL 5
Emissions Reductions for PTACs *
CO2 (Mt) ....................
NOX (kt) .....................
Hg (t) .........................
0.06 ...........................
0.004 to 0.10 .............
0 to 0.002 ..................
0.06 ...........................
0.004 to 0.10 .............
0 to 0.002 ..................
0.10 ...........................
0.006 to 0.16 .............
0 to 0.004 ..................
0.06 ...........................
0.004 to 0.10 .............
0 to 0.002 ..................
0.16.
0.010 to 0.24.
0 to 0.005.
0.14 ...........................
0.012 to 0.30 .............
0 to 0.005 ..................
0.14.
0.012 to 0.30.
0 to 0.005.
0.20 ...........................
0.016 to 0.40 .............
0 to 0.007 ..................
0.29.
0.022 to 0.55.
0 to 0.010.
Emissions Reductions for PTHPs *
CO2 (Mt) ....................
NOX (kt) .....................
Hg (t) .........................
0.06 ...........................
0.005 to 0.13 .............
0 to 0.002 ..................
0.08 ...........................
0.007 to 0.18 .............
0 to 0.003 ..................
0.08 ...........................
0.007 to 0.18 .............
0 to 0.003 ..................
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Emissions Reductions for PTACs and PTHPs *
CO2 (Mt) ....................
NOX (kt) .....................
Hg (t) .........................
0.12 ...........................
0.009 to 0.23 .............
0 to 0.004 ..................
0.14 ...........................
0.011 to 0.28 .............
0 to 0.005 ..................
0.18 ...........................
0.014 to 0.34 .............
0 to 0.006 ..................
* Negative values indicate emission increases. Detail may not appear to sum to total due to rounding.
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58812
Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
The estimated cumulative CO2, NOX,
and Hg emissions reductions for the
amended energy conservation standards
range up to a maximum of 2.34 Mt for
CO2, 0.04 to 4.34 kt for NOX, and 0 to
0.08 t for Hg for standard size PTACs
and PTHPs over the period from 2012 to
2042. In the Environmental Assessment
(Chapter 16 of the FR TSD), DOE reports
estimated annual changes in CO2, NOX,
and Hg emissions attributable to each
TSL. As discussion in section IV.J of
this final rule, DOE does not report SO2
emissions reduction from power plants
because reductions from an energy
conservation standard would not affect
the overall level of SO2 emissions in the
United States due to the emissions caps
for SO2.
The NEMS–BT modeling assumed
that NOX would be subject to the Clean
Air Interstate Rule (CAIR) issued by the
U.S. Environmental Protection Agency
on March 10, 2005.16 70 FR 25162 (May
12, 2005). On July 11, 2008, the U.S.
Court of Appeals for the District of
Columbia Circuit (D.C. Circuit) issued
its decision in North Carolina v.
Environmental Protection Agency,17 in
which the court vacated the CAIR. 531
F.3d 896 (D.C. Cir. 2008). If left in place,
the CAIR would have permanently
capped emissions of NOX in 28 eastern
States and the District of Columbia. As
with the SO2 emissions cap, a cap on
NOX emissions would have meant that
energy conservation standards are not
likely to have a physical effect on NOX
emissions in States covered by the CAIR
caps. While the caps would have meant
that physical emissions reductions in
those States would not have resulted
from the energy conservation standards
that DOE is amending today, the
standards might have produced an
environmental-related economic impact
in the form of lower prices for emissions
allowance credits, if large enough. DOE
notes that the estimated total reduction
in NOX emissions, including projected
emissions or corresponding allowance
credits in States covered by the CAIR
cap was insignificant and too small to
affect allowance prices for NOX under
the CAIR.
Even though the D.C. Circuit vacated
the CAIR, DOE notes that the D.C.
Circuit left intact EPA’s 1998 NOX SIP
Call rule, which capped seasonal
(summer) NOX emissions from electric
generating units and other sources in 23
jurisdictions and gave those
jurisdictions the option to participate in
a cap and trade program for those
emissions. 63 FR 57356, 57359 (Oct. 27,
16 See
https://www.epa.gov/cleanairinterstaterule/.
No. 05–1244, 2008 WL 2698180 at *1 (DC
Cir. July 11, 2008).
17 Case
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17:58 Oct 06, 2008
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1998).18 DOE notes that the SIP Call rule
may provide a similar, although smaller
in extent, regional cap and may limit
actual reduction in NOX emissions from
revised standards occurring in States
participating in the SIP Call rule.
However, the possibility that the SIP
Call rule may have the same effect as
CAIR is highly uncertain. Therefore,
DOE established a range of NOX
reductions due to the standards being
amended in today’s final rule. DOE’s
low estimate was based on the emission
rate of the cleanest new natural gas
combined-cycle power plant available
for electricity generated based on the
assumption that energy conservation
standards would result in only the
cleanest available fossil-fueled
generation being displaced. DOE used
the emission rate, specified in 0.0341t of
NOX emitted per TWh of electricity
generated, associated with an advanced
natural gas combined-cycle power plant,
as specified by NEMS–BT. To estimate
the reduction in NOX emissions, DOE
multiplied this emission rate by the
reduction in electricity generation due
to the amended energy conservation
standards considered. DOE’s high
estimate of 0.843 t of NOX per TWh was
based on the use of a nationwide NOX
emission rate for all electrical
generation. Use of such an emission rate
assumes that future energy conservation
standards would result in displaced
electrical generation mix that is
equivalent to today’s mix of power
plants (i.e., future power plants
displaced are no cleaner than what are
being used currently to generate
electricity). In addition, under the high
estimate assumption, energy
conservation standards would have
little to no effect on the generation mix.
18 In the NO SIP Call rule, EPA found that
X
sources in the District of Columbia and 22
‘‘upwind’’ states (States) were emitting NOX (an
ozone precursor) at levels that significantly
contributed to ‘‘downwind’’ states not attaining the
ozone NAAQS or at levels that interfered with
states in attainment maintaining the ozone NAAQS.
In an effort to ensure that ‘‘downwind’’ states attain
or continue to attain the ozone NAAQS, EPA
established a region-wide cap for NOX emissions
from certain large combustion sources and set a
NOX emissions budget for each State. Unlike the
cap that CAIR would have established, the NOX SIP
Call Rule’s cap only constrains seasonal (summer
time) emissions. In order to comply with the NOX
SIP Call Rule, States could elect to participate in the
NOX Budget Trading Program. Under the NOX
Budget Trading Program, each emission source is
required to have one allowance for each ton of NOX
emitted during the ozone season. States have
flexibility in how they allocate allowances through
their State Implementation Plans but States must
remain within the EPA-established budget.
Emission sources are allowed to buy, sell and bank
NOX allowances as appropriate. It should be noted
that, on April 16, 2008, EPA determined that
Georgia is no longer subject to the NOX SIP Call
rule. 73 FR 21528 (April 22, 2008).
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Based on AEO2008 for a recent year
(2006) in which no regulatory or nonregulatory measures were in effect to
limit NOX emissions, DOE multiplied
this emission rate by the reduction in
electricity generation due to the
standards considered. The range in NOX
emission changes calculated under
using the low and high estimate
scenarios are shown in Table V.26 and
Table V.27 by TSL. The range of total
NOX emission reductions is from 0.04 to
4.34 tons for the range of TSLs
considered. These changes in NOX
emissions are extremely small, with a
range between 0.0001 and 0.009 percent
of the national base case emissions
forecast by NEMS–BT, depending on the
TSL.
As noted above in section IV.J, with
regard to Hg emissions, DOE is able to
report an estimate of the physical
quantity changes in these emissions
associated with an energy conservation
standard. As opposed to using the
NEMS–BT model, DOE established a
range of Hg rates to estimate the Hg
emissions that could be reduced from
standards. DOE’s low estimate was
based on the assumption that future
standards would displace electrical
generation from natural gas-fired power
plants resulting in an effective emission
rate of zero. The low-end emission rate
is zero because virtually all Hg emitted
from electricity generation is from coalfired power plants. Based on an
emission rate of zero, no emissions
would be reduced from energy
conservation standards. DOE’s high
estimate was based on the use of a
nationwide mercury emission rate from
AEO2008. Because power plant
emission rates are a function of local
regulation, scrubbers, and the mercury
content of coal, it is extremely difficult
to come up with a precise high-end
emission rate. Therefore, DOE believes
the most reasonable estimate is based on
the assumption that all displaced coal
generation would have been emitting at
the average emission rate for coal
generation as specified by AEO2008. As
noted previously, because virtually all
mercury emitted from electricity
generation is from coal-fired power
plants, DOE based the emission rate on
the tons of mercury emitted per TWh of
coal-generated electricity. Based on the
emission rate for a recent year (2006),
DOE derived a high-end emission rate of
0.0255 tons per TWh. To estimate the
reduction in mercury emissions, DOE
multiplied the emission rate by the
reduction in coal-generated electricity
due to the standards considered as
determined in the utility impact
analysis. The estimated changes in Hg
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emissions are shown in Table V.26 and
Table V.27 for both the standard and
non-standard size PTAC and PTHP
equipment for the period from 2012 to
2042. The range of total Hg emission
reductions is from 0 to 0.082 tons for the
range of TSLs considered. These
changes in Hg emissions are extremely
small, with a range between 0 and 0.016
percent of the national base case
emissions forecast by NEMS–BT,
depending on the TSL.
The NEMS–BT model used for today’s
rulemaking could not be used to
estimate Hg emission reductions due to
standards as it assumed that Hg
emissions would be subject to EPA’s
Clean Air Mercury Rule 19 (CAMR),
which would have permanently capped
emissions of mercury for new and
existing coal-fired plants in all States by
2010. Similar to SO2 and NOX, DOE
assumed that under such a system,
energy conservation standards would
have resulted in no physical effect on
these emissions, but might have resulted
in an environmental-related economic
benefit in the form of a lower price for
emissions allowance credits, if large
enough. DOE estimated that the change
in the Hg emissions from energy
conservation standards would not be
large enough to influence allowance
prices under CAMR.
On February 8, 2008, the D.C. Circuit
issued its decision in New Jersey v.
Environmental Protection Agency, 20 in
which the D.C. Circuit, among other
actions, vacated the CAMR referenced
above. In light of this development and
because the NEMS–BT model could not
be used to directly calculate the Hg
emission reductions, DOE used the
current Hg emission rates as discussed
above to calculate the reductions in Hg
emissions in Table V.26 and Table V.27.
In the NOPR, DOE stated that it was
considering taking into account a
monetary benefit of CO2 emission
reductions associated with this
rulemaking. To put the potential
monetary benefits from reduced CO2
emissions into a form that is likely to be
most useful to decisionmakers and
stakeholders, DOE used the same
methods used to calculate the net
present value of consumer cost savings:
The estimated year-by-year reductions
in CO2 emissions were converted into
monetary values and these resulting
annual values were then discounted
over the life of the affected appliances
to the present using both 3 percent and
7 percent discount rates.
19 70
FR 28606 (May 18, 2005).
05–1097, 2008 WL 341338, at * (DC Cir.
Feb. 9, 2008),
20 No.
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In the NOPR, DOE proposed to use
the range $0 to $14 per ton. These
estimates were based on an assumption
of no benefit to an average benefit value
reported by the IPCC.21 It is important
to note that the IPCC estimate used as
the upper bound value was derived
from an estimate of the mean value of
worldwide impacts from potential
climate impacts caused by CO2
emissions, and not just the effects likely
to occur within the United States. As
DOE considers a monetary value for CO2
emission reductions, the value should
be restricted to a representation of those
costs/benefits likely to be experienced
in the United States. As DOE also
explained in the NOPR, it expects that
such values would be lower than
comparable global values, however,
there currently are no consensus
estimates for the U.S. benefits likely to
result from CO2 emission reductions.
However, DOE believes it is appropriate
to use U.S. benefit values, where
available, and not world benefit values,
in its analysis.22 Because U.S. specific
estimates are not available, and DOE did
not receive any additional information
that would help serve to narrow the
proposed range as a representative range
for domestic U.S. benefits, DOE believes
it is appropriate to use the global mean
value as an appropriate upper bound
U.S. value for purposes of sensitivity
analysis.
DOE received several comments in
response to the proposed estimated
value of CO2 emissions reductions.
EarthJustice questioned both the upper
and lower bounds of DOE’s range of
21 During the preparation of its most recent
review of the state of climate science, the
Intergovernmental Panel on Climate Change (IPCC)
identified various estimates of the present value of
reducing carbon-dioxide emissions by one ton over
the life that these emissions would remain in the
atmosphere. The estimates reviewed by the IPCC
spanned a range of values. In the absence of a
consensus on any single estimate of the monetary
value of CO2 emissions, DOE used the estimates
identified by the study cited in Summary for
Policymakers prepared by Working Group II of the
IPCC’s Fourth Assessment Report to estimate the
potential monetary value of CO2 reductions likely
to result from standards finalized in this
rulemaking. According to IPCC, the mean social
cost of carbon (SCC) reported in studies published
in peer-reviewed journals was $43 per ton of
carbon. This translates into about $12 per ton of
carbon dioxide. The literature review (Tol 2005)
from which this mean was derived did not report
the year in which these dollars were denominated.
However, we understand this estimate was
denominated in 1995 dollars. Updating that
estimate to 2007 dollars yields a SCC of $15 per ton
of carbon dioxide.
22 In contrast, most of the estimates of costs and
benefits of increasing the efficiency of PTACs and
PTHPs include only economic values of impacts
that would be experienced in the U.S. For example,
in determining impacts on manufacturers, DOE
generally does not consider impacts that occur
solely outside of the United States.
PO 00000
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58813
estimated CO2 values, both of which
EarthJustice argued were too low.
EarthJustice also stated that it would be
inappropriate to limit the consideration
to the value of CO2 to a domestic value.
EarthJustice and the joint comment from
ACEE and the Natural Resource Defense
Council recommended that DOE
consider relying on the estimate used in
DOE’s analysis of the America’s Climate
Security Bill of 2007 (S. 2191).23 AHRI
commented that DOE should not rely on
the IPCC study or values under the
European Union ‘‘cap and trade’’
program, but instead should consider a
monetary value for CO2 only once a U.S.
‘‘cap and trade’’ program has been
established, stressing that DOE should
consider only the domestic value of CO2
emissions.
Given the uncertainty surrounding
estimates of the SCC, relying on any
single study may be inadvisable since
its estimate of the SCC will depend on
many assumptions made by its authors.
The Working Group II’s contribution to
the Fourth Assessment Report of the
IPCC notes that:
The large ranges of SCC are due in the large
part to differences in assumptions regarding
climate sensitivity, response lags, the
treatment of risk and equity, economic and
non-economic impacts, the inclusion of
potentially catastrophic losses, and discount
rates.24
Because of this uncertainty, DOE relied
on Tol (2005), which was presented in
the IPCC’s Fourth Assessment Report,
and was a comprehensive meta-analysis
of estimates for the value of SCC.
Commenters did not provide a rationale
for why it would be more accurate or
reliable for DOE to use values based on
the limited number of studies they
cited. As a result, DOE continues to rely
on the Tol study reported by the IPCC
as the basis for its analysis.
DOE continues to believe that the
most appropriate monetary values for
consideration in the development of
efficiency standards are those drawn
from studies that attempt to estimate the
present value of the marginal economic
benefits likely to result from reducing
greenhouse gas emissions, rather than
estimates that are based on the market
23 EarthJustice, ACEEE, and the Natural Resource
Defense Council noted that the analysis of the
America’s Climate Security Bill of 2007, used a
value of $17 per ton of CO2 with a 7.4 percent
annual growth rate. EarthJustice also cited a study
by the United Kingdom’s Department for
Environment, Food, and Rural Affairs, which
recommended valuing carbon emissions at just over
$25 per ton of CO2.
24 Climate Change 2007—Impacts, Adaption and
Vulnerability Contribution of Working Group II to
the Fourth Assessment Report of the IPCC, 17.
Available at https://www.ipcc-wg2.org (last accessed
Aug. 7, 2008).
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
value of emission allowances under
existing cap and trade programs or
estimates that are based on the cost of
reducing emissions—both of which are
largely determined by policy decisions
that set the timing and extent of
emission reductions and do not
necessarily reflect the benefit of
reductions. DOE also believes that the
studies it relies upon generally should
be studies that were the subject of a peer
review process and were published in
reputable journals.
In today’s final rule, DOE is
essentially relying on the range of
values proposed in the NOPR, which
was based on the values presented in
Tol (2005), as proposed. However, DOE
notes that in the proposed rule, DOE
mistakenly assumed that the values
presented in Tol (2005) were in 2000
dollars. In actuality, the values in Tol
(2005) were indicated to be
approximately 1995 values in 1995
dollars. Had DOE, at the NOPR stage,
applied the correct dollar year of the
values presented in Tol (2005), DOE
would have proposed the range of $0 to
$15 in the NOPR. Additionally, DOE has
applied an annual growth rate of 2.4%
to the value of SCC, as suggested by the
IPCC Working Group II (2007, p. 822),
based on estimated increases in
damages from future emissions reported
in published studies. As a result, for
today’s final rule, DOE is assigning a
range for the SCC of $0 to $20 ($2007)
per ton of CO2 emissions.
EarthJustice questioned the use of the
median estimated social cost of CO2 as
an upper bound of the range. However,
the upper bound of the range used by
DOE is based on Tol (2005), which
reviewed 103 estimates of the SCC from
28 published studies, and concluded
that when only peer-reviewed studies
published in recognized journals are
considered, ‘‘that climate change
impacts may be very uncertain but [it]
is unlikely that the marginal damage
costs of carbon dioxide emissions
exceed $50 per ton carbon [comparable
to a 2007 value of $20 per ton carbon
dioxide when expressed in 2007 U.S.
dollars with a 2.4% growth rate.]’’
EarthJustice also questioned the use of
$0 as the lower bound of DOE’s
estimated range. In setting a lower
bound, DOE agrees with the IPCC
Working Group II (2007) report that
‘‘significant warming across the globe
and the locations of significant observed
changes in many systems consistent
with warming is very unlikely to be due
solely to natural variability of
temperatures or natural variability of the
systems’’ (pp. 9), and thus tentatively
concludes that a global value of zero for
reducing emissions cannot be justified.
However, DOE also believes that it is
reasonable to allow for the possibility
that the U.S. portion of the global cost
of carbon dioxide emissions may be
quite low. In fact, some of the studies
looked at in Tol (2005) reported
negative values for the SCC. As stated in
the NOPR, DOE is using U.S. benefit
values, and not world benefit values, in
its analysis and, further, DOE believes
that U.S. domestic values will be lower
than the global values. Additionally, the
statutory criteria in EPCA do not require
consideration of global effects.
Therefore, DOE is using a lower bound
of $0 per ton of CO2 emissions in
estimating the potential benefits of
today’s final rule.
The resulting estimates of the
potential range of net present value
benefits associated with the reduction of
CO2 emissions are reflected in Table
V.28.
TABLE V.28—ESTIMATES OF SAVINGS FROM CO2 EMISSIONS REDUCTIONS UNDER PTAC AND PTHP TRIAL STANDARD
LEVELS AT 7% DISCOUNT RATE AND 3% DISCOUNT RATE
Estimated
cumulative CO2
(Mt) emission
reductions
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DOE also investigated the potential
monetary impact resulting from the
impact of today’s energy conservation
standards on SO2, NOX, and Hg
emissions. As previously stated, DOE’s
initial analysis assumed the presence of
nationwide emission caps on SO2 and
Hg, and caps on NOX emissions in the
28 States covered by the CAIR caps. In
the presence of these caps, DOE
concluded that no physical reductions
in power sector emissions would occur,
but that the lower generation
requirements associated with energy
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Value of estimated CO2
emission reductions (million
2007$) at 3% discount rate
0.49
0.81
1.05
1.06
1.09
1.68
2.34
$0
$0
$0
$0
$0
$0
$0
to
to
to
to
to
to
to
$4.8 ...........................
$8.0 ...........................
$10.4 .........................
$10.5 .........................
$10.8 .........................
$16.5 .........................
$22.9 .........................
$0
$0
$0
$0
$0
$0
$0
to
to
to
to
to
to
to
$9.0.
$14.9.
$19.4.
$19.5.
$20.0.
$30.9.
$43.0.
0.12
0.14
0.18
0.20
0.29
Standard Size TSL:
1 ............................................................................................
2 ............................................................................................
3 ............................................................................................
A ...........................................................................................
4 ............................................................................................
5 ............................................................................................
6 ............................................................................................
Non-Standard Size TSL:
1 ............................................................................................
2 ............................................................................................
3 ............................................................................................
4 ............................................................................................
5 ............................................................................................
Value of estimated CO2
emission reductions (million
2007$) at 7% discount rate
$0
$0
$0
$0
$0
to
to
to
to
to
$1.2
$1.4
$1.8
$2.0
$2.9
$0
$0
$0
$0
$0
to
to
to
to
to
$2.2.
$2.7.
$3.4.
$3.7.
$5.4.
conservation standards could
potentially put downward pressure on
the prices of emissions allowances in
cap-and-trade markets. Estimating this
effect is very difficult because of the
factors such as credit banking, which
can change the trajectory of prices. DOE
has further concluded that the effect
from energy conservation standards on
SO2 allowance prices is likely to be
negligible, based upon runs of the
NEMS–BT model. See Chapter 16
(Environmental Assessment) of the FR
TSD for further details.
PO 00000
Frm 00044
Fmt 4701
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...........................
...........................
...........................
...........................
...........................
As discussed earlier, with respect to
NOX the CAIR rule has been vacated by
the courts, so projected annual NOX
allowances from NEMS–BT are no
longer relevant. In DOE’s subsequent
analysis, NOX emissions are not
controlled by a nationwide regulatory
system. For the range of NOX reduction
estimates (and Hg reduction estimates),
DOE estimated the national monetized
benefits of emissions reductions from
today’s rule based on environmental
damage estimates from the literature.
Available estimates suggest a very wide
E:\FR\FM\07OCR3.SGM
07OCR3
Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
range of monetary values for NOX
emissions, ranging from $370 per ton to
$3,800 per ton of NOX from stationary
sources, measured in 2001 dollars 25 or
a range of $432 per ton to $4,441 per ton
in 2007 dollars.
DOE has already conducted research
for today’s final rule and determined
that the basic science linking mercury
emissions from power plants to impacts
on humans is considered highly
uncertain. However, DOE identified two
estimates of the environmental damages
of mercury based on two estimates of
58815
$664,000 per ton emitted in 2004$ or
$729,000 per ton in 2007$), which DOE
derived from a published evaluation of
mercury control using different methods
and assumptions from the first study,
but also based on the present value of
the lifetime earnings of children
exposed.27 The resulting estimates of
the potential range of the present value
benefits associated with the national
reduction of NOX and national
reductions in Hg emissions are reflected
in Table V.29 and Table V.30.
the adverse impact of childhood
exposure to methyl mercury on IQ for
American children, and subsequent loss
of lifetime economic productivity
resulting from these IQ losses. The high
end 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 ($1.3 billion per year in
year 2000$), which works out to $32.6
million per ton emitted per year
(2007$).26 The low-end estimate was
TABLE V.29—ESTIMATES OF SAVINGS FROM REDUCTIONS OF NOX AND HG UNDER PTAC AND PTHP TRIAL STANDARD
LEVELS AT A 7% DISCOUNT RATE
Estimated cumulative
NOX (kt) emission reductions *
Standard Size TSL:
1 .........................................
2 .........................................
3 .........................................
A ........................................
4 .........................................
5 .........................................
6 .........................................
Non-Standard Size TSL:
1 .........................................
2 .........................................
3 .........................................
4 .........................................
5 .........................................
Value of estimated NOX
emission reductions
(thousand 2007$)
Estimated cumulative Hg
(tons) emission
reductions*
Value of estimated Hg
emission reductions
(thousand 2007$)
0.04
0.07
0.08
0.09
0.09
0.13
0.18
to
to
to
to
to
to
to
0.94
1.64
2.02
2.13
2.25
3.17
4.34
.....................
.....................
.....................
.....................
.....................
.....................
.....................
$4 to $1,091 ....................
$7 to $1,892 ....................
$9 to $2,335 ....................
$10 to $2,462 ..................
$10 to $2,599 ..................
$14 to $3,658 ..................
$20 to $5,014 ..................
0
0
0
0
0
0
0
to
to
to
to
to
to
to
0.017
0.028
0.037
0.037
0.038
0.059
0.082
........................
........................
........................
........................
........................
........................
........................
$0
$0
$0
$0
$0
$0
$0
to
to
to
to
to
to
to
$182.
$299.
$392.
$393.
$403.
$624.
$871.
0.01
0.01
0.01
0.02
0.02
to
to
to
to
to
0.23
0.28
0.34
0.40
0.55
.....................
.....................
.....................
.....................
.....................
$1
$1
$2
$2
$2
0
0
0
0
0
to
to
to
to
to
0.004
0.005
0.006
0.007
0.010
........................
........................
........................
........................
........................
$0
$0
$0
$0
$0
to
to
to
to
to
$45.
$54.
$69.
$75.
$110.
to
to
to
to
to
$263
$319
$390
$463
$631
.......................
.......................
.......................
.......................
.......................
* Values in Table V.32 may not appear to sum to the cumulative values in Table V.26 due to rounding.
TABLE V.30—ESTIMATES OF SAVINGS FROM REDUCTIONS OF NOX AND HG UNDER PTAC AND PTHP TRIAL STANDARD
LEVELS AT A 3% DISCOUNT RATE
Estimated cumulative
NOX (kt) emission
reductions *
Standard Size TSL:
1 .........................................
2 .........................................
3 .........................................
A ........................................
4 .........................................
5 .........................................
6 .........................................
Non-Standard Size TSL:
1 .........................................
2 .........................................
3 .........................................
4 .........................................
5 .........................................
Value of estimated NOX
emission reductions
(thousand 2007$)
Estimated cumulative Hg
(tons) emission
reductions *
Value of estimated Hg
emission reductions
(thousand 2007$)
0.04
0.07
0.08
0.09
0.09
0.13
0.18
to
to
to
to
to
to
to
0.94
1.64
2.02
2.13
2.25
3.17
4.34
.....................
.....................
.....................
.....................
.....................
.....................
.....................
$9 to $2,250 ....................
$15 to $3,903 ..................
$19 to $4,815 ..................
$20 to $5,079 ..................
$21 to $5,362 ..................
$30 to $7,545 ..................
$41 to $10,341 ................
0
0
0
0
0
0
0
to
to
to
to
to
to
to
0.017
0.028
0.037
0.037
0.038
0.059
0.082
........................
........................
........................
........................
........................
........................
........................
$0
$0
$0
$0
$0
$0
$0
to
to
to
to
to
to
to
$331.
$544.
$712
$714.
$732.
$1,135.
$1,582.
0.01
0.01
0.01
0.02
0.02
to
to
to
to
to
0.23
0.28
0.34
0.40
0.55
.....................
.....................
.....................
.....................
.....................
$2
$3
$3
$4
$5
0
0
0
0
0
to
to
to
to
to
0.004
0.005
0.006
0.007
0.010
........................
........................
........................
........................
........................
$0
$0
$0
$0
$0
to
to
to
to
to
$83.
$98.
$125.
$136.
$200.
to
to
to
to
to
$542 .......................
$659 .......................
$805 .......................
$954 .......................
$1,301 ....................
pwalker on PROD1PC71 with RULES3
* Values in Table V.33 may not appear to sum to the cumulative values in Table V.26 due to rounding.
25 2006 Report to Congress on the Costs and
Benefits of Federal Regulations and Unfunded
Mandates on State, Local, and Tribal Entities. Office
of Management and Budget Office of Information
and Regulatory Affairs, Washington, DC.
VerDate Aug<31>2005
17:58 Oct 06, 2008
Jkt 217001
26 Trasande, L., et al., ‘‘Applying Cost Analyses to
Drive Policy that Protects Children’’ 1076 ANN.
N.Y. ACAD. SCI. 911 (2006).
27 Ted Gayer and Robert Hahn, Designing
Environmental Policy: Lessons from the Regulation
of Mercury Emissions, Regulatory Analysis 05–01.
AEI-Brookings Joint Center For Regulatory Studies,
PO 00000
Frm 00045
Fmt 4701
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Washington, DC, 31 pp., 2004. A version of this
paper was published in the Journal of Regulatory
Economics in 2006. The estimate was derived by
back-calculating the annual benefits per ton from
the net present value of benefits reported in the
study.
E:\FR\FM\07OCR3.SGM
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58816
Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
7. Other Factors
In developing today’s standards, the
Secretary took into consideration: (1)
The impacts of setting different
amended standards for PTACs and
PTHPs; (2) the potential that amended
standards could cause equipment
switching (i.e., purchase of PTACs
instead of PTHPs) and the effects of any
such switching; (3) the uncertainties
associated with the impending phaseout
in 2010 of R–22 refrigerant; and (4) the
impact of amended standards on the
manufacturers of and market for nonstandard size packaged terminal
equipment (e.g., impacts on small
businesses). To address the impact of
setting different amended energy
conservation standards for PTACs and
PTHPs and the potential that amended
energy conservation standards could
cause equipment switching, DOE
conducted a sensitivity analysis. The
results of the sensitivity analysis are
shown in section V.B. DOE discusses
the uncertainties associated with the
impending refrigerant phaseout in 2010
of R–22 refrigerant and the impact of
amended energy conservation standards
on the non-standard size industry in the
conclusion section below.
D. Conclusion
EPCA contains criteria for prescribing
new or amended energy conservation
standards. For commercial HVAC and
water heating equipment such as PTACs
and PTHPs, DOE must adopt as national
standards the levels in amendments to
ASHRAE Standard 90.1 unless DOE
determines, ‘‘supported by clear and
convincing evidence,’’ that standards
more stringent than those levels ‘‘would
result in significant additional
conservation of energy and [be]
technologically feasible and
economically justified.’’ (42 U.S.C.
6313(a)(6)(A)(ii)(II)) Any more stringent
standard must be designed to achieve
the maximum improvement in energy
efficiency and be technologically
feasible and economically justified. (42
U.S.C. 6316(a); 42 U.S.C. 6295(o)(2)(A))
Moreover, in determining whether an
energy conservation standard is
economically justified, DOE must weigh
all seven factors specified in EPCA, and
set forth above, to determine whether
the benefits of the standard exceed its
costs. (42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i))
In this rulemaking, DOE has evaluated
whether standards more stringent than
the efficiency levels in ASHRAE
Standard 90.1–1999 for PTACs and
PTHPs are justified under the above
criteria. As stated in sections III.B.1 and
C, DOE determined, based on clear and
convincing evidence, that all of the
more stringent standard levels
considered in this rulemaking are
technologically feasible and would save
significant additional amounts of
energy. To determine if these more
stringent TSLs are economically
justified, DOE compared the maximum
technologically feasible levels with the
base case, and determined whether
those levels are economically justified.
Upon finding the maximum
technologically feasible levels not to be
justified, DOE analyzed the next lower
TSL to determine whether that level was
economically justified. DOE repeated
this procedure until it identified a TSL
that was economically justified.
In the NOPR, DOE weighed the
benefits and burdens for standard size
and non-standard size PTACs and
PTHPs through TSL 1 through 7. In
response to both the uniqueness of the
two separate industries and comments
from interested parties on the potential
impacts of standards on the standard
size and non-standard size equipment,
DOE weighed the benefits and burdens
separately in today’s final rule.
In addition to the quantitative results,
DOE also considered other factors that
might affect economic justification. DOE
took into consideration the EPAmandated refrigerant phaseout and its
effect on PTAC and PTHP equipment
efficiency, which concern both standard
size and non-standard size PTACs and
PTHPs. In addition, DOE considered the
uniqueness of the PTAC and PTHP
industry with its substantial number of
manufacturers of non-standard size
equipment. In particular, DOE
considered the declining shipments of
non-standard size equipment, the small
size segment of the industry (both
relative to the rest of the PTAC and
PTHP industry and in absolute terms),
and the small businesses that could be
affected by amended energy
conservation standards.
1. Standard Size PTACs and PTHPs
Table V.31 summarizes DOE’s
quantitative analysis results for each
TSL it considered for standard size
PTACs and PTHPs in this final rule.
This table presents the results or, in
some cases a range of results, for each
TSL, and will aid the reader in the
discussion of costs and benefits of each
TSL. The range of values for industry
impacts represents the results for the
different markup scenarios that DOE
used to estimate manufacturer impacts.
TABLE V.31—SUMMARY OF RESULTS FOR STANDARD SIZE PTACS AND PTHPS BASED UPON THE AEO2008 ENERGY
PRICE FORECAST *
pwalker on PROD1PC71 with RULES3
TSL 1
Primary energy saved
(quads) .....................
7% Discount rate
(Standard Size)
3% Discount rate
(Standard Size)
Generation capacity reduction (GW) (Standard Size) ** ................
NPV (2007$ million)
(Standard Size):
7% Discount rate ..
3% Discount rate ..
Industry impacts
(Standard Size):
Industry NPV
(2007$ million) ...
Industry NPV (%
Change) .............
VerDate Aug<31>2005
17:58 Oct 06, 2008
TSL 2
TSL 3
TSL A
TSL 4
TSL 5
TSL 6
0.015
0.024
0.031
0.032
0.033
0.049
0.068
0.003
0.006
0.007
0.007
0.008
0.011
0.015
0.007
0.012
0.016
0.016
0.017
0.025
0.035
(0.040)
(0.062)
(0.086)
(0.082)
(0.082)
(0.139)
(0.196)
1
17
8
43
2
38
10
54
6
49
(11)
31
(41)
(10)
(3)–(28)
(6)–(45)
(3)–(60)
(8)–(61)
(8)–(68)
(1)–(103)
(4)–(164)
(0.8)–(7)
(1)–(11)
(0.8)–(14)
(2)–(14)
(2)–(16)
(0.2)–(24)
(0.9)–(38)
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
58817
TABLE V.31—SUMMARY OF RESULTS FOR STANDARD SIZE PTACS AND PTHPS BASED UPON THE AEO2008 ENERGY
PRICE FORECAST *—Continued
pwalker on PROD1PC71 with RULES3
TSL 1
Cumulative emissions
impacts (Standard
Size) †:
CO2 (Mt) ................
NOX (kt) ................
Hg (t) .....................
Employment Impacts
(Standard Size):
Indirect Employment Impacts .....
Direct, Domestic
Employment Impacts ..................
Mean LCC savings
(2007$) (Standard
Size) *:
Standard Size
PTAC, 9,000
Btu/h ..................
Standard Size
PTHP, 9,000
Btu/h ..................
Standard Size
PTAC, 12,000
Btu/h ..................
Standard Size
PTHP, 12,000
Btu/h ..................
Mean PBP (years)
(Standard Size):
Standard Size
PTAC, 9,000
Btu/h ..................
Standard Size
PTHP, 9,000
Btu/h ..................
Standard Size
PTAC, 12,000
Btu/h ..................
Standard Size
PTHP, 12,000
Btu/h ..................
LCC Results (Standard
Size):
Standard Size
PTAC, 9,000
Btu/h.
Net Cost (%) ..
No Impact (%)
Net Benefit
(%) ..............
Standard Size
PTHP, 9,000
Btu/h.
Net Cost (%) ..
No Impact (%)
Net Benefit
(%) ..............
Standard Size
PTAC, 12,000
Btu/h.
Net Cost (%) ..
No Impact (%)
Net Benefit
(%) ..............
Standard Size
PTHP, 12,000
Btu/h.
Net Cost (%) ..
No Impact (%)
VerDate Aug<31>2005
TSL 2
TSL 3
TSL A
TSL 4
TSL 5
TSL 6
(0.49)
(0.04)–(0.94)
0–(0.017)
(0.81)
(0.07)–(1.64)
0–(0.028)
(1.05)
(0.08)–(2.02)
0–(0.037)
(1.06)
(0.09)–(2.13)
0–(0.037)
(1.09)
(0.09)–(2.25)
0–(0.038)
(1.68)
(0.13)–(3.17)
0–(0.059)
(2.34)
(0.18)–(4.34)
0–(0.082)
41
70
87
91
96
138
190
1
2
3
3
3
6
9
(1)
(1)
(3)
(3)
(1)
(6)
(10)
11
20
20
28
28
28
24
(2)
(2)
(5)
(2)
(2)
(10)
(15)
13
24
24
24
20
20
14
13.0
13.0
13.7
13.7
13.0
14.5
15.2
5.1
4.5
4.5
4.4
4.4
4.4
5.1
13.1
13.1
14.0
13.1
13.1
14.9
15.9
5.1
4.6
4.6
4.6
5.5
5.5
6.4
15%
77%
15%
77%
30%
56%
30%
56%
15%
77%
46%
37%
62%
18%
7%
7%
14%
14%
7%
17%
21%
7%
78%
10%
57%
10%
57%
13%
37%
13%
37%
13%
37%
24%
18%
16%
33%
33%
50%
50%
50%
58%
16%
77%
16%
77%
31%
56%
16%
77%
16%
77%
48%
36%
65%
18%
7%
7%
13%
7%
7%
16%
17%
7%
77%
10%
57%
10%
57%
10%
57%
21%
37%
21%
37%
35%
18%
17:58 Oct 06, 2008
Jkt 217001
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58818
Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
TABLE V.31—SUMMARY OF RESULTS FOR STANDARD SIZE PTACS AND PTHPS BASED UPON THE AEO2008 ENERGY
PRICE FORECAST *—Continued
TSL 1
Net Benefit
(%) ..............
TSL 2
16%
TSL 3
33%
TSL A
33%
TSL 4
33%
TSL 5
42%
TSL 6
42%
47%
pwalker on PROD1PC71 with RULES3
* Parentheses indicate negative values. For LCCs, a negative value means an increase in LCC by the amount indicated.
** Change in installed generation capacity by the year 2042 based on AEO 2008 Reference Case.
† CO emissions impacts are physical reductions from all sources. NO and Hg emissions impacts are physical reductions at power plants.
2
X
First, DOE considered TSL 6, the maxtech efficiency level for standard size
PTACs and PTHPs. TSL 6 would likely
save 0.068 quads of energy through 2042
for standard size PTACs and PTHPs, an
amount DOE considers significant.
Discounted at seven percent, the
projected energy savings through 2042
would be 0.015 quads. For the Nation as
a whole, DOE projects that TSL 6 would
result in a net decrease of $41 million
in NPV for standard size PTACs and
PTHPs, using a discount rate of seven
percent and a net decrease of $10
million for standard size PTACs and
PTHPs, using a discount rate of three
percent. The emissions reductions at
TSL 6 for standard size PTACs and
PTHPs are 2.34 Mt of CO2, between 0.18
kt and 4.34 kt of NOX, and between zero
and 0.082 t of Hg. Total generating
capacity needed in 2042 is estimated to
decrease compared to the reference case
by 0.196 gigawatts (GW) under TSL 6.
At TSL 6, DOE projects that the
average PTAC customer will experience
an increase in LCC for all standard size
equipment classes. Purchasers of
standard size PTACs are projected to
lose on average ¥$12 (2007$) over the
life of the product, and purchasers of
standard size PTHPs would save on
average $20 (2007$). DOE estimates LCC
increases for 63 percent of customers in
the Nation who purchase a standard size
PTAC, and for 29 percent of customers
in the Nation who purchase a standard
size PTHP. The mean payback period of
each standard size PTAC equipment
class at TSL 6 is projected to be
substantially longer than the mean
lifetime of the equipment.
The projected change in the standard
size industry value (INPV) ranges from
a decrease of $4 million to a decrease of
$164 million, in 2007$. For standard
size PTACs and PTHPs, the impacts are
driven primarily by the assumptions
regarding the ability to pass on larger
increases in MPCs to the customer.
Currently, there are equipment lines
being manufactured with efficiency
levels above TSL 6 utilizing R–22
refrigerant. Using the degradations
estimated in the engineering analysis,
DOE believes standard size equipment
could be produced at TSL 6 in the lower
VerDate Aug<31>2005
17:58 Oct 06, 2008
Jkt 217001
range of cooling capacities. DOE
believes manufacturers would not be
able to manufacture standard size
PTACs and PTHPs at TSL 6 at the high
range of the cooling capacities (e.g.,
15,000 Btu/h) within a given equipment
class (i.e., standard size PTACs with a
cooling capacity greater than or equal to
7,000 Btu/h and less than or equal to
15,000 Btu/h). DOE has not initially
been able to identify technologies and
design approaches for R–410A units to
meet these higher levels in the absence
of the availability of high efficiency
compressors spanning the full range of
cooling capacities. At TSL 6, 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 6 could result in a net loss
of 38.3 percent in INPV to the standard
size PTAC and PTHP industry.
After carefully considering the
analysis and weighing the benefits and
burdens of TSL 6, the Secretary has
concluded that at TSL 6, even if
manufacturers could overcome the
barriers to produce R–410 equipment in
the full range of cooling capacities by
the effective date of an amended energy
conservation standard, the benefits of
energy savings and emissions
reductions would be outweighed by the
potential multi-million dollar negative
net economic cost to the Nation, the
economic burden on consumers, and the
large capital conversion costs that could
result in a reduction in INPV for
manufacturers.
Next, DOE considered TSL 5. Primary
energy savings is estimated at 0.049
quads of energy through 2042 for
standard size PTACs and PTHPs, which
DOE considers significant. Discounted
at seven percent, the energy savings
through 2042 would be 0.011 quads. For
the Nation as a whole, DOE projects that
TSL 5 would result in a net decrease of
$11 million in NPV for standard size
PTACs and PTHPs, using a discount rate
of seven percent and an increase of $31
million for standard size PTACs and
PTHPs, using a discount rate of three
percent. The emissions reductions are
projected to be 1.68 Mt of CO2, between
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Fmt 4701
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0.013 kt and 3.17 kt of NOX and
between 0 and 0.082 t of Hg. Total
generating capacity needed in 2042
under TSL 5 is estimated to decrease by
0.139 GW for standard size PTACs and
PTHPs.
At TSL 5, DOE found the impacts of
amended energy conservation standards
on customers of PTACs would likely
differ significantly from their impacts
on PTHP customers. While only 16
percent of customers of standard size
PTHPs would likely have an LCC
increase at TSL 5, 47 percent of
customers of standard size PTACs
would experience an LCC increase at
this TSL. A customer for a standard size
PTAC, on average, would experience an
increase in LCC of $8, while the
customer for a standard size PTHP, on
average, would experience a decrease in
LCC of $25. At TSL 5, DOE projects that
the average PTAC customer for a
standard size PTAC will experience an
increase in LCC in each equipment
class. In addition, the mean payback
period of each standard size PTAC
equipment class at TSL 5 is projected to
be substantially longer than the mean
lifetime.
At TSL 5, the projected change in
INPV ranges between losses of $1
million and $103 million. For
manufacturers of standard size
equipment alone, DOE estimated a
decrease in the INPV to range from 0.2
percent to 24.0 percent. The magnitude
of projected impacts is still largely
determined, however, by the
manufacturers’ ability to pass on larger
increases in MPC to the customer. Thus,
the potential INPV decrease of $103
million assumes that DOE’s projections
of partial cost recovery as described in
Chapter 13 of the TSD remain valid. In
addition, at TSL 5 the impending
refrigerant phaseout could also have a
significant impact on manufacturers.
Currently, both standard size PTACs
and PTHPs using R–22 refrigerant are
available on the market at and above
TSL 5 efficiency levels. However, at the
performance degradations that DOE
estimated in the engineering analysis for
R–410A equipment, manufacturers
would be unable to produce R–410A
equipment at these levels unless high
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efficiency R–410A compressors become
available. The absence of such
compressors would likely mean that the
negative financial impacts of TSL 5
would be greater than characterized by
DOE’s MIA analysis. Even though the
ability of manufacturers to produce
equipment utilizing R–410A is greater at
TSL 5 than at TSL 6, DOE anticipates
that manufacturers would not be able to
produce standard size PTACs and
PTHPs at TSL 5 in the full range of
capacities available today due to the
physical size constraints imposed by the
wall sleeve dimensions.
While DOE recognizes the increased
economic benefits to the nation that
could result from TSL 5 for standard
size PTACs and PTHPs, DOE concludes
that the benefits of a Federal standard at
TSL 5 would still be outweighed by the
economic burden that would be placed
upon PTAC customers. In addition, DOE
believes at TSL 5, the benefits of energy
savings and emissions impacts would be
outweighed by the large impacts on
standard size manufacturers’ INPV.
Finally, DOE is concerned that standard
size manufacturers may be unable to
offer the full capacity range of
equipment utilizing R–410A by the
effective date of the amended energy
conservation standards.
Next, DOE considered TSL 4. For TSL
4, DOE combined the efficiency levels
in TSL 1 for PTACs and the efficiency
levels in TSL 5 for PTHPs. This
combination of efficiency levels serves
to maximize LCC savings, while
recognizing the differences in LCC
results for standard size PTACs and
PTHPs. DOE projects that TSL 4 for
standard size PTACs and PTHPs would
save 0.033 quads of energy through
2042, an amount DOE considers
significant. Discounted at seven percent,
the projected energy savings through
2042 would be 0.008 quads. For the
Nation as a whole, DOE projects that
TSL 4 would result in net savings in
NPV of $6 million for standard size
PTACs and PTHPs, using a discount rate
of seven percent, and $49 million for
standard size PTACs and PTHPs, using
a discount rate of three percent. The
estimated emissions reductions are 1.09
Mt of CO2, between 0.09 kt and 2.25 kt
of NOX, and between 0 and 0.038 t of
Hg. Total generating capacity needed in
2042 under TSL 4 would likely decrease
by 0.082 GW.
At TSL 4, DOE projects that the
average PTAC or PTHP customer would
experience LCC savings. Purchasers of
standard size PTACs, on average, have
LCC increase of $2 (2007$) over the life
of the product and purchasers of PTHPs
would save on average $25 (2007$).
DOE estimates an LCC increase for 15
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percent of customers in the Nation who
purchase a standard size PTAC, and for
16 percent of customers in the Nation
who purchase a standard size PTHP. For
standard size PTACs and PTHPs, the
remainder of customers would
experience either a decrease or no
change in LCC. DOE also projects that
the mean payback period of each
standard size PTAC equipment class at
TSL 4 would be substantially longer
than the mean lifetime of the
equipment.
The projected change in INPV ranges
between a loss of $8 million and a loss
of $68 million for the standard size
PTAC and PTHP industry. Just as with
TSLs 5 and 6, the projected impacts
continue to be driven primarily by the
manufacturers’ ability to pass on
increases in MPCs to the customer. The
loss of $68 million assumes DOE’s
projections of partial cost recovery as
described in Chapter 13 of the TSD. TSL
4 requires the production of standard
size PTACs at the efficiency levels in
TSL 1 and standard size PTHPs at
efficiency levels at TSL 5. For the larger
cooling capacity range (e.g., 15,000 Btu/
h) of standard size PTACs with cooling
capacities greater than or equal to 7,000
Btu/h and less than or equal to 15,000
Btu/h, DOE believes manufacturers
would not be able to produce equipment
in a given equipment class at the EER
required by the TSL 4 energy-efficiency
equation. Specifically, DOE is
concerned that standard size
manufacturers would be forced to
eliminate larger cooling capacity
equipment due to the stringency of the
standard in the higher cooling capacity
regions.
While DOE recognizes the increased
economic benefits to the nation that
could result from TSL 4 for standard
size PTACs and PTHPs, DOE concludes
that the benefits of a Federal standard at
TSL 4 would still be outweighed by the
economic burden that would be placed
upon PTAC customers. In addition, DOE
believes at TSL 4, the benefits of energy
savings and emissions impacts would be
outweighed by the large impacts on
standard size manufacturers’ INPV.
Finally, DOE is concerned that standard
size manufacturers may be unable to
offer the full capacity range of
equipment utilizing R–410A by the
effective date of the amended energy
conservation standards.
Next, DOE considered TSL A. TSL A
is a modified version of TSL 3 and TSL
4 DOE used for the final rule. To
generate the efficiency analyzed in TSL
A for standard size equipment, DOE
further investigated the slope of the
energy-efficiency equation as discussed
in section IV.C. DOE adjusted the slope
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58819
of the energy-efficiency equation to
make the curve steeper. In other words,
DOE adjusted the energy-efficiency to
require more stringent efficiency levels
for lower cooling capacities, where
manufacturers have more physical space
inside the box sleeve to make efficiency
improvements, while lessening the
stringency for higher cooling capacities,
where manufacturers are already using
most of the physical space inside the
box sleeve for capacity increases,
leaving little room for efficiency
improvements. For TSL A, DOE
combined the efficiency levels in TSL 3
and TSL 1 for standard size PTACs
depending on cooling capacity. For TSL
A, DOE combined the efficiency levels
in TSL 5 and TSL 3 for standard size
PTHPs depending on cooling capacity.
This combination of efficiency levels
serves to maximize LCC savings, while
recognizing the differences in LCC
results for standard size PTACs and
PTHPs and the differences in the energy
efficiency potentials between the
various cooling capacities of standard
size equipment. (See Chapter 9 of the
TSD for further explanation and a
graphical representation of the energyefficiency equations.)
DOE projects that TSL A for standard
size PTACs and PTHPs would save
0.032 quads of energy through 2042, an
amount DOE considers significant.
Discounted at seven percent, the
projected energy savings through 2042
would be 0.007 quads. For the Nation as
a whole, DOE projects that TSL A would
result in net savings in NPV of $10
million for standard size PTACs and
PTHPs, using a discount rate of seven
percent, and $54 million for standard
size PTACs and PTHPs, using a
discount rate of three percent. The
estimated emissions reductions are 1.06
Mt of CO2, between 0.09 kt and 2.13 kt
of NOX, and between 0 and 0.037 t of
Hg. Total generating capacity needed in
2042 under TSL A would likely
decrease by 0.082 GW.
At TSL A, DOE projects that the
average PTAC or PTHP customer would
experience LCC savings. Purchasers of
standard size PTACs, on average, would
experience an LCC increase of $3
(2007$) over the life of the product
while purchasers of PTHPs would save
on average $26 (2007$). DOE estimates
LCC savings for 24 percent of customers
in the Nation who purchase a standard
size PTAC, and for 12 percent of
customers in the Nation who purchase
a standard size PTHP. For standard size
PTACs and PTHPs, the remainder of
customers would experience either a
decrease or no change in LCC. DOE also
projects that the mean payback period of
each standard size PTAC equipment
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class at TSL A would be substantially
longer than the mean lifetime of the
equipment.
The projected change in INPV ranges
between losses of $8 million and $61
million for the standard size PTAC and
PTHP industry at TSL A. Just as with
TSL 4, the projected impacts continue to
be driven primarily by the
manufacturers’ ability to pass on
increases in MPCs to the customer.
However, TSL A requires efficiency
levels for standard size PTHPs to be 0.2
EER higher than the efficiency levels for
PTACs. DOE believes bringing these
efficiency levels closer together will
ultimately aid manufacturers in using
one equipment platform to design their
standard size PTAC and PTHP
equipment offerings. The loss of $61
million assumes the continued validity
of DOE’s projections of partial cost
recovery as described in Chapter 13 of
the TSD. For the larger cooling capacity
range (e.g., 15,000 Btu/h), DOE believes
manufacturers could produce
equipment at the EER required by the
TSL A energy-efficiency equation
utilizing R–410A. Specifically, DOE
believes manufacturers would not be
forced to eliminate larger cooling
capacity equipment since DOE modified
the slope of the energy-efficiency
equation at TSL A to accommodate the
additional concerns regarding the
physical constraints at larger cooling
capacities.
After considering the analysis and
weighing the benefits and the burdens,
DOE concludes that the benefits of a
TSL A standard outweigh the burdens.
In particular, the Secretary concludes
that TSL A saves a significant amount
of energy and is technologically feasible
and economically justified in the full
range of cooling capacities for R–410A
standard size PTACs and PTHPs.
Therefore, DOE adopts the energy
conservation standards for standard size
PTACs and PTHPs at TSL A, as
described by the energy-efficiency
equations. Table V.32 sets out the
energy conservation standards for
standard size PTACs and PTHPs in the
full range of cooling capacities that DOE
is adopting.
TABLE V.32—FINAL ENERGY CONSERVATION STANDARDS FOR STANDARD SIZE PTACS AND PTHPS
Equipment class
Final energy conservation standards *
Equipment
Category
Cooling capacity
PTAC ..........................................
Standard Size ** .........................
PTHP ..........................................
Standard Size ** .........................
<7,000 ........................................
7,000–15,000 ..............................
>15,000 ......................................
<7,000 ........................................
7,000–15,000 ..............................
>15,000 ......................................
EER = 11.7
EER = 13.8 ¥ (0.300 × Cap †)
EER = 9.3
EER = 11.9
COP = 3.3
EER = 14.0 ¥ (0.300 × Cap †)
COP = 3.7 ¥ (0.052 × Cap †)
EER = 9.5
COP = 2.9
* For equipment rated according to the DOE test procedure (ARI Standard 310/380–2004), all energy efficiency ratio (EER) values must be
rated at 95 °F outdoor dry-bulb temperature for air-cooled equipment and evaporatively-cooled equipment and at 85 °F entering water temperature for water cooled equipment. All coefficient of performance (COP) values must be rated at 47 °F outdoor dry-bulb temperature for air-cooled
equipment.
** Standard size refers to PTAC or PTHP equipment with wall sleeve dimensions having an external wall opening greater than or equal to 16
inches high or greater than or equal to 42 inches wide, and a cross-sectional area greater than or equal to 670 square inches.
† Cap means cooling capacity in thousand British thermal units per hour (Btu/h) at 95 °F outdoor dry-bulb temperature.
2. Non-Standard Size PTACs and PTHPs
Table V.33 summarizes DOE’s
quantitative analysis results for each
TSL it considered for non-standard size
PTACs and PTHPs in this final rule.
This table presents the results or, in
some cases a range of results, for each
TSL, and will aid the reader in the
discussion of costs and benefits of each
TSL. The range of values for industry
impacts represents the results for the
different markup scenarios that DOE
used to estimate manufacturer impacts.
TABLE V.33—SUMMARY OF RESULTS FOR NON-STANDARD SIZE PTACS AND PTHPS BASED UPON THE AEO2008
ENERGY PRICE FORECAST *
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TSL 1
Primary energy saved (quads) ............................................
7% Discount rate (Non-Standard Size) ........................
3% Discount rate (Non-Standard Size) ........................
Generation capacity reduction (GW) (Standard Size) ** .....
NPV (2007$million) (Non-Standard Size):
7% Discount rate ..........................................................
3% Discount rate ..........................................................
Industry Impacts (Non-Standard Size):
Industry NPV (2007$ million) ........................................
Industry NPV (% Change) ............................................
Cumulative Emissions Impacts (Non-Standard Size): †
CO2 (Mt) ........................................................................
NOX (kt) ........................................................................
Hg (t) .............................................................................
Employment Impacts (Non-Standard Size):
Indirect Employment Impacts .......................................
Direct, Domestic Employment Impacts ........................
Mean LCC Savings (2007$) (Non-Standard Size): *
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TSL 2
TSL 3
TSL 4
TSL 5
0.004
0.001
0.002
(0.009)
0.004
0.001
0.002
(0.010)
0.005
0.001
0.003
(0.013)
0.006
0.001
0.003
(0.014)
0.009
0.002
0.004
(0.021)
5
14
6
16
7
19
8
23
10
29
(16)–(17)
(54)–(58)
(17)–(19)
(58)–(64)
(17)–(20)
(56)–(65)
(21)–(23)
(69)–(78)
(20)–(24)
(65)–(81)
(0.12)
(0.01)–(0.23)
0–(0.004)
(0.14)
(0.01)–(0.28)
0–(0.005)
(0.18)
(0.01)–(0.34)
0–(0.006)
(0.20)
(0.02)–(0.40)
0–(0.007)
(0.29)
(0.02)–(0.55)
0–(0.010)
8
(106)–1
9
(106)–1
12
(107)–1
14
(107)–1
20
(108)–2
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58821
TABLE V.33—SUMMARY OF RESULTS FOR NON-STANDARD SIZE PTACS AND PTHPS BASED UPON THE AEO2008
ENERGY PRICE FORECAST *—Continued
TSL 1
Non-Standard Size PTAC, 11,000
Non-Standard Size PTHP, 11,000
Mean PBP (years) (Standard Size):
Non-Standard Size PTAC, 11,000
Non-Standard Size PTHP, 11,000
TSL 2
TSL 3
TSL 4
TSL 5
Btu/h ......................
Btu/h ......................
26
62
26
66
30
66
26
80
31
80
Btu/h ......................
Btu/h ......................
4.4
2.2
4.4
2.8
5.1
2.8
4.4
3.0
5.9
3.0
LCC Results (Non-Standard Size)
Non-Standard Size PTAC, 11,000 Btu/h:
Net Cost (%) .................................................................
No Impact (%) ...............................................................
Net Benefit (%) .............................................................
Non-Standard Size PTHP, 11,000 Btu/h:
Net Cost (%) .................................................................
No Impact (%) ...............................................................
Net Benefit (%) .............................................................
6
73
22
6
73
22
14
47
39
6
73
22
25
23
52
1
73
27
3
47
50
3
47
50
5
23
72
5
23
72
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* Parentheses indicate negative values. For LCCs, a negative value means an increase in LCC by the amount indicated.
** Change in installed generation capacity by the year 2042 based on AEO2008 Reference Case.
† CO emissions impacts are physical reductions from all sources. NO and Hg emissions impacts are physical reductions at power plants.
2
X
First, DOE considered TSL 5, the maxtech efficiency level for non-standard
size PTACs and PTHPs. TSL 5 would
likely save 0.009 quads of energy
through 2042 for non-standard size
PTACs and PTHPs, an amount DOE
considers significant. Discounted at
seven percent, the projected energy
savings through 2042 would be 0.002
quads. For the Nation as a whole, DOE
projects that TSL 5 would result in a net
increase of $10 million in NPV for nonstandard size PTACs and PTHPs, using
a discount rate of seven percent, and
$29 million for non-standard size
PTACs and PTHPs, using a discount rate
of three percent. The emissions
reductions at TSL 5 for non-standard
size PTACs and PTHPs are 0.29 Mt of
CO2, between 0.02 and 0.55 kt of NOX,
and between 0.0 and 0.01 t of Hg. Total
generating capacity needed in 2042 is
estimated to decrease compared to the
reference case by 0.021 GW under TSL
5 for non-standard size equipment.
At TSL 5, DOE projects that the
average PTAC customer will experience
a decrease in LCC for all non-standard
size equipment classes. Purchasers of
non-standard size PTACs are projected
to save on average $31 (2007$) over the
life of the product and purchasers of
non-standard size PTHPs would save on
average $80 (2007$). DOE estimates LCC
increases for 25 percent of customers in
the Nation that purchase a non-standard
size PTAC, and for 5 percent of
customers in the Nation that purchase a
non-standard size PTHP.
The projected change in the nonstandard size industry value (INPV)
ranges from a decrease of $20 million to
a decrease of $24 million, in 2007$. For
non-standard size PTACs and PTHPs,
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the impacts are driven primarily by the
assumptions regarding the ability to
pass on larger increases in MPCs to the
customer. Currently, there are very few
equipment lines being manufactured
that have efficiency levels at or above
TSL 5 utilizing R–22 refrigerant. Using
the degradations estimated in the
engineering analysis, DOE believes nonstandard size equipment could be
produced at TSL 5 in the lower range of
cooling capacities. DOE believes
manufacturers would not be able to
manufacture non-standard size PTACs
and PTHPs at TSL 5 at the high range
of cooling capacities (e.g., 15,000 Btu/h)
within a given equipment class for nonstandard size PTACs and PTHPs with
cooling capacities greater than or equal
to 7,000 Btu/h and less than or equal to
15,000 Btu/h. In addition, DOE believes
many small manufacturers of nonstandard size equipment would be
unable to recover the large investments
needed to change over all of their
existing equipment lines to the
efficiency levels required by TSL 5. If
some small non-standard manufacturers
cannot invest the product and capital
conversion costs necessary to comply
with TSL 5, they would be forced to
abandon their equipment lines and exit
the business. Others could be forced to
reduce their equipment offerings in
order to reduce the magnitude of the
investments required to meet TSL 5
efficiency levels for non-standard
equipment.
After carefully considering the
analysis and weighing the benefits and
burdens of TSL 5, the Secretary has
reached the following conclusion: At
TSL 5, even if manufacturers overcome
the barriers to produce R–410
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equipment in the full range of cooling
capacities by the effective date of an
amended energy conservation standard,
the benefits of energy savings and
emissions reductions would be
outweighed by the potential multimillion dollar negative economic
burden on manufacturers, the risks of
small, non-standard manufacturers
exiting from the market, and the
reduction of equipment lines resulting
from decreased equipment offerings.
Next, DOE considered TSL 4. For TSL
4, DOE combined the efficiency levels
in TSL 1 for non-standard size PTACs
and the efficiency levels in TSL 5 for
non-standard size PTHPs. This
combination of efficiency levels serves
to maximize LCC savings, while
recognizing the differences in LCC
results for non-standard size PTACs and
PTHPs. DOE projects that TSL 4 for nonstandard size PTACs and PTHPs would
save 0.006 quads of energy through
2042, an amount DOE considers
significant. Discounted at seven percent,
the projected energy savings through
2042 would be 0.001 quads. For the
Nation as a whole, DOE projects that
TSL 4 would result in net savings in
NPV of $8 million for non-standard size
PTACs and PTHPs, using a discount rate
of seven percent, and $23 million for
non-standard size PTACs and PTHPs,
using a discount rate of three percent.
The estimated emissions reductions are
0.20 Mt of CO2, between 0.02 kt and
0.40 kt of NOX, and between 0 and 0.007
t of Hg. Total generating capacity
needed in 2042 under TSL 4 would
likely decrease by 0.014 GW.
At TSL 4, DOE projects that the
average PTAC or PTHP customer would
experience LCC savings. Purchasers of
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non-standard size PTACs, on average,
would experience an LCC decrease of
$26 (2007$) over the life of the product
and purchasers of non-standard size
PTHPs would save on average $80
(2007$). DOE estimates an LCC increase
for 6 percent of customers in the Nation
who purchase a non-standard size
PTAC, and for 5 percent of customers in
the Nation who purchase a nonstandard size PTHP. The remaining
customers of non-standard size PTACs
and PTHPs would experience either a
decrease or no change in LCC.
The projected change in INPV ranges
between losses of $21 million and $23
million for the non-standard size PTAC
and PTHP industry. Just as with TSL 5,
the projected impacts continue to be
driven primarily by the manufacturers’
ability to pass on increases in MPCs to
the customer. The loss of $23 million
assumes that DOE’s projections of
partial cost recovery as described in
Chapter 13 of the TSD remain valid.
TSL 4 requires the production of nonstandard size PTACs at the efficiency
levels in TSL 1 and non-standard size
PTHPs at efficiency levels at TSL 5.
Thus, TSL 4 requires the production of
non-standard size PTHPs using R–410A
that would have efficiencies equivalent
to the ‘‘max tech’’ efficiency levels with
R–410A applying the degradations
estimated in the engineering analysis in
the absence of a high efficiency
compressor. For the larger cooling
capacity range (i.e., 15,000 Btu/h)
within a given equipment class of nonstandard size PTACs and PTHPs with a
cooling capacity greater than or equal to
7,000 Btu/h and less than or equal to
15,000 Btu/h, DOE believes
manufacturers would not be able to
produce equipment at the efficiency
levels provided by the TSL 4 energyefficiency equations. At larger cooling
capacities for non-standard equipment,
manufacturers do not have the
additional space within the box sleeve
to add heat exchanger area to increase
the efficiency of the equipment.
Specifically, DOE believes non-standard
manufacturers would eliminate
equipment due to the stringency of the
standard—and the costs associated with
attaining them—at higher cooling
capacity regions. In addition, DOE
believes many small manufacturers of
non-standard size equipment would be
unable to recover the large investments
needed to change over all of their
existing equipment lines to the
efficiency levels required by TSL 4. If
some of these manufacturers cannot
invest the product and capital
conversion costs necessary to comply
with TSL 4, they would be forced to
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abandon their equipment lines and exit
the business. Others could be forced to
reduce their equipment offerings in
order to reduce the magnitude of the
investments required to meet the TSL 4
efficiency levels, which will affect their
ability to offer R–410A-compatible
equipment in the full range of capacities
currently being offered by the time the
new standard would become effective.
Based on the reasons stated earlier,
while DOE recognizes the increased
economic benefits to the nation that
could result from TSL 4 for nonstandard size PTACs and PTHPs, DOE
concludes that the benefits of a Federal
standard at TSL 4 would still be
outweighed by the economic burden
that would be placed upon nonstandard size PTAC and PTHP
manufacturers.
Next, DOE considered TSL 3. TSL 3
includes the same efficiency levels for
non-standard PTACs as non-standard
PTHPs. DOE projects that TSL 3 for nonstandard size PTACs and PTHPs would
save 0.005 quads of energy through
2042, an amount DOE considers
significant. Discounted at seven percent,
the projected energy savings through
2042 would be 0.001 quads. For the
Nation as a whole, DOE projects that
TSL 3 would result in net savings in
NPV of $7 million for non-standard size
PTACs and PTHPs, using a discount rate
of seven percent, and $19 million for
non-standard size PTACs and PTHPs,
using a discount rate of three percent.
The estimated emissions reductions are
0.18 Mt of CO2, between 0.01 and 0.34
kt of NOX, and between 0 and 0.006 t
of Hg. Total generating capacity needed
in 2042 under TSL 3 for non-standard
size PTACs and PTHPs would likely
decrease by 0.013 GW.
At TSL 3, DOE projects that the
average PTAC or PTHP customer would
experience LCC savings. Purchasers of
non-standard size PTACs, on average,
would experience a decrease in LCC of
$30 (2007$) over the life of the product
and purchasers of non-standard size
PTHPs would save on average $66
(2007$). DOE estimates an LCC increase
for 14 percent of customers in the
Nation that purchase a non-standard
size PTAC, and for 3 percent of
customers in the Nation that purchase a
non-standard size PTHP. The remaining
customers would experience either a
decrease or no change in LCC.
The projected change in INPV ranges
between a loss of $17 million and a loss
of $20 million for the non-standard size
PTAC and PTHP industry. Just as with
TSL 5, the projected impacts continue to
be driven primarily by the
manufacturers’ ability to pass on
increases in MPCs to the customer. The
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loss of $20 million assumes the
continued validity of DOE’s projections
of partial cost recovery as described in
Chapter 13 of the TSD. Even at TSL 3,
DOE is concerned about the
manufacturers’ ability to produce and
offer equipment in the full range of
cooling capacities that would fit the
wide variety of wall sleeves that
currently exist. For the larger cooling
capacity range (i.e., 15,000 Btu/h)
within a given equipment class of nonstandard size PTACs and PTHPs with a
cooling capacity greater than or equal to
7,000 Btu/h and less than or equal to
15,000 Btu/h, DOE believes
manufacturers would not be able to
produce equipment at the efficiency
levels provided by the TSL 3 energyefficiency equations. Specifically, DOE
believes non-standard manufacturers
would eliminate equipment due to the
stringency of the standard at higher
cooling capacity regions. In addition,
TSL 3 requires a $23 million investment
by the industry in order to transform all
of the existing equipment lines available
in the current non-standard market to
TSL 3 efficiency levels. DOE believes
many small non-standard manufacturers
would not be able to recover these
investments needed to change over all
of their existing equipment lines to the
efficiency levels required by TSL 3. If
some small non-standard manufacturers
cannot invest the product and capital
conversion costs necessary to comply
with TSL 3, they would be forced to
abandon their equipment lines and exit
the business. Others could be forced to
reduce their equipment offerings in
order to reduce the magnitude of the
investments required to meet TSL 3
efficiency levels for non-standard
equipment.
While DOE recognizes the increased
economic benefits to the nation and the
energy savings that could result from
TSL 3 for non-standard size PTACs and
PTHPs, DOE concludes that, based on
the above, the benefits of an amended
energy conservation standard at TSL 3
would be outweighed by the economic
burden that would be placed upon nonstandard size PTAC and PTHP
manufacturers.
Next, DOE considered TSL 2. TSL 2
requires different efficiency levels for
non-standard size PTACs and nonstandard PTHPs at the same cooling
capacity. DOE projects that TSL 2 for
non-standard size PTACs and PTHPs
would save 0.004 quads of energy
through 2042, an amount DOE considers
significant. Discounted at seven percent,
the projected energy savings through
2042 would be 0.001 quads. For the
Nation as a whole, DOE projects that
TSL 2 would result in net savings in
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NPV of $6 million for non-standard size
PTACs and PTHPs, using a discount rate
of seven percent, and $16 million for
non-standard size PTACs and PTHPs,
using a discount rate of three percent.
The estimated emissions reductions are
0.14 Mt of CO2, between 0.01 kt and
0.28 kt of NOX, and between 0 and 0.005
t of Hg. Total generating capacity
needed in 2042 under TSL 2 for nonstandard size PTACs and PTHPs would
likely decrease by 0.010 GW.
At TSL 2, DOE projects that the
average PTAC or PTHP customer would
experience LCC savings. Purchasers of
non-standard size PTACs, on average,
would have an LCC decrease of $26
(2007$) over the life of the product and
purchasers of non-standard size PTHPs
would save on average $66 (2007$).
DOE estimates an LCC increase for 6
percent of customers in the Nation that
purchase a non-standard size PTAC and
for 3 percent of customers in the Nation
that purchase a non-standard size PTHP.
The remaining customers of nonstandard size PTACs and PTHPs would
experience either a decrease or no
change in LCC.
The projected change in INPV ranges
between a loss of $17 million and a loss
of $19 million for the non-standard size
PTAC and PTHP industry. Just as with
other TSLs, the projected impacts
continue to be driven primarily by the
manufacturers’ ability to pass on
increases in MPCs to the customer. The
loss of $19 million assumes DOE’s
projections of partial cost recovery as
described in Chapter 13 of the TSD
remain valid. Since TSL 2 requires nonstandard size manufacturers to be
produced at the efficiency levels in TSL
3, DOE is concerned about the
manufacturer’s ability to produce and
offer equipment in the full range of
cooling capacities to fit the wide variety
of wall sleeves that currently exist for
non-standard size PTHPs.
For the larger cooling capacity range
(i.e., 15,000 Btu/h) within a given
equipment class of non-standard size
PTACs and PTHPs with a cooling
capacity greater than or equal to 7,000
Btu/h and less than or equal to 15,000
Btu/h, DOE believes manufacturers
would be unable to produce equipment
at the efficiency levels provided by the
TSL 2 energy-efficiency equations.
Specifically, DOE believes non-standard
manufacturers would eliminate
equipment due to the costs required to
satisfy this level at higher cooling
capacity regions. In addition, TSL 2
requires a 23.3 million dollar
investment in order to transform all of
the existing equipment lines available in
the current non-standard market to TSL
2 efficiency levels. The investment
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required at TSL 2 is larger than at TSL
3 because manufacturers could be
forced to design separate equipment
platforms for non-standard size PTACs
and non-standard size PTHPs because of
the differences in efficiency level
requirements. DOE believes many small
manufacturers of non-standard size
equipment would be unable to recover
these investments needed to change
over all of their existing equipment lines
to the efficiency levels required by TSL
2. If some small, non-standard
manufacturers cannot invest the product
and capital conversion costs necessary
to comply with TSL 2, they would be
forced to abandon their equipment lines
and exit the business. Others could be
forced to reduce their equipment
offerings in order to reduce the
magnitude of the investments required
to meet TSL 2 efficiency levels for nonstandard equipment.
While DOE recognizes the increased
economic benefits to the nation and the
energy savings that could result from
TSL 2 for non-standard size PTACs and
PTHPs, DOE concludes, based on the
reasons stated above, that the benefits of
an amended energy conservation
standard at TSL 2 would be outweighed
by the economic burden that would be
placed upon non-standard size PTAC
and PTHP manufacturers.
Last, DOE considered TSL 1. TSL 1
requires the same efficiency levels for
non-standard size PTACs and nonstandard PTHPs at the same cooling
capacity. DOE projects that TSL 1 for
non-standard size PTACs and PTHPs
would save 0.004 quads of energy
through 2042, an amount DOE considers
significant. Discounted at seven percent,
the projected energy savings through
2042 would be 0.001 quads. For the
Nation as a whole, DOE projects that
TSL 1 would result in net savings in
NPV of $5 million for non-standard size
PTACs and PTHPs, using a discount rate
of seven percent, and $14 million for
non-standard size PTACs and PTHPs,
using a discount rate of three percent.
The estimated emissions reductions are
0.12 Mt of CO2, between 0.01 kt and
0.23 kt of NOX, and between 0 and 0.004
t of Hg. Total generating capacity
needed in 2042 under TSL 1 for nonstandard size PTACs and PTHPs would
likely decrease by 0.009 GW.
At TSL 1, DOE projects that the
average PTAC or PTHP customer would
experience an LCC savings. Purchasers
of non-standard size PTACs, on average
would experience an LCC decrease of
$26 (2007$) over the life of the product
and purchasers of non-standard size
PTHPs would save on average $62
(2007$). DOE estimates LCC increase for
6 percent of customers in the Nation
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that purchase a non-standard size
PTAC, and for 1 percent of customers in
the Nation that purchase a non-standard
size PTHP. The remaining customers of
non-standard size equipment would
experience either a decrease or no
change in LCC.
The projected change in INPV ranges
between losses of $16 million and $17
million for the non-standard size PTAC
and PTHP industry. Just as with other
TSLs, the projected impacts continue to
be driven primarily by the
manufacturers’ ability to pass on
increases in MPCs to the customer. The
loss of $17 million assumes DOE’s
projections of partial cost recovery as
described in Chapter 13 of the TSD
remain valid. Even at TSL 1, DOE
estimates manufacturers of nonstandard PTACs and PTHPs would
experience over a 50 percent reduction
in INPV as a result of amended energy
conservation standards. TSL 1 requires
a 22 million dollar investment by the
industry in order to transform all of the
existing equipment lines available in the
current non-standard market to TSL 1
efficiency levels. DOE believes many
small manufacturers of non-standard
equipment would be unable to recover
these investments needed to change
over all of their existing equipment lines
to the efficiency levels required by TSL
1. If some small non-standard
manufacturers cannot invest the product
and capital conversion costs necessary
to comply with TSL 1, they would be
forced to abandon their equipment lines
and exit the business. Others could be
forced to reduce their equipment
offerings in order to reduce the
magnitude of the investments required
to meet TSL 1 efficiency levels for nonstandard equipment.
While DOE recognizes the increased
economic benefits to the nation and the
energy savings that could result from
TSL 1 for non-standard size PTACs and
PTHPs, DOE concludes that the benefits
of an amended energy conservation
standard at TSL 1 would still be
outweighed by the economic burden
that would be placed upon nonstandard size PTAC and PTHP
manufacturers. DOE is especially
concerned about the large investments
required for non-standard size
manufacturers to transform their entire
equipment offerings to TSL 1 efficiency
levels and with the likelihood that small
non-standard size manufacturers would
exit the market, causing some existing
non-standard size PTACs and PTHPs to
become unavailable to consumers.
After considering the analysis and
weighing the benefits and the burdens,
DOE concludes that the benefits of a
standard at the efficiency levels
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specified by ASHRAE Standard 90.1–
1999 outweigh the burdens.
Therefore based on the discussion
above, DOE concludes that the
efficiency levels beyond those in
ASHRAE Standard 90.1–1999 are not
economically justified and is adopting
the efficiency level in ASHRAE
Standard 90.1–1999. Table V.34
demonstrates the amended energy
conservation standards for standard size
PTACs and PTHPs in the full range of
cooling capacities.
TABLE V.34—FINAL ENERGY CONSERVATION STANDARDS FOR NON-STANDARD SIZE PTACS AND PTHPS
Equipment class
Final energy conservation standards *
Equipment
Category
Cooling capacity
PTAC ..........................................
Non-Standard Size ** ..................
<7,000 ........................................
7,000–15,000 ..............................
>15,000 ......................................
<7,000 ........................................
PTHP ..........................................
Non-Standard Size ** ..................
7,000–15,000 ..............................
>15,000 ......................................
EER = 9.4
EER = 10.9 ¥ (0.213 × Cap †)
EER = 7.7
EER = 9.3
COP = 2.7
EER = 10.8 ¥ (0.213 × Cap †)
COP = 2.9 ¥ (0.026 × Cap †)
EER = 7.6
COP = 2.5
* For equipment rated according to the DOE test procedure (ARI Standard 310/380–2004), all energy efficiency ratio (EER) values must be
rated at 95 °F outdoor dry-bulb temperature for air-cooled equipment and evaporatively cooled equipment and at 85 °F entering water temperature for water cooled equipment. All coefficient of performance (COP) values must be rated at 47 °F outdoor dry-bulb temperature for air-cooled
equipment.
** Non-standard size refers to PTAC or PTHP equipment with existing wall sleeve dimensions having an external wall opening of less than 16
inches high or less than 42 inches wide, and a cross-sectional area less than 670 square inches.
† Cap means cooling capacity in thousand British thermal units per hour (Btu/h) at 95 °F outdoor dry-bulb temperature.
VI. Procedural Issues and Regulatory
Review
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A. Review Under Executive Order 12866
Section 1(b)(1) of Executive Order
12866, ‘‘Regulatory Planning and
Review,’’ 58 FR 51735 (October 4, 1993),
requires each agency to identify in
writing the market failure or other
problem that it intends to address that
warrants agency action such as today’s
final rule, and to assess the significance
of that problem in evaluating whether
any new regulation is warranted.
DOE’s analysis suggests that much of
the hospitality industry segment using
PTAC and PTHP equipment tends to be
small hotels or motels. DOE believes
that these small hotels and motels tend
to be individually owned and operated
and lack corporate direction in terms of
energy policy. The transaction costs for
these smaller owners or operators to
research, purchase, and install optimum
efficiency equipment are too high to
make such action commonplace. DOE
believes that there is a lack of
information and/or information
processing capability about energy
efficiency opportunities in the PTAC
and PTHP market available to hotel or
motel owners. Unlike residential
heating and air conditioning products,
PTACs and PTHPs are not included in
energy labeling programs such as the
Federal Trade Commission’s energy
labeling program. Furthermore, the
energy use of PTACs and PTHPs
depends on the climate and equipment
usage and, as such, is not readily
available for the owners or operators to
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decide whether improving the energy
efficiency of PTAC and PTHP
equipment is cost effective.
PTACs and PTHPs are not purchased
in the same manner as other regulated
appliances that are sold in retail stores
(e.g., room air conditioners). When
purchased by the end user, PTACs and
PTHPs are more likely to be purchased
through contractors and builders that
perform the installation. (See Chapter 8
of the final rule TSD) The AHRI
Certified Directory includes PTACs and
PTHPs, and provides the energy
efficiency and capacity information on
PTACs and PTHPs produced by
participating manufacturers.
To the extent that a lack of
information may exist, DOE could
expect the energy efficiency for PTACs
and PTHPs to be more or less randomly
distributed across key variables such as
energy prices and usage levels. DOE
found that energy efficiency and energy
cost savings are not the primary drivers
of the hotel and motel business. Instead,
hotel and motel operators work on a
fixed budget and are concerned
primarily with providing clean and
comfortable rooms to the customers to
ensure customer satisfaction. If
consumer satisfaction decreases, hotel
or motel owners may incur increased
transaction costs, thus preventing access
to capital to finance energy efficiency
investment.
A related issue is the problem of
asymmetric information (one party to a
transaction has more and better
information than the other) and/or high
transactions costs (costs of gathering
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information and effecting exchanges of
goods and services) among PTAC and
PTHP equipment customers. In the case
of PTACs and PTHPs, in many cases,
the party responsible for the equipment
purchase may not be the one who pays
the operating cost. For example, PTAC
and PTHP equipment are also used in
nursing homes (i.e., assisted living) and
medical office buildings. In these
settings, the builder or complex owner
often makes decisions about PTACs and
PTHPs without input from tenants and
typically does not offer tenants the
option to upgrade that equipment.
Furthermore, DOE believes that the
tenant typically pays the utility bills. If
there were no transactions costs, it
would be in the builder or complex
owners’ interest to install equipment
that the tenants would choose on their
own. For example, a tenant who
knowingly faces higher utility bills from
low-efficiency equipment would expect
to pay less in rent, thereby shifting the
higher utility cost back to the complex
owner. However, this information is not
without a cost. It may not be in the
tenant’s interest to take the time to
develop it or, in the case of the complex
owner who installs less efficient
equipment, to convey that information
to the tenant.
To the extent that asymmetric
information and/or high transaction
costs are problems, one would expect to
find certain outcomes regarding PTAC
and PTHP efficiency. For example, all
things being equal, one would not
expect to see higher rents for office
complexes with high-efficiency
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equipment. Alternatively, one would
expect higher energy efficiency in rental
units where the rent includes utilities,
compared with those where the tenant
pays the utility bills separately. DOE did
not receive any data that would enable
it to conduct tests of market failure in
response to the NOPR.
In addition, this rulemaking is likely
to yield certain ‘‘external’’ benefits
resulting from improved energy
efficiency of PTACs and PTHPs that are
not captured by the users of such
equipment. These benefits include
externalities related to environmental
and energy security that are not
reflected in energy prices, such as
reduced emissions of greenhouse gases.
Regarding environmental externalities,
the emissions reductions in today’s final
rule are projected to be 1.06 million
metric tons (Mt) of CO2, between 0.09
kilotons and 2.13 kilotons (kt) of NOX,
and between 0 and 0.037 tons of Hg.
Because today’s regulatory action is a
significant regulatory action under
section 3(f)(1) of Executive Order 12866,
section 6(a)(3) of the Executive Order
requires DOE to prepare and submit for
review to OMB’s Office of Information
and Regulatory Affairs (OIRA) an
assessment of the costs and benefits of
today’s rule. Accordingly, DOE
presented to OIRA for review the draft
final rule and other documents prepared
for this rulemaking, including a
regulatory impact analysis (RIA). These
documents are included in the
rulemaking record and are available for
public review in the Resource Room of
DOE’s Building Technologies Program,
950 L’Enfant Plaza, SW., 6th Floor,
Washington, DC 20024, (202) 586–9127,
between 9 a.m. and 4 p.m., Monday
through Friday, except Federal holidays.
The NOPR contained a summary of
the RIA, which evaluated the extent to
which major alternatives to standards
for PTACs and PTHPs could achieve
significant energy savings at reasonable
cost, compared with the effectiveness of
the proposed rule. 73 FR 18907–10. The
complete RIA (Regulatory Impact
Analysis for Proposed Energy
Conservation Standards for Packaged
Terminal Air Conditioners and Heat
Pumps), is contained in the TSD
prepared for today’s rule. 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
amended standards.
As explained in the NOPR, DOE
determined that none of the alternatives
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that it examined would save as much
energy or have an NPV as high as the
proposed standards. That same
conclusion applies to the amended
standards in today’s rule. In addition,
several of the alternatives would require
new enabling legislation, because
authority to conduct those alternatives
currently does not exist. The RIA report
in the TSD provides additional detail on
the regulatory alternatives.
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,
and a final regulatory flexibility analysis
(FRFA) for any such rule that an agency
adopts as a final rule, unless the agency
certifies that the rule, if promulgated,
will not have a significant economic
impact on a substantial number of small
entities. A regulatory flexibility analysis
examines the impact of the rule on
small entities and considers alternative
ways of reducing negative impacts.
Also, as required by Executive Order
13272, ‘‘Proper Consideration of Small
Entities in Agency Rulemaking,’’ 67 FR
53461 (August 16, 2002), DOE
published procedures and policies on
February 19, 2003, to ensure that the
potential impacts of its rules on small
entities are properly considered during
the rulemaking process. 68 FR 7990.
DOE has made its procedures and
policies available on the Office of
General Counsel’s Web site: https://
www.gc.doe.gov.
Small businesses, as defined by the
Small Business Administration (SBA)
for the packaged terminal equipment
manufacturing industry, are
manufacturing enterprises with 750
employees or fewer. DOE used the small
business size standards published on
March 11, 2008, as amended, by the
SBA to determine whether any small
entities would be required to comply
with the rule. 61 FR 3286 and codified
at 13 CFR part 121. The size standards
are listed by North American Industry
Classification System (NAICS) code and
industry description. PTAC and PTHP
manufacturing is classified under
NAICS 333415, which sets a threshold
of 750 employees or less for an entity to
be considered as a small business under
the ‘‘Air-Conditioning and Warm Air
Heating Equipment and Commercial
and Industrial Refrigeration Equipment
Manufacturer’’ category.
For the NOPR, DOE identified and
interviewed two manufacturers of
PTACs and PTHPs that are small
businesses affected by this rulemaking.
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58825
73 FR 18910. DOE reviewed the
proposed rule under the provisions of
the Regulatory Flexibility Act and the
procedures and policies published on
February 19, 2003. Id. On the basis of
this review, DOE determined that it
could not certify that the proposed
standards (TSL4), if promulgated, would
have no significant economic impact on
a substantial number of small entities.
Id. DOE made this determination
because of the potential impacts of the
proposed standard levels on PTAC and
PTHP manufacturers generally,
including small businesses. Id.
Because of these potential impacts on
small manufacturers, DOE prepared an
IRFA during the NOPR stage of this
rulemaking. DOE provided the IRFA in
its entirety in the NOPR, 73 FR 18910–
12, and also transmitted a copy to the
Chief Counsel for Advocacy of the SBA
for review. Chapter 13 of the TSD
contains more information about the
impact of this rulemaking on
manufacturers.
The IRFA divided potential impacts
on small businesses into two broad
categories: (1) Impacts associated with
standard size PTAC and PTHP
manufacturers; and (2) impacts
associated with non-standard size PTAC
and PTHP manufacturers. The PTAC
and PTHP industry is characterized by
both domestic and international
manufacturers. Standard size PTACs
and PTHPs are primarily manufactured
outside of the U.S. with the exception
of one domestic PTAC and PTHP
manufacturer. Non-standard size PTACs
and PTHPs are primarily manufactured
domestically by a handful of
manufacturers. Consolidation within the
PTAC and PTHP industry has reduced
the number of parent companies that
manufacture similar equipment under
different affiliates and labels.
DOE has prepared a FRFA for this
rulemaking, which is presented in the
following discussion. Comments
received in response to the IRFA
regarding the impacts on small
businesses in the non-standard industry
are summarized in section IV.K.2. In
addition, DOE further reviewed the nonstandard size industry, in particular, the
market for small businesses, and
presented its finding in section IV.K.2.
The FRFA below is written in
accordance with the requirements of the
Regulatory Flexibility Act, and
addresses the comments received from
interested parties in response to the
IRFA.
1. Reasons for the Final Rule
Part A–1 of Title III of EPCA
addresses the energy efficiency of
certain types of commercial and
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industrial equipment. (42 U.S.C. 6311–
6317) It contains specific mandatory
energy conservation standards for
commercial PTACs and PTHPs. (42
U.S.C. 6313(a)(3)) EPACT 1992, Public
Law 102–486, also amended EPCA with
respect to PTACs and PTHPs, providing
definitions in section 122(a), test
procedures in section 122(b), labeling
provisions in section 122(c), and the
authority to require information and
reports from manufacturers in section
122(e). DOE publishes today’s final rule
pursuant to Part A–1. The PTAC and
PTHP test procedures appear at 10 CFR
431.96.
EPCA established Federal energy
conservation standards that generally
correspond to the levels in ASHRAE
Standard 90.1, as in effect on October
24, 1992 (ASHRAE Standard 90.1–
1989), for each type of covered
equipment listed in section 342(a) of
EPCA, including PTACs and PTHPs. (42
U.S.C. 6313(a)) For each type of
equipment, EPCA directed that if
ASHRAE Standard 90.1 is amended,
DOE must adopt an amended standard
at the new level in ASHRAE Standard
90.1, unless clear and convincing
evidence supports a determination that
adoption of a more stringent level as a
national standard would produce
significant additional energy savings
and be technologically feasible and
economically justified. (42 U.S.C.
6313(a)(6)(A)(ii)(II)) In accordance with
these statutory criteria, DOE is
amending the energy conservation
standards for PTACs and PTHPs by
raising the efficiency levels for this
equipment above the efficiency levels
specified by ASHRAE Standard 90.1–
1999 for standard size PTACs and
PTHPs and adopting the efficiency
levels in ASHRAE Standard 90.1–1999
for non-standard size PTACs and
PTHPs.
2. Objectives of, and Legal Basis for, the
Rule
To determine whether economic
justification exists, DOE reviews
comments received and conducts
analysis to determine whether the
economic benefits of the amended
standard exceed the burdens to the
greatest extent practicable, taking into
consideration seven factors set forth in
42 U.S.C. 6295(o)(2)(B) (see section II.B
of this preamble). (42 U.S.C. 6316(a))
Further information concerning the
background of this rulemaking is
provided in Chapter 1 of the TSD.
3. Description and Estimated Number of
Small Entities Regulated
Through market research, interviews
with manufacturers of all sizes,
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discussions with industry trade groups,
and comments from interested parties
on the IRFA, DOE identified six small
manufacturers in the PTAC and PTHP
industry. These six manufacturers can
be further sub-categorized by their
manufacturing scale: (1) One small
business competes successfully making
standard-size PTACs and PTHPs in high
volumes; (2) the remaining five small
businesses make PTACs and PTHPs at
much lower volumes. While three of
these five low-volume small businesses
make PTACs and PTHPs that fit into
standard-size sleeves, the customization
options offered by these manufacturers
suggests that these units have more in
common with the non-standard size
equipment that these manufacturers also
offer than with the high-volume
standard size PTAC and PTHP
equipment on the market. DOE found
one small manufacturer of standard size
PTACs and PTHPs manufactures
equipment outside the U.S. DOE found
the five small manufacturers produce
equipment domestically. None of the six
firms are divisions of larger owned
companies.
4. Description and Estimate of
Compliance Requirements
Potential impacts on all
manufacturers of PTACs and PTHPs
vary by TSL. Margins for all businesses
could be impacted negatively by the
adoption of any TSL, since all
manufacturers have expressed an
inability to pass on cost increases to
retailers and consumers. The six small
domestic businesses under discussion
differ from their competitors in that they
are much smaller entities than their
competitors in the standard PTAC and
PTHP industry. Any rule affecting
products manufactured by these small
businesses will affect them
disproportionately because of their size
and their focus on non-standard PTAC
and PTHP equipment. However, due to
the low number of competitors that
agreed to be interviewed, DOE was not
able to characterize the small business
industry segment with a separate cashflow analysis due to concerns about
maintaining confidentiality.
For all other TSLs concerning PTAC
and PTHP equipment (which are not
being considered in today’s rule), the
impact on small, focused business
entities will be proportionately greater
than for their competitors since these
businesses lack the scale to afford
significant R&D expenses and capital
expansion budgets. The exact extent is
hard to gauge since manufacturers did
not respond to all proposed investment
requirements by TSL during interviews.
However, research associated with other
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small entities in prior rulemakings
suggests that many costs associated with
complying with rulemakings are
typically fixed, regardless of production
volume. Thus, given their focus and
scale, any appliance rulemaking could
affect these six small businesses
disproportionately compared to their
larger and more diversified competitors.
5. Significant Issues Raised by Public
Comments
DOE summarized comments from
interested parties in section IV.K.1.
6. Steps DOE Has Taken To Minimize
the Economic Impact on Small, NonStandard Size PTAC and PTHP
Manufacturers
In consideration of the benefits and
burdens of standards, including the
burdens posed to small manufacturers,
DOE concluded that the efficiency
levels in ASHRAE Standard 90.1–1999
are the highest levels that can be
justified for non-standard size PTAC
and PTHP equipment. DOE discusses
the potential impacts on small, nonstandard manufacturers from higher
TSLs in section IV.K.1. Since DOE has
adopted the efficiency levels in
ASHRAE Standard 90.1–1999, DOE
believes it has taken the necessary steps
to minimize the economic impact on
small, non-standard size PTAC and
PTHP manufacturers.
C. Review Under the Paperwork
Reduction Act
DOE stated in the NOPR that this
rulemaking would impose no new
information and recordkeeping
requirements, and that OMB clearance
is not required under the Paperwork
Reduction Act (44 U.S.C. 3501 et seq.).
73 FR 18912. DOE received no
comments on this in response to the
NOPR and, as with the proposed rule,
today’s rule imposes no information and
recordkeeping requirements. DOE takes
no further action in this rulemaking
with respect to the Paperwork
Reduction Act.
D. Review Under the National
Environmental Policy Act
DOE prepared an environmental
assessment of the impacts of today’s
standards, which it published as a
chapter within the TSD for the final
rule. DOE found the environmental
effects associated with today’s various
standards levels for PTACs and PTHPs
to be not significant, and therefore it is
issuing a Finding of No Significant
Impact (FONSI) pursuant to the
National Environmental Policy Act of
1969 (42 U.S.C. 4321 et seq.), the
regulations of the Council on
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Environmental Quality (40 CFR parts
1500–1508), and DOE’s regulations for
compliance with the National
Environmental Policy Act (10 CFR part
1021). The FONSI is available in the
docket for this rulemaking.
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E. Review Under Executive Order 13132
DOE reviewed this rule pursuant to
Executive Order 13132, Federalism, 64
FR 43255 (August 4, 1999), which
imposes certain requirements on
agencies formulating and implementing
policies or regulations that preempt
State law or that have federalism
implications. In accordance with DOE’s
statement of policy describing the
intergovernmental consultation process
that it will follow in the development of
regulations that have federalism
implications, 65 FR 13735 (March 14,
2000), DOE examined the proposed rule
and determined that the rule 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. 73 FR 18912. DOE
received no comments on this issue in
response to the NOPR, and its
conclusions on this issue are the same
for the final rule as they were for the
proposed rule. DOE takes no further
action in today’s final rule with respect
to 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 (February 7, 1996)
imposes on Federal agencies the general
duty to adhere to the following
requirements: (1) Eliminate drafting
errors and ambiguity, (2) write
regulations to minimize litigation, 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
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review regulations in light of applicable
standards in section 3(a) and section
3(b) to determine whether they are met
or whether 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, the final regulations meet the
relevant standards of Executive Order
12988.
G. Review Under the Unfunded
Mandates Reform Act of 1995
As described in the NOPR, title II of
the Unfunded Mandates Reform Act of
1995 (Pub. L. 104–4) (UMRA) imposes
requirements on Federal agencies when
their regulatory actions will have certain
types of impacts on State, local, and
Tribal governments and the private
sector. 73 FR 18912–13. DOE concluded
that, because this rule would contain
neither an intergovernmental mandate
nor a mandate that may result in
expenditure of $100 million or more in
any year, the requirements of UMRA do
not apply to the rule. Id. DOE received
no comments concerning the UMRA in
response to the NOPR, and its
conclusions on this issue are the same
for the final rule as for the proposed
rule. DOE takes no further action in
today’s final rule with respect to the
UMRA.
H. Review Under the Treasury and
General Government Appropriations
Act of 1999
DOE determined that, for this
rulemaking, it need not prepare a
Family Policymaking Assessment under
Section 654 of the Treasury and General
Government Appropriations Act, 1999
(Pub. L. 105–277). 73 FR 18913. DOE
received no comments concerning
Section 654 in response to the NOPR,
and thus takes no further action in
today’s final rule with respect to this
provision.
I. Review Under Executive Order 12630
DOE determined, under Executive
Order 12630, Governmental Actions and
Interference with Constitutionally
Protected Property Rights, 53 FR 8859
(March 18, 1988), that today’s rule
would not result in any takings which
might require compensation under the
Fifth Amendment to the U.S.
Constitution. 73 FR 18913. DOE
received no comments concerning
Executive Order 12630 in response to
the NOPR, and thus takes no further
action in today’s final rule with respect
to this Executive Order.
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58827
J. Review Under the Treasury and
General Government Appropriations
Act of 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 (February 22, 2002), and DOE’s
guidelines were published at 67 FR
62446 (October 7, 2002). DOE has
reviewed today’s final rule under the
OMB and DOE guidelines and
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 at 28355
(May 22, 2001), requires Federal
agencies to prepare and submit to the
OIRA a Statement of Energy Effects for
any significant energy action. DOE
determined that the proposed rule was
not a significant energy action within
the meaning of Executive Order 13211.
73 FR 18913. Accordingly, it did not
prepare a Statement of Energy Effects on
the proposed rule. DOE received no
comments on this issue in response to
the NOPR. As with the proposed rule,
DOE has concluded that today’s final
rule is not a significant energy action
within the meaning of Executive Order
13211, and has not prepared a
Statement of Energy Effects on the rule.
L. Review Under the Information
Quality Bulletin for Peer Review
On December 16, 2004, the OMB, in
consultation with the Office of Science
and Technology, issued its Final
Information Quality Bulletin for Peer
Review (the Bulletin). 70 FR 2664
(January 14, 2005). The purpose of the
Bulletin is to enhance the quality and
credibility of the Government’s
scientific information. The Bulletin
establishes that certain scientific
information shall be peer reviewed by
qualified specialists before it is
disseminated by the federal government,
and, as indicated in the NOPR, this
includes influential scientific
information related to agency regulatory
actions, such as the analyses in this
rulemaking. 73 FR 18913.
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
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Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
Review Report pertaining to the energy
conservation standards rulemaking
analyses. The ‘‘Energy Conservation
Standards Rulemaking Peer Review
Report’’ dated February 2007 has been
disseminated and is available at the
following web site: https://www.eere.
energy.gov/buildings/appliance_
standards/peer_review.html. DOE on
June 28–29, 2005.
M. Congressional Notification
As required by 5 U.S.C. 801, DOE will
submit to Congress a report regarding
the issuance of today’s final rule prior
to the effective date set forth at the
outset of this notice. The report will
state that it has been determined that
the rule is a ‘‘major rule’’ as defined by
5 U.S.C. 804(2). DOE also will submit
the supporting analyses to the
Comptroller General in the U.S.
Government Accountability Office
(GAO) and make them available to
Congress.
VII. Approval of the Office of the
Secretary
The Secretary of Energy has approved
publication of today’s final rule.
List of Subjects in 10 CFR Part 431
Administrative practice and
procedure, Confidential business
information, Energy conservation.
Issued in Washington, DC, on September
29, 2008.
John F. Mizroch,
Acting Assistant Secretary, Energy Efficiency
and Renewable Energy.
For the reasons set forth in the
preamble, chapter II of title 10, Code of
Federal Regulations, part 431 is
amended to read as set forth below.
■
PART 431—ENERGY EFFICIENCY
PROGRAM FOR CERTAIN
COMMERCIAL AND INDUSTRIAL
EQUIPMENT
1. The authority citation for part 431
continues to read as follows:
■
Authority: 42 U.S.C. 6291–6317.
2. Section 431.92 is amended by
adding in alphabetical order new
definitions for ‘‘Non-standard size,’’ and
‘‘Standard size’’ to read as follows:
■
§ 431.92 Definitions concerned
commercial air conditioners and heat
pumps.
*
*
*
*
*
Non-standard size means a packaged
terminal air conditioner or packaged
terminal heat pump with existing wall
sleeve dimensions having an external
wall opening of less than 16 inches high
or less than 42 inches wide, and a crosssectional area less than 670 square
inches.
*
*
*
*
*
Standard size means a packaged
terminal air conditioner or packaged
terminal heat pump with wall sleeve
dimensions having an external wall
opening of greater than or equal to 16
inches high or greater than or equal to
42 inches wide, and a cross-sectional
area greater than or equal to 670 square
inches.
*
*
*
*
*
3. Section 431.97 is amended by
revising paragraph (a), including Tables
1 and 2, and by adding a new paragraph
(c) to read as follows:
■
§ 431.97 Energy efficiency standards and
their effective dates.
(a) All small or large commercial
package air conditioning and heating
equipment manufactured on or after
January 1, 1994 (except for large
commercial package air-conditioning
and heating equipment, for which the
effective date is January 1, 1995), and
before January 1, 2010, in the case of the
air-cooled equipment covered by the
standards in paragraph (b), must meet
the applicable minimum energy
efficiency standard level(s) set forth in
Tables 1 and 2 of this section. Each
standard size packaged terminal air
conditioner or packaged terminal heat
pump manufactured on or after January
1, 1994, and before September 30, 2012,
must meet the applicable minimum
energy efficiency standard level(s) set
forth in Tables 1 and 2 of this section.
Each non-standard size packaged
terminal air conditioner or packaged
terminal heat pump manufactured on or
after January 1, 1994, and before
September 30, 2010, must meet the
applicable minimum energy efficiency
standard level(s) set forth in Tables 1
and 2 of this section.
TABLE 1 TO § 431.97—MINIMUM COOLING EFFICIENCY LEVELS
Efficiency level 1
Product
Category
Sub-category
Products
manufactured until
October 29, 2003
Air Cooled, 3 Phase
<65,000 Btu/h ...........
Split System .............
Single Package ........
SEER = 10.0 ............
SEER = 9.7 ..............
SEER = 10.0.
SEER = 9.7.
Air Cooled .................
Small Commercial
Packaged Air Conditioning and Heating Equipment.
Cooling capacity
≥65,000 Btu/h and
<135,000 Btu/h.
<17,000 Btu/h ...........
All ..............................
EER = 8.9 .................
EER = 8.9.
AC .............................
HP .............................
EER = 9.3 .................
EER = 9.3 .................
EER = 12.1.
EER = 11.2.
≥17,000 Btu/h and
<65,000 Btu/h.
≥65,000 Btu/h and
<135,000 Btu/h.
≥135,000 Btu/h and
<240,000 Btu/h.
AC .............................
HP .............................
AC .............................
HP .............................
All ..............................
EER
EER
EER
EER
EER
EER
EER
EER
EER
EER
≥135,000 Btu/h and
<240,000 Btu/h.
All ..............................
EER = 9.6 .................
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Water Cooled, Evaporatively Cooled,
and Water-Source.
Large Commercial
Packaged Air Conditioning and Heating Equipment.
Air Cooled .................
Water-Cooled and
Evaporatively
Cooled.
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=
=
=
=
=
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9.3 .................
9.3 .................
10.5 ...............
10.5 ...............
8.5 .................
07OCR3
Products manufactured
on and after
October 29, 2003
=
=
=
=
=
12.1.
12.0.
11.5.2
12.0.
8.5.
EER = 9.6.3
Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
58829
TABLE 1 TO § 431.97—MINIMUM COOLING EFFICIENCY LEVELS—Continued
Efficiency level 1
Product
Category
Sub-category
Products
manufactured until
October 29, 2003
All ..............................
<7,000 Btu/h .............
All ..............................
EER = 8.88 ...............
EER = 8.88.
≥7,000 Btu/h and
≤15,000 Btu/h.
...................................
...................................
EER = 10.0¥(0.16 ×
capacity [in kBtu/h
at 95 °F outdoor
dry-bulb temperature]).
EER = 7.6 .................
EER = 10.0¥(0.16 ×
capacity [in kBtu/h at
95 °F outdoor drybulb temperature]).
>15,000 Btu/h ...........
Packaged Terminal
Air Conditioners
and Heat Pumps.
Cooling capacity
Products manufactured
on and after
October 29, 2003
EER = 7.6.
equipment rated according to the ARI standards, all EER values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled products and evaporatively cooled products and at 85 °F entering water temperature for water-cooled products. For water-source heat pumps rated
according to the ISO standard, EER must be rated at 30 °C (86 °F) entering water temperature.
2 Deduct 0.2 from the required EER for units with heating sections other than electric resistance heat.
3 Effective 10/29/2004, the minimum value became EER = 11.0.
1 For
TABLE 2 TO § 431.97—MINIMUM HEATING EFFICIENCY LEVELS
Efficiency level 1
Product
Category
Products
manufactured until
October 29, 2003
Air Cooled, 3 Phase
<65,000 Btu/h ...........
Split System ..............
Single Package .........
HSPF = 6.8 ...............
HSPF = 6.6 ...............
HSPF = 6.8.
HSPF = 6.6.
<135,000 Btu/h .........
COP = 4.2.
≥65,000 Btu/h and
<135,000 Btu/h.
≥135,000 Btu/h and
<240,000 Btu/h.
Split System and Single Package.
All ..............................
COP = 3.8 .................
Air Cooled .................
Large Commercial
Packaged Air Conditioning and Heating
Equipment.
Packaged Terminal
Heat Pumps.
Sub-category
Water-Source ............
Small Commercial
Packaged Air Conditioning and Heating
Equipment.
Cooling capacity
COP = 3.0 .................
COP = 3.0.
Split System and Single Package.
COP = 2.9 .................
COP = 2.9.
All ..............................
COP = 1.3 + (0.16 ×
the applicable minimum cooling EER
prescribed in Table
1—Minimum Cooling Efficiency Levels).
COP = 1.3 + (0.16 ×
the applicable minimum cooling EER
prescribed in Table
1—Minimum Cooling Efficiency Levels).
Air Cooled .................
All ..............................
All ..............................
Products manufactured on and after
October 29, 2003
1 For units tested by ARI standards, all COP values must be rated at 47 °F outdoor dry-bulb temperature for air-cooled products, and at 70 °F
entering water temperature for water-source heat pumps. For heat pumps tested by the ISO Standard 13256–1, the COP values must be obtained at the rating point with 20 °C (68 °F) entering water temperature.
*
*
*
*
*
(c) Each standard size packaged
terminal air conditioner or packaged
terminal heat pump manufactured on or
after September 30, 2012 and each nonstandard size packaged terminal air
conditioner or packaged terminal heat
pump manufactured on or after
September 30, 2010, shall have an
Energy Efficiency Ratio and Coefficient
of Performance no less than:
Equipment class
Equipment
Category
Cooling capacity (British thermal
units per hour [Btu/h])
PTAC ..............................................
Standard Size ...............................
<7,000 ...........................................
7,000–15,000 ................................
>15,000 .........................................
<7,000 ...........................................
7,000–15,000 ................................
>15,000 .........................................
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Non-Standard Size ........................
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Energy conservation standards *
EER
EER
EER
EER
EER
EER
07OCR3
=
=
=
=
=
=
11.7
13.8¥(0.300 × Cap**)
9.3
9.4
10.9¥(0.213 × Cap**)
7.7
58830
Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 / Rules and Regulations
Equipment class
Equipment
Category
Cooling capacity (British thermal
units per hour [Btu/h])
PTHP ..............................................
Standard Size ...............................
<7,000 ...........................................
7,000–15,000 ................................
>15,000 .........................................
Non-Standard Size ........................
<7,000 ...........................................
7,000–15,000 ................................
>15,000 .........................................
Energy conservation standards *
EER = 11.9
COP = 3.3
EER = 14.0¥(0.300 × Cap**)
COP = 3.7¥(0.052 × Cap**)
EER = 9.5
COP = 2.9
EER = 9.3
COP = 2.7
EER = 10.8¥(0.213 × Cap**)
COP = 2.9¥(0.026 × Cap**)
EER = 7.6
COP = 2.5
* For equipment rated according to the DOE test procedure, all EER values must be rated at 95 °F outdoor dry-bulb temperature for air-cooled
products and evaporatively-cooled products and at 85 °F entering water temperature for water cooled products. All COP values must be rated at
47 °F outdoor dry-bulb temperature for air-cooled products, and at 70 °F entering water temperature for water-source heat pumps.
** Cap means cooling capacity in thousand British thermal units per hour (Btu/h) at 95 °F outdoor dry-bulb temperature.
*
*
*
*
*
APPENDIX
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[The following letter from the Department
of Justice will not appear in the Code of
Federal Regulations.]
DEPARTMENT OF JUSTICE,
Antitrust Division,
Main Justice Building,
950 Pennsylvania Avenue, NW.,
Washington, DC 20530–0001, (202)
514–2401/(202) 616–2645(f),
antitrust@justice.usdoj.gov, https://
www.usdoj.gov.
June 6, 2008
Warren Belmar, Deputy General Counsel for
Energy Policy, Department of Energy,
Washington, DC 20585.
Dear Deputy General Counsel Belmar:
I am responding to your April 3, 2008 letter
seeking the views of the Attorney General
about the potential impact on competition of
two proposed energy conservation standards
for packaged terminal air conditioners
(‘‘PTACs’’) and packaged terminal heat
pumps (‘‘PTHPs’’). Your request was
submitted pursuant to Section
325(o)(2)(B)(i)(V) of the Energy Policy and
Conservation Act, as amended, (‘‘EPCA’’), 42
U.S.C. 6295(o)(B)(i)(V), which requires the
Attorney General to make a determination of
the impact of any lessening of competition
that is likely to result from the imposition of
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proposed energy conservation standards. The
Attorney General’s responsibility for
responding to requests from other
departments about the effect of a program on
competition has been delegated to the
Assistant Attorney General for the Antitrust
Division in 28 CFR 0.40(g).
In conducting its analysis the Antitrust
Division examines whether a proposed
standard may lessen competition, for
example, by placing certain manufacturers of
a product at an unjustified competitive
disadvantage compared to other
manufacturers, or by inducing avoidable
inefficiencies in production or distribution of
particular products. In addition to harming
consumers directly through higher prices,
these effects could undercut the ultimate
goals of the legislation.
We have reviewed the proposed standards
and the supplementary information
submitted to the Attorney General, including
the transcript of the May 1 public meeting on
the proposed standards. We have
additionally conducted interviews with
members of the industry.
What we have heard raises legitimate
issues about whether the proposed standards
may adversely affect competition. The
proposed standard for non-standard PTACs
and PTHPs may create a risk that is too strict
for the manufacturers to satisfy, given the
state of technology.
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Customers that own older buildings with
non-standard wall openings for air
conditioning and heating units could face the
choice of incurring capital expenditures to
alter the size of the wall openings so that
they could use standard sized units, or of not
being able to replace their nonstandard sized
units with units that are appropriately sized
and meet the proposed energy conservation
standards. Similarly, we have heard that the
proposed standards for standard sized PTHPs
may be too strict for manufacturers to satisfy.
Since there are few manufacturers of
standard PTHPs and of nonstandard PTACs
and PTHPs, if some manufacturers cannot
meet the proposed standards, consumers will
have fewer competitive alternatives and may
pay higher prices.
The Department of Justice is not in a
position to judge whether manufacturers will
be able to meet the proposed standards—we
urge, however, the Department of Energy to
take into account these possible impacts on
competition in determining its final energy
efficiency standard for PTACs and PTHPs.
Sincerely,
Deborah A. Garza,
Acting Assistant Attorney General.
[FR Doc. E8–23312 Filed 10–6–08; 8:45 am]
BILLING CODE 6450–01–P
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Agencies
[Federal Register Volume 73, Number 195 (Tuesday, October 7, 2008)]
[Rules and Regulations]
[Pages 58772-58830]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-23312]
[[Page 58771]]
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Part III
Department of Energy
-----------------------------------------------------------------------
10 CFR Part 431
Energy Conservation Program for Commercial and Industrial Equipment:
Packaged Terminal Air Conditioner and Packaged Terminal Heat Pump
Energy Conservation Standards; Final Rule
Federal Register / Vol. 73, No. 195 / Tuesday, October 7, 2008 /
Rules and Regulations
[[Page 58772]]
-----------------------------------------------------------------------
DEPARTMENT OF ENERGY
10 CFR Part 431
[Docket Number: EERE-2007-BT-STD-0012]
RIN 1904-AB44
Energy Conservation Program for Commercial and Industrial
Equipment: Packaged Terminal Air Conditioner and Packaged Terminal Heat
Pump Energy Conservation Standards
AGENCY: Office of Energy Efficiency and Renewable Energy, Department of
Energy.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Department of Energy (DOE) has determined that its
adoption of amended energy conservation standards for commercial
standard size packaged terminal air conditioners (PTACs) and packaged
terminal heat pumps (PTHPs), at efficiency levels more stringent than
those in American Society of Heating, Refrigerating, and Air-
Conditioning Engineers (ASHRAE)/Illuminating Engineering Society of
North America (IESNA) Standard 90.1-1999, is supported by clear and
convincing evidence that such standards would result in significant
additional conservation of energy and are technologically feasible and
economically justified. On this basis, DOE is today amending the
existing energy conservation standards for these types of equipment. In
addition, DOE has determined that its adoption of amended energy
conservation standards more stringent than the efficiency levels
specified by ASHRAE Standard 90.1-1999 for non-standard size PTACs and
PTHPs is not supported by clear and convincing evidence, thus, DOE is
adopting the efficiency levels in ASHRAE Standard 90.1-1999 for non-
standard size PTACs and PTHPs in today's final rule.
DATES: The effective date of this rule is November 6, 2008. The
standards established in today's final rule will be applicable starting
October 8, 2012 for standard size PTACs and PTHPs. The standards
established in today's final rule will be applicable starting October
7, 2010 for non-standard size PTACs and PTHPs.
ADDRESSES: For access to the docket to read background documents, the
technical support document, transcripts of the public meetings in this
proceeding, or comments received, visit the U.S. Department of Energy,
Resource Room of the Building Technologies Program, 950 L'Enfant Plaza,
SW., 6th Floor, Washington, DC 20024, (202) 586-2945, between 9 a.m.
and 4 p.m., Monday through Friday, except Federal holidays. For more
information about visiting the Resource Room, please call Ms. Brenda
Edwards at (202) 586-2945. (Note: DOE's Freedom of Information Reading
Room no longer houses rulemaking materials.) You may also obtain copies
of the final rule notice in this proceeding, related documents (e.g.,
the notice of proposed rulemaking and technical support document DOE
used to reassess whether to adopt certain efficiency levels in ASHRAE
Standard 90.1), draft analyses, public meeting materials, and related
test procedure documents from the Office of Energy Efficiency and
Renewable Energy's Web site at https://www.eere.energy.gov/buildings/
appliance_standards/commercial/packaged_ac_hp.html.
FOR FURTHER INFORMATION CONTACT: Wes Anderson, Project Manager, Energy
Conservation Standards for Packaged Terminal Air Conditioners and
Packaged Terminal Heat Pumps, U.S. Department of Energy, Energy
Efficiency and Renewable Energy, Building Technologies Program, EE-2J,
1000 Independence Avenue, SW., Washington, DC 20585-0121. Phone: (202)
586-7335. E-mail: Wes.Anderson@ee.doe.gov.
Francine Pinto, Esq., or Michael Kido, Esq., U.S. Department of
Energy, Office of General Counsel, GC-72, 1000 Independence Avenue,
SW., Washington, DC 20585. Phone: (202) 586-9507. E-mail:
Francine.Pinto@hq.doe.gov or Michael.Kido@hq.doe.gov.
SUPPLEMENTARY INFORMATION:
I. Summary of the Final Rule and Its Benefits
A. The Standard Levels
B. Current Federal Standards for Packaged Terminal Air
Conditioners and Packaged Terminal Heat Pumps
C. Benefits to Customers of Packaged Terminal Air Conditioners
and Packaged Terminal Heat Pumps
D. Impact on Manufacturers
E. National Benefits
F. Other Considerations
G. Conclusion
II. Introduction
A. Authority
B. Background
1. Current Standards
2. History of Standards Rulemaking for Packaged Terminal
Equipment
III. General Discussion
A. Test Procedures
B. Technological Feasibility
1. General
2. Maximum Technologically Feasible Levels
C. Energy Savings
D. Economic Justification
1. Economic Impact on Commercial Consumers and Manufacturers
2. Life-Cycle Costs
3. Energy Savings
4. Lessening of Utility or Performance of Equipment
5. Impact of Any Lessening of Competition
6. Need of the Nation To Conserve Energy
7. Other Factors
IV. Analysis Methodology and Discussion of Comments on Analysis
Methodology
A. Market and Technology Assessment
1. Equipment Classes--Generally
2. Comments
B. Screening Analysis
1. Scroll Compressors
2. ECM Motors
3. Fan Motors
4. Micro-Channel Heat Exchangers
5. Thermal Expansion Valves
C. Engineering Analysis
1. Material Prices for the Cost Model
2. Impacts of the Refrigerant Phaseout on PTAC and PTHP
Equipment Performance
3. Manufacturer Production Cost Increases With R-410A
D. Energy Use Characterization
E. Life-Cycle Cost Analysis
1. Equipment Prices
2. Installation Costs
3. Annual Energy Use
4. Electricity Prices
5. Maintenance Costs
6. Repair Costs
7. Equipment Lifetime
8. Discount Rate
F. National Impact Analysis--National Energy Savings and Net
Present Value Analysis
1. Shipments Analysis
2. Base Case and Standards Case Forecasted Distribution of
Efficiencies
G. Manufacturer Impact Analysis
1. GRIM Input Updates
2. Cumulative Regulatory Burden
3. Employment Impacts
H. Employment Impact Analysis
I. Utility Impact Analysis
J. Environmental Analysis
K. Other Comments
1. Burdens on Small, Non-Standard Size PTAC and PTHP
Manufacturers
2. PTAC and PTHP Labeling
V. Analytical Results and Conclusions
A. Trial Standard Levels
B. Significance of Energy Savings
C. Economic Justification
1. Economic Impact on Commercial Consumers
2. Economic Impact on Manufacturers
3. National Net Present Value and Net National Employment
4. Impact on Utility or Performance of Equipment
5. Impact of Any Lessening of Competition
6. Need of the Nation to Conserve Energy
7. Other Factors
D. Conclusion
1. Standard Size PTACs and PTHPs
2. Non-Standard Size PTACs and PTHPs
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Order 12866
B. Review Under the Regulatory Flexibility Act
1. Reasons for the Final Rule
2. Objectives of, and Legal Basis for, the Rule
3. Description and Estimated Number of Small Entities Regulated
[[Page 58773]]
4. Description and Estimate of Compliance Requirements
5. Significant Issues Raised by Public Comments
6. Steps DOE Has Taken To Minimize the Economic Impact on Small,
Non-Standard Size PTAC and PTHP Manufacturers
C. Review Under the Paperwork Reduction Act
D. Review Under the National Environmental Policy Act
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 of 1999
I. Review Under Executive Order 12630
J. Review Under the Treasury and General Government
Appropriations Act of 2001
K. Review Under Executive Order 13211
L. Review Under the Information Quality Bulletin for Peer Review
M. Congressional Notification
VII. Approval of the Office of the Secretary
I. Summary of the Final Rule and Its Benefits
A. The Standard Levels
The Energy Policy and Conservation Act, as amended (EPCA), (42
U.S.C. 6291, et seq.), establishes mandatory energy conservation
standards for certain commercial equipment covered by the American
Society of Heating, Refrigerating, and Air-Conditioning Engineers
(ASHRAE) and the Illuminating Engineering Society of North America
(IESNA) Standard 90.1, including packaged terminal air conditioners
(PTACs) and packaged terminal heat pumps (PTHPs) (collectively referred
to as ``packaged terminal equipment''). EPCA states that the Department
of Energy (DOE) may prescribe amended standards for this equipment that
exceed the stringency of efficiency levels contained in amendments to
ASHRAE Standard 90.1, only if DOE determines by rule that any such
standard ``would result in significant additional conservation of
energy and is technologically feasible and economically justified.''
(42 U.S.C. 6313(a)(6)(A)(ii)(II)) This determination must be
``supported by clear and convincing evidence.'' Id. If DOE is unable to
find that clear and convincing evidence exists that a more stringent
efficiency level than the efficiency level contained in ASHRAE Standard
90.1 would result in a significant additional energy savings and is
technologically feasible and economically justified, then EPCA states
DOE must establish an amended uniform national standard for the product
at the minimum level specified in the amended ASHRAE/IES Standard 90.1.
(42 U.S.C. 6313(a)(6)(A)(ii)(I)) The standards in today's final rule,
which apply to all packaged terminal equipment, satisfy these
requirements and will achieve the maximum improvements in energy
efficiency that are technologically feasible and economically
justified. (See 42 U.S.C. 6316(a); 42 U.S.C. 6295(o)(2)(A).)
Table I.1 shows the amended energy conservation standards that DOE
is adopting today. These amended energy conservation standards will
apply to standard size PTACs and PTHPs manufactured for sale in the
United States, or imported to the United States, on or after October 8,
2012 and non-standard size PTACs and PTHPs manufactured for sale in the
United States, or imported to the United States, on or after October 7,
2010.
Table I.1--Amended Energy Conservation Standards for PTACs and PTHPs
------------------------------------------------------------------------
Equipment class
--------------------------------------------------------
Cooling
capacity Energy
(British conservation
Equipment Category thermal units standards *
per hour [Btu/
h])
------------------------------------------------------------------------
PTAC................. Standard Size <7,000......... EER = 11.7
**.
7,000-15,000... EER = 13.8-
(0.300 x Cap
[dagger][dagge
r])
>15,000........ EER = 9.3
--------------------------------------------------
Non-Standard <7,000......... EER = 9.4
Size [dagger].
7,000-15,000... EER = 10.9 -
(0.213 x Cap
[dagger][dagge
r])
>15,000........ EER = 7.7
------------------------------------------------------------------------
PTHP................. Standard Size <7,000......... EER = 11.9
**.
COP = 3.3
7,000-15,000... EER = 14.0 -
(0.300 x Cap
[dagger][dagge
r])
COP = 3.7 -
(0.052 x Cap
[dagger][dagge
r])
>15,000........ EER = 9.5
COP = 2.9
--------------------------------------------------
Non-Standard <7,000......... EER = 9.3
Size [dagger].
COP = 2.7
7,000-15,000... EER = 10.8 -
(0.213 x Cap
[dagger][dagge
r])
COP = 2.9 -
(0.026 x Cap
[dagger][dagge
r])
>15,000........ EER = 7.6
COP = 2.5
------------------------------------------------------------------------
* For equipment rated according to the DOE test procedure (Air-
Conditioning and Refrigeration Institute [ARI] Standard 310/380-2004),
all energy efficiency ratio (EER) values must be rated at 95 [deg]F
outdoor dry-bulb temperature for air-cooled equipment and
evaporatively cooled equipment and at 85 [deg]F entering water
temperature for water-cooled equipment. All coefficient of performance
(COP) values must be rated at 47 [deg]F outdoor dry-bulb temperature
for air-cooled equipment.
** Standard size refers to PTAC or PTHP equipment with wall sleeve
dimensions having an external wall opening greater than or equal to 16
inches high or greater than or equal to 42 inches wide, and a cross-
sectional area greater than or equal to 670 square inches.
[dagger] Non-standard size refers to PTAC or PTHP equipment with
existing wall sleeve dimensions having an external wall opening of
less than 16 inches high or less than 42 inches wide, and a cross-
sectional area less than 670 square inches.
[dagger][dagger] Cap means cooling capacity in thousand Btu/h (kBtu/h)
at 95 [deg]F outdoor dry-bulb temperature.
DOE only presents the benefits and burdens of adopting a standard
level higher than the efficiency levels specified in ASHRAE Standard
90.1-1999. The benefits and burdens of adopting the efficiency levels
in ASHRAE Standard 90.1-1999 for non-standard size PTACs and PTHPs are
not calculated in this rulemaking because
[[Page 58774]]
DOE considers this the baseline efficiency levels even though they
represent an increase in energy efficiency when compared to the current
Federal energy conservation standards.
B. Current Federal Standards for Packaged Terminal Air Conditioners and
Packaged Terminal Heat Pumps
Table I.2 presents the minimum efficiency levels in the current
Federal energy conservation standards for PTACs and PTHPs.
Table I.2--Existing Federal Energy Conservation Standards for PTACs and PTHPs
----------------------------------------------------------------------------------------------------------------
Equipment class
-----------------------------------------------------------
Cooling capacity (Btu/ Existing Federal energy conservation standards*
Equipment h)
----------------------------------------------------------------------------------------------------------------
PTAC............................... <7,000............... EER = 8.88
7,000-15,000......... EER = 10.0 - (0.16 x Cap**)
>15,000.............. EER = 7.6
PTHP............................... <7,000............... EER = 8.88
COP = 2.7
7,000-15,000......... EER = 10.0 - (0.16 x Cap**)
COP = 1.3 + (0.16 x EER)
>15,000.............. EER = 7.6
COP = 2.5
----------------------------------------------------------------------------------------------------------------
* For equipment rated according to the ARI standards, all EER values must be rated at 95 [deg]F outdoor dry-bulb
temperature for air-cooled products and evaporatively cooled products and at 85 [deg]F entering water
temperature for water-cooled products. All COP values must be rated at 47 [deg]F outdoor dry-bulb temperature
for air-cooled products, and at 70 [deg]F entering water temperature for water-source heat pumps.
** Cap means cooling capacity in kBtu/h at 95 [deg]F outdoor dry-bulb temperature.
C. Benefits to Customers of Packaged Terminal Air Conditioners and
Packaged Terminal Heat Pumps
Table I.3 presents the impacts on commercial customers of the
energy conservation standards adopted in today's final rule.
Table I.3--Impacts of New Standards for a Sample of Commercial Customers *
----------------------------------------------------------------------------------------------------------------
Total
Amended energy Total installed Life-cycle Payback
Equipment class conservation standard installed cost cost period
cost increase savings (years)
----------------------------------------------------------------------------------------------------------------
Standard Size PTAC, 9,000 Btu/h 11.1 EER.............. 1,229 $22 ($3) 13.7
Cooling Capacity.
Standard Size PTAC, 12,000 Btu/h 10.2 EER.............. 1,469 16 (2) 13.1
Cooling Capacity.
Standard Size PTHP, 9,000 Btu/h 11.3 EER.............. 1,362 40 28 4.4
Cooling Capacity.
3.2 COP
Standard Size PTHP, 12,000 Btu/h 10.4 EER.............. 1,603 38 24 4.6
Cooling Capacity.
3.0 COP
Non-Standard Size PTAC, 11,000 Btu/h 8.6 EER............... 1,570 ** N/A ** N/A ** N/A
Cooling Capacity.
Non-Standard Size PTHP, 11,000 Btu/h 8.5 EER............... 1,692 ** N/A ** N/A ** N/A
Cooling Capacity.
2.6 COP
----------------------------------------------------------------------------------------------------------------
* The values in Table I.3 represent average values and all monetary values are expressed in 2007$.
** DOE did not calculate the implications on commercial customers of non-standard equipment because DOE is
adopting the efficiency levels in ASHRAE Standard 90.1-1999 (i.e., the baseline efficiency levels).
The economic impacts on commercial consumers (i.e., the average
life-cycle cost (LCC) savings) are positive. For example, the typical,
standard size PTAC with a cooling capacity of 9,000 Btu/h that meets
the existing Federal energy conservation standards has an installed
price of $1,207 and an annual energy cost of $109 (cooling only). A
typical, standard size PTHP of the same cooling capacity that meets the
existing Federal energy conservation standards has an installed price
of $1,362 and an annual energy cost of $209. To meet the new standard,
DOE estimates that the installed price of a typical, standard size PTAC
with a cooling capacity of 9,000 Btu/h will be $1,229, an increase of
$22. This price increase will be offset by an annual energy savings of
about $3. Similarly, for a typical, standard size PTHP of the same
cooling capacity to meet the new standard, the increase in installed
price would be $40, offset by an annual energy savings of $11. Whereas
the typical, non-standard size PTAC that meets the ASHRAE Standard
90.1-1999 efficiency levels has an installed price of $1,570 and an
annual energy cost of $180.
D. Impact on Manufacturers
Using a real corporate discount rate of five-percent, DOE estimates
the net present value (NPV) of the standard size packaged terminal
equipment industry to be $427 million in 2007$ and the NPV of the non-
standard size packaged terminal equipment industry to be $30 million in
2007$. DOE expects the impact of today's standards on the industry net
present value (INPV) of manufacturers of standard size packaged
terminal equipment to be between a two-percent loss and a 14 percent
loss (-$8 million to -$61 million). Based
[[Page 58775]]
on DOE's interviews with the manufacturers of PTACs and PTHPs, DOE
expects minimal plant closings or loss of employment as a result of the
standards for both the standard size and non-standard size industries.
E. National Benefits
DOE estimates the amended energy conservation standards will save
approximately 0.032 quads (quadrillion (1015) Btu) of energy
over 30 years (2012-2042). This is equivalent to all the electricity
used annually by approximately 500 motels.\1\
---------------------------------------------------------------------------
\1\ Energy Informaton Agency. 2003 CBECS public use sample,
where specific building activity = ``motel or inn'' (PBAPLUS8=39).
Anual electricity use averages about 177,700 kWh per yer.
---------------------------------------------------------------------------
By 2042, DOE expects the energy savings from the standards to
eliminate the need for approximately one new 82-megawatt (MW) power
plant. These energy savings will result in cumulative greenhouse gas
emission reductions of approximately 1.06 million tons (Mt) of carbon
dioxide (CO2), or an amount equal to that produced by
approximately 6,700 cars every year. Additionally, the standards will
help alleviate air pollution by resulting in between approximately 90
and 2,130 tons (0.09 and 2.13 kilotons (kt)) of nitrogen oxides
(NOX) cumulative emission reductions from 2012 through 2042.
Finally, the standards will also alleviate air pollution by resulting
in between approximately 0 and 0.037 tons of mercury (Hg) cumulative
emission reductions from 2012 through 2042.
The national NPV of the standard for standard size PTACs and PTHPs
is $10 million using a seven-percent discount rate and $54 million
using a three-percent discount rate, cumulative from 2012 to 2062 in
2007$. This is the estimated total value of future savings minus the
estimated increased equipment costs, discounted to 2008.
The benefits and costs of today's final rule can also be expressed
in terms of annualized 2007$ values over the forecast period 2012
through 2042. Using a seven-percent discount rate for the annualized
cost analysis, the cost of the amended energy conservation standards
established in today's final rule for standard size PTACs and PTHPs is
$4.7 million per year in increased equipment and installation costs
while the annualized benefits are $5.7 million per year in reduced
equipment operating costs. Using a three-percent discount rate, the
cost of the amended energy conservation standards established in
today's final rule for standard size PTACs and PTHPs is $4.1 million
per year, whereas the benefits of today's amended energy conservation
standards are $6.5 million per year.
F. Other Considerations
DOE noted in the April 2008 Notice of Proposed Rulemaking (NOPR)
that PTAC and PTHP equipment manufacturers also face a mandated
refrigerant phaseout on January 1, 2010. 73 FR 18858, 18860 (April 7,
2008). R-22, the only refrigerant currently used by PTACs and PTHPs, is
a hydrochlorofluorocarbon (HCFC) refrigerant subject to the phaseout
requirement. Phaseout of this refrigerant could have a significant
impact on the manufacturing, performance, and cost of PTAC and PTHP
equipment. DOE discussed and estimated the impacts of the refrigerant
phaseout on PTAC and PTHP equipment and on the manufacturers of this
equipment in the NOPR, see generally, 73 FR 18872-74, and today's final
rule.
G. Conclusion
DOE concludes that the benefits (energy savings, commercial
customer LCC savings, positive national NPV, and emissions reductions)
to the Nation of the amended standards for standard size equipment
outweigh their costs (loss of manufacturer INPV and commercial customer
LCC increases for some users of PTACs and PTHPs). DOE believes that
these amended standards are technologically feasible, economically
justified, and will save additional significant amounts of energy as
compared to the savings that would result from adoption of the
efficiency levels for standard size PTACs and PTHPs in ASHRAE Standard
90.1-1999. DOE also believes that the standards for non-standard size
equipment (i.e., the efficiency levels in ASHRAE Standard 90.1-1999)
are technologically feasible, economically justified, and will save
significant amounts of energy compared to the current Federal energy
conservation standards. Finally, DOE concludes that today's standards
for PTACs and PTHPs are designed to achieve the maximum improvements in
energy efficiency that are technologically feasible and economically
justified. Currently, PTACs and PTHPs that meet the new standard levels
are commercially available utilizing R-22 refrigerant. DOE believes
that PTACs and PTHPs utilizing R-410A equipment at the new standard
levels will be commercially available by the effective dates of the new
standard levels.
II. Introduction
A. Authority
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. Part A-1 of Title III (42 U.S.C. 6311-6317)
establishes a similar program for ``Certain Industrial Equipment,''
including PTACs and PTHPs, the subjects of this rulemaking.\2\ DOE
publishes today's final rule pursuant to Part A-1 of Title III, which
provides for test procedures, labeling, and energy conservation
standards for PTACs and PTHPs and certain other equipment, and
authorizes DOE to require information and reports from manufacturers.
The test procedure for PTACs and PTHPs appears in title 10 Code of
Federal Regulations (CFR) section 431.96.
---------------------------------------------------------------------------
\2\ This part was originally titled Part C. However, it was
redesignated Part A-1 after Part B of Title III of EPCA was repealed
by Public Law 109-58.
---------------------------------------------------------------------------
EPCA established Federal energy conservation standards that
generally correspond to the levels in ASHRAE Standard 90.1, effective
October 24, 1992, for most types of covered equipment listed in section
342(a) of EPCA, including PTACs and PTHPs. (42 U.S.C. 6313(a)) For each
type of equipment, EPCA directs that if ASHRAE Standard 90.1 is
amended, DOE must adopt an amended standard at the new level in ASHRAE
Standard 90.1, unless clear and convincing evidence supports a
determination that adoption of a more stringent level as a national
standard would produce significant additional energy savings and be
technologically feasible and economically justified. (42 U.S.C.
6313(a)(6)(A)(ii)(II))
EPCA also provides that in deciding whether a more stringent
standard is economically justified for equipment such as PTACs and
PTHPs, DOE must, after receiving comments on the proposed standard,
determine whether the benefits of such a standard exceed its burdens by
considering the following seven factors to the greatest extent
practicable:
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 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
[[Page 58776]]
result from the imposition of the standard;
3. The total projected amount of energy savings likely to result
directly from the imposition of the standard;
4. Any lessening of the utility or the performance of the 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 conservation; and
7. Other factors the Secretary of Energy (Secretary) considers
relevant. (42 U.S.C. 6316(a); 42 U.S.C. 6295(o)(2)(B)(i)-(ii))
EPCA also contains an ``anti-backsliding'' provision, which
prohibits DOE from prescribing any amended energy conservation standard
that either increases the maximum allowable energy use or decreases the
minimum required energy efficiency of covered equipment. (42 U.S.C.
6316(a); 42 U.S.C. 6295(o)(1)) It is a fundamental principle in EPCA's
statutory scheme that DOE cannot amend standards downward; that is, DOE
may not weaken standards that have been previously promulgated. Natural
Resources Defense Council v. Abraham, 355 F.3d 179 (2d Cir. 2004).
In addition, EPCA, as amended (42 U.S.C. 6295(o)(2)(B)(iii)),
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
(and as applicable, water) savings during the first year that the
consumer will receive as a result of the standard,'' as calculated
under the test procedure in place for that standard. This approach
provides an alternative path in establishing economic justification
under the EPCA factors. (42 U.S.C. 6295(o)(2)(B)(iii)) DOE considered
this test, but believes that the criterion it applies (i.e., a limited
payback period) is not sufficient for determining economic
justification. Instead, DOE has considered a full range of impacts,
including those to the consumer, manufacturer, Nation, and environment.
Additionally, the Secretary may not prescribe an 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 product type (or class)'' with performance
characteristics, features, sizes, capacities, and volumes that are
substantially the same as those generally available in the United
States at the time of the Secretary's finding. (42 U.S.C. 6316(a); 42
U.S.C. 6295(o)(4))
Section 325(q)(1) of EPCA directs that DOE must specify a different
standard level than that which applies generally to such type or class
of equipment for any group of 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 within that
type or class. (42 U.S.C. 6295(q)(1)(A) and (B)) In determining whether
a performance-related feature justifies such 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. (42 U.S.C. 6295(q)(1)) Any rule prescribing such a
standard must include an explanation of the basis on which DOE
established such higher or lower level. (42 U.S.C. 6295(q)(2))
Federal energy efficiency requirements for commercial equipment
generally supersede State laws or regulations concerning energy
conservation testing, labeling, and standards. (42 U.S.C. 6297(a)-(c);
42 U.S.C. 6316(a) and (b)) However, DOE can grant waivers of preemption
for particular State laws or regulations, in accordance with the
procedures and other provisions of section 327(d) of the Act, as
amended. (42 U.S.C. 6297(d); 42 U.S.C. 6316(b)(2)(D))
B. Background
1. Current Standards
As described in greater detail in the NOPR, 73 FR 18861-62, the
current energy conservation standards in EPCA for PTACs and PTHPs apply
to all equipment manufactured on or after January 1, 1994. (42 U.S.C.
6313(a)(3); 10 CFR 431.97) Table I.2 details these standards.
2. History of Standards Rulemaking for Packaged Terminal Equipment
On October 29, 1999, ASHRAE adopted ASHRAE Standard 90.1-1999,
which revised the efficiency levels for various categories of
commercial equipment covered by EPCA, including PTACs and PTHPs. In
amending the ASHRAE Standard 90.1-1989 levels for packaged terminal
equipment, ASHRAE used the equipment classes contained in EPCA, which
are distinguished by equipment type (i.e., air conditioner (PTAC) or
heat pump (PTHP)) and cooling capacity. However, ASHRAE further divided
these classes by wall sleeve dimensions, because they affect the energy
efficiency of PTACs and PTHPs. Table II.1 shows the efficiency levels
in ASHRAE Standard 90.1-1999 for this equipment.
Table II.1--ASHRAE Standard 90.1-1999 Energy Efficiency Levels for PTACs
and PTHPs
------------------------------------------------------------------------
Equipment class
-------------------------------------------------------- ASHRAE standard
Cooling 90.1-1999
Equipment Category capacity (Btu/ efficiency
h) levels *
------------------------------------------------------------------------
PTAC................. Standard Size <7,000......... EER = 11.0
**.
7,000-15,000... EER = 12.5 -
(0.213 x Cap
[dagger][dagge
r])
>15,000........ EER = 9.3
--------------------------------------------------
Non-Standard <7,000......... EER = 9.4
Size [dagger].
7,000-15,000... EER = 10.9 -
(0.213 x Cap
[dagger][dagge
r])
>15,000........ EER = 7.7
------------------------------------------------------------------------
PTHP................. Standard Size <7,000......... EER = 10.8
**. COP = 3.0
7,000-15,000.. EER = 12.3 -
(0.213 x Cap
[dagger][dagge
r])
COP = 3.2 -
(0.026 x Cap
[dagger][dagge
r])
[[Page 58777]]
>15,000........ EER = 9.1
COP = 2.8
--------------------------------------------------
Non-Standard <7,000......... EER = 9.3
Size [dagger]. COP = 2.7
7,000-15,000... EER = 10.8 -
(0.213 x Cap
[dagger][dagge
r])
COP = 2.9 -
(0.026 x Cap
[dagger][dagge
r])
>15,000........ EER = 7.6
COP = 2.5
------------------------------------------------------------------------
* For equipment rated according to ARI standards, all EER values must be
rated at 95 [deg]F outdoor dry-bulb temperature for air-cooled
products and evaporatively cooled products and at 85 [deg]F entering
water temperature for water-cooled products. All COP values must be
rated at 47 [deg]F outdoor dry-bulb temperature for air-cooled
products.
** Standard size refers to PTAC or PTHP equipment with wall sleeve
dimensions greater than or equal to 16 inches high, or greater than or
equal to 42 inches wide.
[dagger] Non-standard size refers to PTAC or PTHP equipment with wall
sleeve dimensions less than 16 inches high and less than 42 inches
wide. ASHRAE Standard 90.1-1999 also includes a factory labeling
requirement for non-standard size PTAC and PTHP equipment as follows:
``MANUFACTURED FOR REPLACEMENT APPLICATIONS ONLY; NOT TO BE INSTALLED
IN NEW CONSTRUCTION PROJECTS.''
[dagger][dagger] Cap means cooling capacity in kBtu/h at 95 [deg]F
outdoor dry-bulb temperature.
After publication of ASHRAE Standard 90.1-1999, DOE analyzed many
of its equipment categories to evaluate possible consideration of more
stringent efficiency levels than those specified in the Standard. DOE
summarized this analysis in a report, Screening Analysis for EPACT-
Covered Commercial HVAC [Heating, Ventilating and Air-Conditioning] and
Water-Heating Equipment (commonly referred to as the 2000 Screening
Analysis).\3\ On January 12, 2001, DOE published a final rule adopting
the efficiency levels in ASHRAE Standard 90.1-1999 for many types of
commercial HVAC and water heating equipment, excluding packaged
terminal equipment and certain other types of equipment. 66 FR 3336.
Regarding PTACs and PTHPs, the preamble to the final rule stated that
the 2000 Screening Analysis indicated at least a reasonable possibility
of finding ``clear and convincing evidence'' that more stringent
standards ``would be technologically feasible and economically
justified and would result in significant additional conservation of
energy.'' 66 FR 3349-50. Under EPCA, these are the criteria for DOE's
adoption of standards more stringent than the efficiency levels in
ASHRAE Standard 90.1. (42 U.S.C. 6313(a)(6)(A)(ii)(II)).
---------------------------------------------------------------------------
\3\ U.S. Department of Energy, Office of Energy Efficiency and
Renewable Energy. ``Energy Conservation Program for Consumer
Products: Screening Analysis for EPACT-Covered Commercial HVAC and
Water-Heating Equipment Screening Analysis.'' April 2000. https://
www.eere.energy.gov/buildings/highperformance/pdfs/screening_
analysis_main.pdf.
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More recently, DOE announced the availability of a technical
support document (TSD) it developed to reassess whether to adopt as
national standards certain efficiency levels that were in amendments to
ASHRAE Standard 90.1, including the levels in the 1999 amendments for
PTACs and PTHPs. 71 FR 12634 (March 13, 2006) (Notice of Availability).
According to DOE, although the revised analysis in the TSD reduced the
potential energy savings that might result from standards more
stringent than the efficiency levels specified in ASHRAE Standard 90.1-
1999 for PTACs and PTHPs, DOE was inclined to pursue standards that are
more stringent because there was a possibility that clear and
convincing evidence exists that such standards are warranted. Id. at
12638-39. DOE stated that it would explore more stringent efficiency
levels than those in ASHRAE Standard 90.1-1999 for PTACs and PTHPs
through a separate rulemaking. Id. at 12639.
DOE proposed energy conservation standards for PTACs and PTHPs in a
NOPR published on April 7, 2008. 73 FR 18858. In conjunction with the
NOPR, DOE also published on its Web site the complete TSD for the
proposed rule, which incorporated the final analyses that DOE conducted
and technical support documentation of each analysis. The NOPR TSD
included the LCC spreadsheets, the national impact analysis
spreadsheets, and the manufacturer impact analysis (MIA) spreadsheet--
all of which are available on DOE's PTAC and PTHP webpage. The proposed
standards were as follows:
Table II.2--NOPR Proposed Energy Conservation Standards for PTACs and
PTHPs
------------------------------------------------------------------------
Equipment class
-------------------------------------------------------- Proposed energy
Cooling conservation
Equipment Category capacity (Btu/ standards *
h)
------------------------------------------------------------------------
PTAC................. Standard Size <7,000......... EER = 11.4
**.
7,000-15,000... EER = 13.0-
(0.233 x Cap
[dagger][dagge
r])
>15,000........ EER = 9.5
--------------------------------------------------
Non-Standard <7,000......... EER = 10.2
Size.
7,000-15,000... EER = 11.7-
(0.213 x Cap
[dagger][dagge
r])
>15,000........ EER = 8.5
------------------------------------------------------------------------
[[Page 58778]]
PTHP................. Standard Size <7,000......... EER = 11.8
**. COP = 3.3
7,000-15,000... EER = 13.4-
(0.233 x Cap
[dagger][dagge
r])
COP = 3.7-
(0.053 x Cap
[dagger][dagge
r])
>15,000........ EER = 9.9
COP = 2.9
--------------------------------------------------
Non-Standard <7,000......... EER = 10.8
Size. COP = 3.0
7,000-15,000... EER = 12.3-
(0.213 x Cap
[dagger][dagge
r])
COP = 3.1-
(0.026 x Cap
[dagger][dagge
r])
>15,000........ EER = 9.1
COP = 2.8
------------------------------------------------------------------------
* For equipment rated according to the DOE test procedure (ARI Standard
310/380-2004), all EER values must be rated at 95 [deg]F outdoor dry-
bulb temperature for air-cooled equipment and evaporatively cooled
equipment and at 85 [deg]F entering water temperature for water-cooled
equipment. All COP values must be rated at 47 [deg]F outdoor dry-bulb
temperature for air-cooled equipment, and at 70 [deg]F entering water
temperature for water-source heat pumps.
** Standard size refers to PTAC or PTHP equipment with wall sleeve
dimensions greater than or equal to 16 inches high, or greater than or
equal to 42 inches wide.
[dagger] Non-standard size refers to PTAC or PTHP equipment with wall
sleeve dimensions less than 16 inches high and less than 42 inches
wide.
[dagger][dagger] Cap means cooling capacity in kBtu/h at 95 [deg]F
outdoor dry-bulb temperature.
The NOPR also included additional background information on the
history of this rulemaking. 73 FR 18862-63. DOE held a public meeting
in Washington, DC, on May 1, 2008, to accept oral comments on and
solicit information relevant to the proposed rule.
III. General Discussion
A. Test Procedures
Section 343(a) of EPCA, as amended, authorizes the Secretary to
amend the test procedures for PTACs and PTHPs to the latest version
generally accepted by industry or the rating procedures developed or
recognized by the ARI, or ASHRAE as referenced in ASHRAE Standard 90.1,
unless the Secretary determines by clear and convincing evidence that
the latest version of the industry test procedure does not meet
specific requirements. (See 42 U.S.C. 6314(a)(4) As the NOPR explains,
DOE has determined that its existing test procedure for PTACs and PTHPs
does not need modification. 73 FR 18863. Accordingly, DOE has not
adopted a revised test procedure for this equipment.
B. Technological Feasibility
1. General
To adopt standards for PTACs and PTHPs that are more stringent than
the efficiency levels in ASHRAE Standard 90.1 as amended, DOE must
determine, supported by clear and convincing evidence, that such
standards are technologically feasible. (42 U.S.C.
6313(a)(6)(A)(ii)(II)) DOE considers a design option to be
technologically feasible if it is in use by the respective industry or
if research has progressed to the development of a working prototype.
DOE defines technological feasibility as follows: ``Technologies
incorporated in commercially available products or in working
prototypes will be considered technologically feasible.'' 10 CFR part
430, subpart C, appendix A, section 4(a)(4)(i).
This final rule considers the same design options as those
evaluated in the NOPR. (See the final rule TSD accompanying this
notice, Chapter 4.) Based on equipment literature, the teardown
analysis, manufacturer interviews, and the equipment performance
degradations provided by AHRI during the NOPR phase of the rulemaking,
DOE considered the following design options in the final rule analysis:
(1) Higher efficiency compressors; (2) increasing the heat exchanger
area; and (3) recircuiting the heat exchanger coils. Since these three
design options are commercially available, have been used in PTAC and
PTHP equipment, and are the most common ways by which manufacturers
improve the energy efficiency of their PTACs and PTHPs, DOE has
determined that clear and convincing evidence supports the conclusion
that all of the efficiency levels evaluated in this notice are
technologically feasible. DOE further discusses the technical
feasibility of PTAC and PTHP equipment utilizing R-410A in section
IV.C. of today's notice.
2. Maximum Technologically Feasible Levels
In order to evaluate whether energy conservation standards for
PTACs and PTHPs are economically justified, DOE determines the maximum
improvement in energy efficiency or maximum reduction in energy use
that is technologically feasible. (42 U.S.C. 6316(a); 42 U.S.C.
6295(p)(2)) DOE determined the maximum technologically feasible level
(``max-tech'') efficiency levels in its engineering analysis for the
NOPR. 73 FR 18863-64. (See NOPR TSD Chapter 5.) In the NOPR, DOE based
its identification of the max-tech efficiency levels on standard size
and non-standard size PTAC and PTHP equipment utilizing R-22 that is
currently available on the market. For the final rule, DOE revised the
max-tech efficiency levels for standard size and non-standard size
PTACs and PTHPs based on submitted comments, which are discussed in
section IV.C of today's notice. The max-tech efficiency levels
considered for today's final rule are based on the efficiency levels
identified in the NOPR and factor performance degradations stemming
from the switch to R-410A refrigerant.\4\ Table III.1 lists the max-
tech efficiency levels that DOE identified for this rulemaking for the
[[Page 58779]]
estimated system performance of equipment utilizing R-410A. DOE
discusses these levels further in section IV.C.
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\4\ DOE expects the overall system efficiency of R-410A PTAC and
PTHP equipment will be lower than if that equipment used R-22, which
DOE estimated using an overall system performance degradation. This
estimate is based on data submitted by manufacturers and AHRI
pointing to a decline in performance when using R-410A refrigerant
in place of R-22 refrigerant.
Table III.1--R-410A Max-Tech Efficiency Levels (7,000-15,000 Btu/h
Equipment Classes) *
------------------------------------------------------------------------
R-410A ``Max-
Cooling Tech''
Equipment type Equipment class capacity (Btu/ efficiency
h) level **
------------------------------------------------------------------------
PTAC................. Standard Size 9,000.......... 11.5 EER
[dagger].
12,000......... 10.8 EER
--------------------------------------------------
Non-Standard 11,000......... 10.0 EER
Size
[dagger][dagge
r].
------------------------------------------------------------------------
PTHP................. Standard Size 9,000.......... 11.5 EER
[dagger]. 3.3 COP
12,000......... 10.8 EER
3.1 COP
--------------------------------------------------
Non-Standard 11,000......... 10.0 EER
Size 2.9 COP
[dagger][dagge
r].
------------------------------------------------------------------------
* As discussed in the NOPR, DOE is presenting the results for two
cooling capacities of standard size PTACs and PTHPs, 9,000 and 12,000
Btu/h, which fall within the equipment classes of PTACs and PTHPs with
cooling capacities of 7,000-15,000 Btu/h. 73 FR 18870-18871.
** For equipment rated according to the DOE test procedure, all EER
values would be rated at 95 [deg]F outdoor dry-bulb temperature for
air-cooled products and evaporatively cooled products and at 85 [deg]F
entering water temperature for water-cooled products. All COP values
must be rated at 47 [deg]F outdoor dry-bulb temperature for air-cooled
products and at 70 [deg]F entering water temperature for water-source
heat pumps.
[dagger] Standard size refers to PTAC or PTHP equipment with wall sleeve
dimensions having an external wall opening of greater than or equal to
16 inches high or greater than or equal to 42 inches wide, and having
a cross-sectional area greater than or equal to 670 square inches.
[dagger][dagger] Non-standard size refers to PTAC or PTHP equipment with
existing wall sleeve dimensions having an external wall opening of
less than 16 inches high or less than 42 inches wide, and having a
cross-sectional area less than 670 square inches.
C. Energy Savings
DOE forecasted energy savings in its national energy savings (NES)
analysis using an NES spreadsheet tool, which the NOPR discussed in
greater detail. See generally, 73 FR 18864, 18876, 18880-83, 18899.
Among the criteria that govern DOE's adoption of more stringent
standards for PTACs and PTHPs than the amended levels in ASHRAE
Standard 90.1, clear and convincing evidence must support a
determination that the standards would result in ``significant'' energy
savings. (42 U.S.C. 6313(a)(6)(A)(ii)(II)) Although EPCA does not
define ``significant,'' the U.S. Court of Appeals for the District of
Columbia indicated that Congress intended ``significant'' energy
savings to mean savings that were not ``genuinely trivial'' in Section
325 of the Act. Natural Resources Defense Council v. Herrington, 768
F.2d 1355, 1373 (D.C. Cir. 1985). DOE's estimates of the energy savings
for each of the TSLs considered for today's rule provide clear and
convincing evidence that the additional energy savings each would
achieve by exceeding the corresponding efficiency levels in ASHRAE
Standard 90.1-1999 are nontrivial. Therefore, DOE considers these
savings to be ``significant'' as required by 42 U.S.C.
6313(a)(6)(A)(ii)(II).
D. Economic Justification
As noted earlier, EPCA provides seven factors to be evaluated in
determining whether an energy conservation standard for PTACs and PTHPs
is economically justified. (42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)-(ii)) The following paragraphs discuss how DOE has
addressed each of those seven factors in this rulemaking.
1. Economic Impact on Commercial Consumers and Manufacturers
DOE considered the economic impact of the standards on commercial
consumers and manufacturers. For customers, DOE measures the economic
impact as the change in installed cost and life-cycle operating costs,
i.e., the LCC. (See section V.C.1 and Chapter 8 of the TSD.) DOE
investigates the impacts of amended energy conservation standards of
PTACs and PTHPs on manufacturers through the manufacturer impact
analysis (MIA). (See section V.C.2 and Chapter 13 of the TSD.) This
factor is discussed in detail in the NOPR. See generally 73 FR 18860-
61, 18864-66, 18869, 18883-87, 18893-99, 18906-07, 18910-12.
2. Life-Cycle Costs
DOE considered life-cycle costs of PTACs and PTHPs. This factor is
discussed in detail in the NOPR. See generally 73 FR 18860-61, 18865,
18876-80, 18883, 18888, 18891-93. DOE calculated the sum of the
purchase price and the operating expense--discounted over the lifetime
of the equipment--to estimate the range in LCC benefits that commercial
customers would expect to achieve due to the standards.
3. Energy Savings
Although significant additional conservation of energy is a
separate statutory requirement for imposing a more stringent energy
conservation standard than the level in the most current ASHRAE
Standard 90.1, EPCA also requires that DOE consider the total projected
energy savings that will likely result directly from the standard in
determining whether a standard is economically justified. (42 U.S.C.
6316(a); 42 U.S.C. 6295(o)(2)(B)(i)(III)) DOE used the NES spreadsheet
results in its consideration of total projected savings. 73 FR 18860-
61, 18864, 18876, 18880-83, 18899. DOE presents the energy savings at
each TSL for standard size and non-standard size PTACs and PTHPs in
section V.B of today's notice.
4. Lessening of Utility or Performance of Equipment
In selecting today's standard levels, DOE sought to avoid new
standards for PTACs and PTHPs that would lessen the utility or
performance of that equipment. (42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)(IV)) 73 FR 18865, 18866-68, 18900. The design options
considered in the engineering analysis of this rulemaking, which
include higher efficiency compressors, increasing the heat exchanger
area, and recircuiting the heat exchanger coils, do not involve changes
in equipment design or unusual installation requirements that could
reduce the utility or performance of PTACs and PTHPs. In the NOPR, DOE
considered
[[Page 58780]]
industry concerns that one-third of the non-standard size market
subject to the more stringent standards under ASHRAE Standard 90.1-1999
definition would not be able to meet the efficiency levels specified by
ASHRAE Standard 90.1-1999 for standard size equipment due to the
physical size constraints of the wall sleeve if this equipment class
delineation was adopted. In today's final rule, DOE is adopting the
equipment class delineations specified in Addendum t to ASHRAE Standard
90.1-2007. This action should mitigate manufacturers' concerns
regarding the misclassification of non-standard equipment classes. DOE
further discusses the equipment classes it is adopting today and the
comments received from interested parties regarding equipment classes
in section IV.A of today's rulemaking.
5. Impact of Any Lessening of Competition
DOE considers any lessening of competition likely to result from
standards. As discussed in the NOPR (73 FR 18865, 18900), DOE requested
that the Attorney General transmit to the Secretary a written
determination of the impact of any lessening of competition likely to
result from the proposed standards, together with an analysis of the
nature and extent of such impact. (42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)(V) and (B)(ii))
To assist the Attorney General in making such a determination, DOE
provided DOJ with copies of the proposed rule and the TSD for review.
(DOJ, No. 21 at p. 1-2) \5\ The Attorney General's response is
discussed in section IV.K.1, and is reprinted at the end of today's
rulemaking.
---------------------------------------------------------------------------
\5\ ``DOJ, No. 21 at pp 1-2'' refers to (1) a statement that was
submitted by the Department of Justice and is recorded in the
Resource Room of the Building Technologies Program in the docket
under ``Energy Conservation Program for Commercial and Industrial
Equipment: Packaged Terminal Air Conditioner and Packaged Terminal
Heat Pump Energy Conservation Standards,'' Docket Number EERE-2007-
BT-STD-0012, as comment number 21; and (2) a passage that appears on
pages 1 and 2 of that statement.
---------------------------------------------------------------------------
6. Need of the Nation To Conserve Energy
In considering standards for PTACs and PTHPs, the Secretary must
consider the need of the Nation to conserve energy. (42 U.S.C. 6316(a);
42 U.S.C. 6295(o)(2)(B)(i)(VI)) The Secretary recognizes that energy
conservation benefits the Nation in several important ways. The non-
monetary benefits of the standards will likely be reflected in
improvements to the security and reliability of the Nation's energy
system. Today's standards also will likely result in environmental
benefits. As discussed in the proposed rule, DOE has considered these
factors in adopting today's standards. See generally, 73 FR at 18860,
18865, 18888, 18900-02, 18912.
7. Other Factors
In determining whether a standard is economically justified, EPCA
directs the Secretary of Energy to consider any other factors that the
Secretary deems to be relevant. (42 U.S.C. 6316(a); 42 U.S.C.
6295(o)(2)(B)(i)(VII)) In adopting today's standard, DOE considered (1)
the impacts of setting different amended standards for PTACs and PTHPs,
(2) the potential that amended standards could cause equipment
switching (i.e., purchase of PTACs instead of PTHPs) and the effects of
any such switching, (3) the uncertainties associated with the impending
phaseout in 2010 of R-22 refrigerant, and (4) the impact of amended
standards on the manufacture of and market for non-standard size
packaged terminal equipment (e.g., impacts on small businesses). See
generally, 73 FR at 18860, 18865-66, 18872-74, 18882, 18884-87, 18893-
98, 18902, 18911-12.
IV. Analysis Methodology and Discussion of Comments on Analysis
Methodology
DOE used several analytical tools that it developed previously and
adapted for use in this rulemaking. The first tool is a spreadsheet
that calculates LCC and payback period (PBP). The second tool
calculates national energy savings and national NPV. DOE also used the
Government Regulatory Impact Model (GRIM), among other methods, in its
MIA. Finally, DOE developed an approach using the National Energy
Modeling System (NEMS) to estimate impacts of PTAC and PTHP energy
efficiency standards on electric utilities and the environment. The
NOPR discusses each analytical tool in detail. 73 FR at 18866-89.
As a basis for this final rule, DOE has continued to use the
spreadsheets and approaches described above and in the NOPR. DOE used
the same general methodology as applied in the NOPR, but revised some
of the assumptions and inputs for the final rule in response to
comments from interested parties. The following paragraphs discuss
these revisions.
A. Market and Technology Assessment
When beginning an energy conservation standards rulemaking, DOE
develops information that provides an overall picture of the market for
the equipment concerned, including the purpose of the equipment, the
industry structure, and market characteristics. This activity includes
both quantitative and qualitative assessments based primarily on
publicly available information. DOE presented various subjects in the
market and technology assessment for this rulemaking. (See the NOPR and
Chapter 3 of the NOPR TSD.) These include equipment classes,
manufacturers, quantities and types of equipment sold and offered for
sale, retail market trends, and regulatory and nonregulatory programs.
73 FR 18866-69 and Chapter 3 of the NOPR TSD. In response to
publication of the NOPR, DOE received comments from interested parties
about the establishment of equipment classes for the rulemaking.
1. Equipment Classes--Generally
When evaluating and establishing energy conservation standards, DOE
generally divides covered equipment into equipment classes by the type
of energy used, capacity, or other performance-related features that
affect efficiency. Different energy conservation standards may apply to
different equipment classes. (42 U.S.C. 6316(a); 42 U.S.C. 6295(q))
PTACs and PTHPs can be divided into various equipment classes
categorized by physical characteristics that affect equipment
efficiency. Key characteristics that affect the energy efficiency of
t