Energy Conservation Program: Energy Conservation Standards for Microwave Ovens, 39912-39960 [2023-12958]
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
10 CFR Part 430
[EERE–2017–BT–STD–0023]
RIN 1904–AE00
Energy Conservation Program: Energy
Conservation Standards for Microwave
Ovens
Office of Energy Efficiency and
Renewable Energy, Department of
Energy.
ACTION: Final rule.
AGENCY:
The Energy Policy and
Conservation Act, as amended
(‘‘EPCA’’), prescribes energy
conservation standards for various
consumer products and certain
commercial and industrial equipment,
including microwave ovens. EPCA also
requires the U.S. Department of Energy
(‘‘DOE’’) to periodically determine
whether more stringent standards would
be technologically feasible and
economically justified, and whether
they would result in significant energy
savings. In this final rule, DOE is
adopting amended energy conservation
standards for microwave ovens. It has
determined that the amended energy
conservation standards for these
products would result in significant
conservation of energy and are
technologically feasible and
economically justified.
DATES: The effective date of this rule is
August 21, 2023. Compliance with the
amended standards established for
microwave ovens in this final rule is
required on and after June 22, 2026.
ADDRESSES: The docket for this
rulemaking, which includes Federal
Register notices, public meeting
attendee lists and transcripts,
comments, and other supporting
documents/materials, is available for
review at www.regulations.gov. All
documents in the docket are listed in
the www.regulations.gov index.
However, not all documents listed in
the index may be publicly available,
such as information that is exempt from
public disclosure.
The docket web page can be found at
www.regulations.gov/docket/EERE2017-BT-STD-0023. The docket web
page contains instructions on how to
access all documents, including public
comments, in the docket.
For further information on how to
review the docket, contact the
Appliance and Equipment Standards
Program staff at (202) 287–1445 or by
email: ApplianceStandardsQuestions@
ee.doe.gov.
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SUMMARY:
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Dr.
Carl Shapiro, U.S. Department of
Energy, Office of Energy Efficiency and
Renewable Energy, Building
Technologies Office, EE–2J, 1000
Independence Avenue SW, Washington,
DC 20585–0121. Telephone: (202) 287–
5649. Email:
ApplianceStandardsQuestions@
ee.doe.gov.
Ms. Celia Sher, U.S. Department of
Energy, Office of the General Counsel,
GC–33, 1000 Independence Avenue
SW., Washington, DC, 20585–0121.
Telephone: (202) 287–6122. Email:
Celia.Sher@hq.doe.gov.
SUPPLEMENTARY INFORMATION:
FOR FURTHER INFORMATION CONTACT:
DEPARTMENT OF ENERGY
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Table of Contents
I. Synopsis of the Final Rule
A. Benefits and Costs to Consumers
B. Impact on Manufacturers
C. National Benefits and Costs
D. Conclusion
II. Introduction
A. Authority
B. Background
1. Current Standards
2. History of Standards Rulemaking for
Microwave Ovens
III. General Discussion
A. Scope of Coverage
B. Test Procedure
C. Technological Feasibility
1. General
2. Maximum Technologically Feasible
Levels
D. Energy Savings
1. Determination of Savings
2. Significance of Savings
E. Economic Justification
1. Specific Criteria
a. Economic Impact on Manufacturers and
Consumers
b. Savings in Operating Costs Compared To
Increase in Price (LCC and PBP)
c. Energy Savings
d. Lessening of Utility or Performance of
Products
e. Impact of Any Lessening of Competition
f. Need for National Energy Conservation
g. Other Factors
2. Rebuttable Presumption
IV. Methodology and Discussion of Related
Comments
1. Market and Technology Assessment
2. Product Classes
3. Technology Options
B. Screening Analysis
1. Screened-Out Technologies
2. Remaining Technologies
C. Engineering Analysis
1. Efficiency Analysis
a. Baseline Efficiency/Energy Use
b. Higher Efficiency Levels
2. Cost Analysis
3. Cost-Efficiency Results
D. Markups Analysis
E. Energy Use Analysis
F. Life-Cycle Cost and Payback Period
Analysis
1. Product Cost
2. Installation Cost
3. Annual Energy Consumption
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4. Energy Prices
5. Maintenance and Repair Costs
6. Product Lifetime
7. Discount Rates
8. Energy Efficiency Distribution in the NoNew-Standards Case
9. Payback Period Analysis
G. Shipments Analysis
H. National Impact Analysis
1. Product Efficiency Trends
2. National Energy Savings
3. Net Present Value Analysis
I. Consumer Subgroup Analysis
J. Manufacturer Impact Analysis
1. Overview
2. Government Regulatory Impact Model
and Key Inputs
a. Manufacturer Production Costs
b. Shipments Projections
c. Product and Capital Conversion Costs
d. Markup Scenarios
3. Discussion of MIA Comments
K. Emissions Analysis
1. Air Quality Regulations Incorporated in
DOE’s Analysis
L. Monetizing Emissions Impacts
1. Monetization of Greenhouse Gas
Emissions
a. Social Cost of Carbon
b. Social Cost of Methane and Nitrous
Oxide
2. Monetization of Other Emissions
Impacts
M. Utility Impact Analysis
N. Employment Impact Analysis
V. Analytical Results and Conclusions
A. Trial Standard Levels
B. Economic Justification and Energy
Savings
1. Economic Impacts on Individual
Consumers
a. Life-Cycle Cost and Payback Period
b. Consumer Subgroup Analysis
c. Rebuttable Presumption Payback
2. Economic Impacts on Manufacturers
a. Industry Cash Flow Analysis Results
b. Direct Impacts on Employment
c. Impacts on Manufacturing Capacity
d. Impacts on Subgroups of Manufacturers
e. Cumulative Regulatory Burden
3. National Impact Analysis
a. Significance of Energy Savings
b. Net Present Value of Consumer Costs
and Benefits
c. Indirect Impacts on Employment
4. Impact on Utility or Performance of
Products
5. Impact of Any Lessening of Competition
6. Need of the Nation To Conserve Energy
7. Other Factors
8. Summary of Economic Impacts
C. Conclusion
1. Benefits and Burdens of TSLs
Considered for Microwave Ovens
Standards
2. Annualized Benefits and Costs of the
Adopted Standards
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Orders 12866
and 13563
B. Review Under the Regulatory Flexibility
Act
C. Review Under the Paperwork Reduction
Act
D. Review Under the National
Environmental Policy Act of 1969
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E. Review Under Executive Order 13132
F. Review Under Executive Order 12988
G. Review Under the Unfunded Mandates
Reform Act of 1995
H. Review Under the Treasury and General
Government Appropriations Act, 1999
I. Review Under Executive Order 12630
J. Review Under the Treasury and General
Government Appropriations Act, 2001
K. Review Under Executive Order 13211
L. Information Quality
M. Congressional Notification
VII. Approval of the Office of the Secretary
I. Synopsis of the Final Rule
The Energy Policy and Conservation
Act, Public Law 94–163, as amended
(‘‘EPCA’’),1 authorizes DOE to regulate
the energy efficiency of a number of
consumer products and certain
industrial equipment. (42 U.S.C. 6291–
6317) Title III, Part B of EPCA 2
established the Energy Conservation
Program for Consumer Products Other
Than Automobiles. (42 U.S.C. 6291–
6309) These products include
microwave ovens, the subject of this
rulemaking.
Pursuant to EPCA, any new or
amended energy conservation standard
must be designed to achieve the
maximum improvement in energy
efficiency that DOE determines is
technologically feasible and
economically justified. (42 U.S.C.
6295(o)(2)(A)) Furthermore, the new or
amended standard must result in
significant conservation of energy. (42
U.S.C. 6295(o)(3)(B)) EPCA also
provides that not later than 6 years after
issuance of any final rule establishing or
amending a standard, DOE must publish
either a notice of determination that
standards for the product do not need to
be amended, or a notice of proposed
rulemaking including new proposed
energy conservation standards
(proceeding to a final rule, as
appropriate). (42 U.S.C. 6295(m))
In accordance with these and other
statutory provisions discussed in this
document, DOE is adopting amended
energy conservation standards for
microwave ovens. The adopted
standards, which are expressed in watts
(‘‘W’’), are shown in Table I.1. These
standards apply to all products listed in
Table I.1 and manufactured in, or
imported into, the United States starting
on June 22, 2026.
TABLE I.1—ENERGY CONSERVATION
STANDARDS
FOR
MICROWAVE
OVENS (COMPLIANCE STARTING
JUNE 22, 2026)
Maximum
allowable
average
standby
power,
(watts)
Product class
PC 1: Microwave-Only
Ovens and Countertop
Convection Microwave
Ovens.
PC 2: Built-In and Over-theRange Convection Microwave Ovens.
0.6 W
1.0 W
A. Benefits and Costs to Consumers
Table I.2 summarizes DOE’s
evaluation of the economic impacts of
the adopted standards on consumers of
microwave ovens, as measured by the
average life-cycle cost (‘‘LCC’’) savings
and the simple payback period
(‘‘PBP’’).3 The average LCC savings are
positive for all product classes, and the
PBP is less than the average lifetime of
microwave ovens, which is estimated to
be 10.78 years (see section IV.F of this
document).
TABLE I.2—IMPACTS OF ADOPTED ENERGY CONSERVATION STANDARDS ON CONSUMERS OF MICROWAVE OVENS
Average LCC
savings
(2021$)
Product class
PC 1: Microwave-Only Ovens and Countertop Convection Microwave Ovens ......................................................
PC 2: Built-In and Over-the-Range Convection Microwave Ovens ........................................................................
DOE’s analysis of the impacts of the
adopted standards on consumers is
described in section IV.F of this
document.
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B. Impact on Manufacturers
the adopted standards, DOE estimates
the change in INPV to range from
¥$37.2 million, which represents a
change of ¥2.6 percent, to no change in
INPV. In order to bring products into
compliance with amended standards, it
is estimated that industry will incur
total conversion costs of $46.1 million.
DOE’s analysis of the impacts of the
adopted standards on manufacturers is
described in sections IV.J and V.B.2 of
this document.
The industry net present value
(‘‘INPV’’) is the sum of the discounted
cash flows to the industry from the base
year through the end of the analysis
period (2023–2055). Using a real
discount rate of 8.5 percent, DOE
estimates that the INPV for
manufacturers of microwave ovens in
the case without amended standards is
$1,426 million in 2021 dollars. Under
DOE’s analyses indicate that the
adopted energy conservation standards
1 All references to EPCA in this document refer
to the statute as amended through the Energy Act
of 2020, Public Law 116–260 (Dec. 27, 2020), which
reflect the last statutory amendments that impact
Parts A and A–1 of EPCA.
2 For editorial reasons, upon codification in the
U.S. Code, Part B was redesignated Part A.
3 The average LCC savings refer to consumers that
are affected by a standard and are measured relative
to the efficiency distribution in the no-new-
standards case, which depicts the market in the
compliance year in the absence of new or amended
standards (see section [IV.F.9] of this document).
The simple PBP, which is designed to compare
specific efficiency levels, is measured relative to the
baseline product (see section IV.C of this
document).
4 All monetary values in this document are
expressed in 2021 dollars. and, where appropriate,
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C. National Benefits and Costs 4
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0.99
0.83
Simple
payback
period
(years)
1.3
0.8
for microwave ovens would save a
significant amount of energy. Relative to
the case without amended standards,
the lifetime energy savings for
microwave ovens purchased in the 30year period that begins in the
anticipated year of compliance with the
amended standards (2026–2055),
amount to 0.06 quadrillion British
thermal units (‘‘Btu’’), or quads.5 This
represents a savings of 19 percent
relative to the energy use of these
products in the case without amended
standards (referred to as the ‘‘no-newstandards case’’).
are discounted to 2023 unless explicitly stated
otherwise.
5 The quantity refers to full-fuel-cycle (FFC)
energy savings. FFC energy savings includes the
energy consumed in extracting, processing, and
transporting primary fuels (i.e., coal, natural gas,
petroleum fuels), and, thus, presents a more
complete picture of the impacts of energy efficiency
standards. For more information on the FFC metric,
see section IV.H.1 of this document.
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The cumulative net present value
(‘‘NPV’’) of total consumer benefits of
the standards for microwave ovens
ranges from $0.16 (at a 7-percent
discount rate) to $0.35 (at a 3-percent
discount rate). This NPV expresses the
estimated total value of future
operating-cost savings minus the
estimated increased product costs for
microwave ovens purchased in 2026–
2055.
In addition, the adopted standards for
microwave ovens are projected to yield
significant environmental benefits. DOE
estimates that the standards will result
in cumulative emission reductions (over
the same period as for energy savings)
of 1.87 million metric tons (‘‘Mt’’) 6 of
carbon dioxide (‘‘CO2’’), 0.85 thousand
tons of sulfur dioxide (‘‘SO2’’), 2.88
thousand tons of nitrogen oxides
(‘‘NOX’’), 12.64 thousand tons of
methane (‘‘CH4’’), 0.02 thousand tons of
nitrous oxide (‘‘N2O’’), and 0.005 tons of
mercury (‘‘Hg’’).7 The estimated
cumulative reduction in CO2 emissions
through 2030 amounts to 0.10 Mt,
which is equivalent to the emissions
resulting from the annual electricity use
of more than 19 thousand homes.
DOE estimates the value of climate
benefits from a reduction in greenhouse
gases (GHG) using four different
estimates of the social cost of CO2 (‘‘SC–
CO2’’), the social cost of methane (‘‘SC–
CH4’’), and the social cost of nitrous
oxide (‘‘SC–N2O’’). Together these
represent the social cost of GHG (SC–
GHG). DOE used interim SC–GHG
values developed by an Interagency
Working Group on the Social Cost of
Greenhouse Gases (IWG).8 The
derivation of these values is discussed
in section IV.L of this document. For
presentational purposes, the climate
benefits associated with the average SC–
GHG at a 3-percent discount rate are
estimated to be $0.10 billion. DOE does
not have a single central SC–GHG point
estimate and DOE emphasizes the
importance and value of considering the
benefits calculated using all four sets of
SC–GHG estimates.9
DOE estimated the monetary health
benefits of SO2 and NOX emissions
reductions, using benefit-per-ton
estimates from the scientific literature,
as discussed in section IV.L of this
document. DOE estimated the present
value of the health benefits would be
$0.07 billion using a 7-percent discount
rate, and $0.17 billion using a 3-percent
discount rate.10 DOE is currently only
monetizing (for SO2 and NOX) PM2.5
precursor health benefits and (for NOX)
ozone precursor health benefits, but will
continue to assess the ability to
monetize other effects, such as health
benefits, from reductions in direct PM2.5
emissions.
Table I.3 summarizes the monetized
benefits and costs expected to result
from the amended standards for
microwave ovens. There are other
important unquantified effects,
including certain unquantified climate
benefits, unquantified public health
benefits from the reduction of toxic air
pollutants and other emissions,
unquantified energy security benefits,
and distributional effects, among others.
TABLE I.3—SUMMARY OF MONETIZED BENEFITS AND COSTS OF ADOPTED ENERGY CONSERVATION STANDARDS FOR
MICROWAVE OVENS
Billion $2021
3% discount rate
Consumer Operating Cost Savings .....................................................................................................................................................
Climate Benefits * .................................................................................................................................................................................
Health Benefits ** .................................................................................................................................................................................
0.43
0.10
0.17
Total Benefits † .............................................................................................................................................................................
Consumer Incremental Product Costs ‡ ..............................................................................................................................................
0.70
0.08
Net Benefits ..................................................................................................................................................................................
0.62
7% discount rate
Consumer Operating Cost Savings .....................................................................................................................................................
Climate Benefits * (3% discount rate) ..................................................................................................................................................
Health Benefits ** .................................................................................................................................................................................
0.21
0.10
0.07
Total Benefits† ..............................................................................................................................................................................
Consumer Incremental Product Costs ‡ ..............................................................................................................................................
0.38
0.05
Net Benefits ..................................................................................................................................................................................
0.34
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Note: This table presents the costs and benefits associated with microwave ovens shipped in 2026¥2055. These results include benefits to
consumers which accrue after 2055 from the products shipped in 2026–2055.
6 A metric ton is equivalent to 1.1 short tons.
Results for emissions other than CO2 are presented
in short tons.
7 DOE calculated emissions reductions relative to
the no-new-standards-case, which reflects key
assumptions in the Annual Energy Outlook 2022
(‘‘AEO2022’’). AEO2022 represents current Federal
and State legislation and final implementation of
regulations as of the time of its preparation. See
section IV.K of this document for further discussion
of AEO2022 assumptions that effect air pollutant
emissions.
8 See Interagency Working Group on Social Cost
of Greenhouse Gases, Technical Support Document:
Social Cost of Carbon, Methane, and Nitrous Oxide.
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Interim Estimates Under Executive Order 13990,
Washington, DC, February 2021 (‘‘February 2021
SC–GHG TSD’’). www.whitehouse.gov/wp-content/
uploads/2021/02/TechnicalSupportDocument_
SocialCostofCarbonMethaneNitrousOxide.pdf.
9 On March 16, 2022, the Fifth Circuit Court of
Appeals (No. 22–30087) granted the Federal
government’s emergency motion for stay pending
appeal of the February 11, 2022, preliminary
injunction issued in Louisiana v. Biden, No. 21–cv–
1074–JDC–KK (W.D. La.). As a result of the Fifth
Circuit’s order, the preliminary injunction is no
longer in effect, pending resolution of the Federal
government’s appeal of that injunction or a further
court order. Among other things, the preliminary
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injunction enjoined the defendants in that case
from ‘‘adopting, employing, treating as binding, or
relying upon’’ the interim estimates of the social
cost of greenhouse gases—which were issued by the
Interagency Working Group on the Social Cost of
Greenhouse Gases on February 26, 2021—to
monetize the benefits of reducing greenhouse gas
emissions. As reflected in this rule, DOE has
reverted to its approach prior to the injunction and
presents monetized benefits where appropriate and
permissible under law.
10 DOE estimates the economic value of these
emissions reductions resulting from the considered
TSLs for the purpose of complying with the
requirements of Executive Order 12866.
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39915
* Climate benefits are calculated using four different estimates of the social cost of carbon (SC–CO2), methane (SC–CH4), and nitrous oxide
(SC–N2O) (model average at 2.5-percent, 3-percent, and 5-percent discount rates; 95th percentile at 3-percent discount rate) (see section IV.L of
this document). Together these represent the global SC–GHG. For presentational purposes of this table, the climate benefits associated with the
average SC–GHG at a 3-percent discount rate are shown, but DOE does not have a single central SC–GHG point estimate. On March 16, 2022,
the Fifth Circuit Court of Appeals (No. 22–30087) granted the Federal government’s emergency motion for stay pending appeal of the February
11, 2022, preliminary injunction issued in Louisiana v. Biden, No. 21–cv–1074–JDC–KK (W.D. La.). As a result of the Fifth Circuit’s order, the
preliminary injunction is no longer in effect, pending resolution of the Federal government’s appeal of that injunction or a further court order.
Among other things, the preliminary injunction enjoined the defendants in that case from ‘‘adopting, employing, treating as binding, or relying
upon’’ the interim estimates of the social cost of greenhouse gases—which were issued by the Interagency Working Group on the Social Cost of
Greenhouse Gases on February 26, 2021—to monetize the benefits of reducing greenhouse gas emissions. As reflected in this rule, DOE has
reverted to its approach prior to the injunction and presents monetized benefits where appropriate and permissible under law.
** Health benefits are calculated using benefit-per-ton values for NOX and SO2. DOE is currently only monetizing (for SO2 and NOX) PM2.5 precursor health benefits and (for NOX) ozone precursor health benefits, but will continue to assess the ability to monetize other effects, such as
health benefits, from reductions in direct PM2.5 emissions. See section IV.L of this document for more details.
† Total and net benefits include those consumer, climate, and health benefits that can be quantified and monetized. For presentation purposes,
total and net benefits for both the 3-percent and 7-percent cases are presented using the average SC–GHG with 3-percent discount rate.
‡ Costs include incremental equipment costs as well as installation costs.
The benefits and costs of the proposed
standards can also be expressed in terms
of annualized values. The monetary
values for the total annualized net
benefits are (1) the reduced consumer
operating costs, minus (2) the increase
in product purchase prices and
installation costs, plus (3) the value of
climate and health benefits of emission
reductions, all annualized.11
The national operating cost savings
are domestic private U.S. consumer
monetary savings that occur as a result
of purchasing the covered products and
are measured for the lifetime of
microwave ovens shipped in 2026–
2055. The benefits associated with
reduced emissions achieved as a result
of the adopted standards are also
calculated based on the lifetime of
microwave ovens shipped in 2026–
2055. Total benefits for both the 3percent and 7-percent cases are
presented using the average GHG social
costs with 3-percent discount rate.
Estimates of SC–GHG values are
presented for all four discount rates in
section V.B.8 of this document.
Table I.4 presents the total estimated
monetized benefits and costs associated
with the standards adopted in this rule,
expressed in terms of annualized values.
The results under the primary estimate
are as follows.
Using a 7-percent discount rate for
consumer benefits and costs and health
benefits from reduced NOX and SO2
emissions, and the 3-percent discount
rate case for climate benefits from
reduced GHG emissions, the estimated
cost of the standards adopted in this
rule is $4.3 million per year in increased
equipment costs, while the estimated
annual benefits are $19.5 million in
reduced equipment operating costs, $5.2
million in climate benefits, and $6.9
million in health benefits. In this case,
the net benefit would amount to $27.3
million per year.
Using a 3-percent discount rate for all
benefits and costs, the estimated cost of
the amended standards is $4.3 million
per year in increased equipment costs,
while the estimated annual benefits are
$23.5 million in reduced operating
costs, $5.2 million in climate benefits,
and $9.2 million in health benefits. In
this case, the net benefit would amount
to $33.5 million per year.
TABLE I.4—ANNUALIZED BENEFITS AND COSTS OF ADOPTED STANDARDS FOR MICROWAVE OVENS
Million 2021 $/year
Primary
estimate
Low-netbenefits
estimate
High-netbenefits
estimate
3% discount rate
Consumer Operating Cost Savings .............................................................................................
Climate Benefits * .........................................................................................................................
Health Benefits ** .........................................................................................................................
23.5
5.2
9.2
22.2
5.1
9.0
25.0
5.4
9.4
Total Benefits † .....................................................................................................................
Consumer Incremental Product Costs ‡ ......................................................................................
37.9
4.3
36.3
4.3
39.8
4.2
Net Benefits ..........................................................................................................................
33.5
31.9
35.6
Consumer Operating Cost Savings .............................................................................................
Climate Benefits * (3% discount rate) ..........................................................................................
Health Benefits ** .........................................................................................................................
19.5
5.2
6.9
18.6
5.1
6.7
20.5
5.4
7.1
Total Benefits † .....................................................................................................................
Consumer Incremental Product Costs ‡ ......................................................................................
31.6
4.3
30.4
4.3
32.9
4.2
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7% discount rate
11 To convert the time-series of costs and benefits
into annualized values, DOE calculated a present
value in 2022, the year used for discounting the
NPV of total consumer costs and savings. For the
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benefits, DOE calculated a present value associated
with each year’s shipments in the year in which the
shipments occur (e.g., 2020 or 2030), and then
discounted the present value from each year to
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2022. Using the present value, DOE then calculated
the fixed annual payment over a 30-year period,
starting in the compliance year, that yields the same
present value.
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TABLE I.4—ANNUALIZED BENEFITS AND COSTS OF ADOPTED STANDARDS FOR MICROWAVE OVENS—Continued
Million 2021 $/year
Primary
estimate
Net Benefits ..........................................................................................................................
27.3
Low-netbenefits
estimate
26.1
High-netbenefits
estimate
28.7
Note: This table presents the costs and benefits associated with microwave ovens shipped in 2026–2055. These results include benefits to
consumers which accrue after 2055 from the products shipped in 2026–2055. The Primary, Low Net Benefits, and High Net Benefits Estimates
utilize projections of energy prices from the AEO2022 Reference case, Low Economic Growth case, and High Economic Growth case, respectively. In addition, incremental equipment costs reflect a medium decline rate in the Primary Estimate, a low decline rate in the Low Net Benefits
Estimate, and a high decline rate in the High Net Benefits Estimate. The methods used to derive projected price trends are explained in sections
IV.F.1 and IV.H.1 of this document. Note that the Benefits and Costs may not sum to the Net Benefits due to rounding.
* Climate benefits are calculated using four different estimates of the global SC–GHG (see section IV.L of this document). For presentational
purposes of this table, the climate benefits associated with the average SC–GHG at a 3-percent discount rate are shown, but DOE does not
have a single central SC–GHG point estimate, and it emphasizes the importance and value of considering the benefits calculated using all four
sets of SC–GHG estimates. On March 16, 2022, the Fifth Circuit Court of Appeals (No. 22–30087) granted the Federal government’s emergency
motion for stay pending appeal of the February 11, 2022, preliminary injunction issued in Louisiana v. Biden, No. 21–cv–1074–JDC–KK (W.D.
La.). As a result of the Fifth Circuit’s order, the preliminary injunction is no longer in effect, pending resolution of the Federal government’s appeal of that injunction or a further court order. Among other things, the preliminary injunction enjoined the defendants in that case from ‘‘adopting,
employing, treating as binding, or relying upon’’ the interim estimates of the social cost of greenhouse gases—which were issued by the Interagency Working Group on the Social Cost of Greenhouse Gases on February 26, 2021—to monetize the benefits of reducing greenhouse gas
emissions. As reflected in this rule, DOE has reverted to its approach prior to the injunction and presents monetized benefits where appropriate
and permissible under law.
** Health benefits are calculated using benefit-per-ton values for NOX and SO2. DOE is currently only monetizing (for SO2 and NOX) PM2.5 precursor health benefits and (for NOX) ozone precursor health benefits, but will continue to assess the ability to monetize other effects such as
health benefits from reductions in direct PM2.5 emissions. See section IV.L of this document for more details.
† Total benefits for both the 3-percent and 7-percent cases are presented using the average SC–GHG with 3-percent discount rate.
‡ Costs include incremental equipment costs as well as installation costs.
DOE’s analysis of the national impacts
of the adopted standards is described in
sections IV.H, IV.K, and IV.L of this
document.
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D. Conclusion
DOE concludes that the standards
adopted in this final rule represent the
maximum improvement in energy
efficiency that is technologically
feasible and economically justified, and
would result in the significant
conservation of energy. Specifically,
with regards to technological feasibility,
products achieving these standard levels
are already commercially available for
all product classes covered by this
proposal. As for economic justification,
DOE’s analysis shows that the benefits
of the standards exceed, to a great
extent, the burdens of the standards.
Using a 7-percent discount rate for
consumer benefits and costs and NOX
and SO2 reduction benefits, and a 3percent discount rate case for GHG
social costs, the estimated cost of the
standards for microwave ovens is $4.3
million per year in increased product
costs, while the estimated annual
benefits are $19.5 million in reduced
product operating costs, $5.2 million in
climate benefits, and $6.9 million in
health benefits. The net benefit amounts
to $27.3 million per year.
The significance of energy savings
offered by a new or amended energy
conservation standard cannot be
determined without knowledge of the
specific circumstances surrounding a
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given rulemaking.12 For example, some
covered products and equipment have
most of their energy consumption occur
during periods of peak energy demand.
The impacts of these products on the
energy infrastructure can be more
pronounced than products with
relatively constant demand.
Accordingly, DOE evaluates the
significance of energy savings on a caseby-case basis.
As previously mentioned, the
standards are projected to result in
estimated national energy savings of
0.06 quads in FFC energy use and
emissions, the equivalent of the primary
annual energy use of 1.6 million homes.
In addition, the standards are projected
to reduce CO2 emissions by 1.87 Mt.
Based on these findings, DOE has
determined the energy savings from the
standard levels adopted in this final rule
are ‘‘significant’’ within the meaning of
42 U.S.C. 6295(o)(3)(B). A more detailed
discussion of the basis for these
conclusions is contained in the
remainder of this document and the
accompanying final rule technical
support document (‘‘TSD’’).
II. Introduction
The following section briefly
discusses the statutory authority
underlying this final rule, as well as
some of the relevant historical
12 Procedures, Interpretations, and Policies for
Consideration in New or Revised Energy
Conservation Standards and Test Procedures for
Consumer Products and Commercial/Industrial
Equipment, 86 FR 70892, 70901 (Dec. 13, 2021).
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background related to the establishment
of standards for microwave ovens.
A. Authority
EPCA authorizes DOE to regulate the
energy efficiency of a number of
consumer products and certain
industrial equipment. Title III, Part B of
EPCA established the Energy
Conservation Program for Consumer
Products Other Than Automobiles.
These products include microwave
ovens, the subject of this document. (42
U.S.C. 6292(a)(10)) EPCA prescribed
energy conservation standards for these
products, and directs DOE to conduct
future rulemakings to determine
whether to amend these standards. (42
U.S.C. 6295(h)(2)(A)–(B)) EPCA further
provides that, not later than 6 years after
the issuance of any final rule
establishing or amending a standard,
DOE must publish either a notice of
determination that standards for the
product do not need to be amended, or
a NOPR including new proposed energy
conservation standards (proceeding to a
final rule, as appropriate). (42 U.S.C.
6295(m)(1))
The energy conservation program
under EPCA consists essentially of four
parts: (1) testing, (2) labeling, (3) the
establishment of Federal energy
conservation standards, and (4)
certification and enforcement
procedures. Relevant provisions of
EPCA specifically include definitions
(42 U.S.C. 6291), test procedures (42
U.S.C. 6293), labeling provisions (42
U.S.C. 6294), energy conservation
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
standards (42 U.S.C. 6295), and the
authority to require information and
reports from manufacturers (42 U.S.C.
6296).
Federal energy efficiency
requirements for covered products
established under EPCA generally
supersede State laws and regulations
concerning energy conservation testing,
labeling, and standards. (42 U.S.C.
6297(a)–(c)) DOE may, however, grant
waivers of Federal preemption in
limited instances for particular State
laws or regulations, in accordance with
the procedures and other provisions set
forth under EPCA. (See 42 U.S.C.
6297(d))
Subject to certain criteria and
conditions, DOE is required to develop
test procedures to measure the energy
efficiency, energy use, or estimated
annual operating cost of each covered
product. (42 U.S.C. 6295(o)(3)(A) and 42
U.S.C. 6295(r)) Manufacturers of
covered products must use the
prescribed DOE test procedure as the
basis for certifying to DOE that their
products comply with the applicable
energy conservation standards adopted
under EPCA and when making
representations to the public regarding
the energy use or efficiency of those
products. (42 U.S.C. 6293(c) and
6295(s)) Similarly, DOE must use these
test procedures to determine whether
the products comply with standards
adopted pursuant to EPCA. (42 U.S.C.
6295(s)) The DOE test procedures for
microwave ovens appear at title 10 of
the Code of Federal Regulations (‘‘CFR’’)
§ 430.23(i) and 10 CFR part 430, subpart
B, appendix I (‘‘appendix I’’).
DOE must follow specific statutory
criteria for prescribing new or amended
standards for covered products,
including microwave ovens. Any new or
amended standard for a covered product
must be designed to achieve the
maximum improvement in energy
efficiency that the Secretary of Energy
determines is technologically feasible
and economically justified. (42 U.S.C.
6295(o)(2)(A) and 42 U.S.C.
6295(o)(3)(B)) Furthermore, DOE may
not adopt any standard that would not
result in the significant conservation of
energy. (42 U.S.C. 6295(o)(3)) Moreover,
DOE may not prescribe a standard (1)
for certain products, including
microwave ovens, if no test procedure
has been established for the product, or
(2) if DOE determines by rule that the
standard is not technologically feasible
or economically justified. (42 U.S.C.
6295(o)(3)(A)–(B)) In deciding whether a
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proposed standard is economically
justified, DOE must determine whether
the benefits of the standard exceed its
burdens. (42 U.S.C. 6295(o)(2)(B)(i))
DOE must make this determination after
receiving comments on the proposed
standard, and by considering, to the
greatest extent practicable, the following
seven statutory factors:
(1) The economic impact of the
standard on manufacturers and
consumers of the products subject to the
standard;
(2) The savings in operating costs
throughout the estimated average life of
the covered products in the type (or
class) compared to any increase in the
price, initial charges, or maintenance
expenses for the covered products that
are likely to result from the standard;
(3) The total projected amount of
energy (or as applicable, water) savings
likely to result directly from the
standard;
(4) Any lessening of the utility or the
performance of the covered products
likely to result from the standard;
(5) The impact of any lessening of
competition, as determined in writing
by the Attorney General, that is likely to
result from the standard;
(6) The need for national energy and
water conservation; and
(7) Other factors the Secretary of
Energy (‘‘Secretary’’) considers relevant.
(42 U.S.C. 6295(o)(2)(B)(i)(I)–(VII))
Further, EPCA, as codified,
establishes a rebuttable presumption
that a standard is economically justified
if the Secretary finds that the additional
cost to the consumer of purchasing a
product complying with an energy
conservation standard level will be less
than three times the value of the energy
savings during the first year that the
consumer will receive as a result of the
standard, as calculated under the
applicable test procedure. (42 U.S.C.
6295(o)(2)(B)(iii))
EPCA, as codified, also contains what
is known as an ‘‘anti-backsliding’’
provision, which prevents the Secretary
from prescribing any amended standard
that either increases the maximum
allowable energy use or decreases the
minimum required energy efficiency of
a covered product. (42 U.S.C.
6295(o)(1)) Also, the Secretary may not
prescribe an amended or new standard
if interested persons have established by
a preponderance of the evidence that
the standard is likely to result in the
unavailability in the United States in
any covered product type (or class) of
performance characteristics (including
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39917
reliability), features, sizes, capacities,
and volumes that are substantially the
same as those generally available in the
United States. (42 U.S.C. 6295(o)(4))
Additionally, EPCA specifies
requirements when promulgating an
energy conservation standard for a
covered product that has two or more
subcategories. DOE must specify a
different standard level for a type or
class of products that has the same
function or intended use if DOE
determines that products within such
group (A) consume a different kind of
energy from that consumed by other
covered products within such type (or
class); or (B) have a capacity or other
performance-related feature which other
products within such type (or class) do
not have and such feature justifies a
higher or lower standard. (42 U.S.C.
6295(q)(1)) In determining whether a
performance-related feature justifies a
different standard for a group of
products, DOE must consider such
factors as the utility to the consumer of
such a feature and other factors DOE
deems appropriate. Id. Any rule
prescribing such a standard must
include an explanation of the basis on
which such higher or lower level was
established. (42 U.S.C. 6295(q)(2))
Finally, pursuant to the amendments
contained in the Energy Independence
and Security Act of 2007 (EISA 2007),
Public Law 110–140, any final rule for
new or amended energy conservation
standards promulgated after July 1,
2010, is required to address standby
mode and off mode energy use. (42
U.S.C. 6295(gg)(3)) Specifically, when
DOE adopts a standard for a covered
product after that date, it must, if
justified by the criteria for adoption of
standards under EPCA (42 U.S.C.
6295(o)), incorporate standby mode and
off mode energy use into a single
standard, or, if that is not feasible, adopt
a separate standard for such energy use
for that product. (42 U.S.C.
6295(gg)(3)(A)–(B))
B. Background
1. Current Standards
In a final rule published on June 17,
2013 (‘‘June 2013 Final Rule’’), DOE
prescribed the current energy
conservation standards for microwave
ovens manufactured on and after June
17, 2016. 78 FR 36316. These standards
are set forth in DOE’s regulations at 10
CFR 430.32(j)(3) and are repeated in
Table II.1.
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TABLE II.1—FEDERAL ENERGY CON- various issues on which DOE sought
SERVATION STANDARDS FOR MICRO- comment to inform its determination of
whether the standards need to be
WAVE OVENS
Product class
Microwave-Only Ovens and
Countertop Convection
Microwave Ovens.
Built-In and Over-the-Range
Convection Microwave
Ovens.
Maximum
allowable
average
standby power
1.0 W.
2.2 W.
2. History of Standards Rulemaking for
Microwave Ovens
EPCA prescribed an energy
conservation standard for kitchen ranges
and ovens, and directed DOE to conduct
two cycles of rulemakings to determine
whether to amend standards for these
products. (42 U.S.C. 6295(h)(2)(A)–(B))
DOE completed the first of these
rulemaking cycles by publishing a final
rule on September 8, 1998, that codified
the prescriptive design standard for gas
cooking products established in EPCA,
but found that no standards were
justified for electric cooking products,
including microwave ovens, at that
time. 63 FR 48038, 48053–48054. DOE
completed the second rulemaking cycle
and published a final rule on April 8,
2009, in which it determined, among
other things, that standards for
microwave oven active mode energy use
were not economically justified. 74 FR
16040.
DOE published the June 2013 Final
Rule, adopting energy conservation
standards for microwave ovens. 78 FR
36316. In the June 2013 Final Rule, DOE
maintained its prior determination that
active mode standards are not warranted
for microwave ovens and prescribed
energy conservation standards that
address the standby and off mode
energy use of microwave ovens. 78 FR
36316, 36317.
In support of the present review of the
microwave oven energy conservation
standards, DOE published an early
assessment request for information on
August 13, 2019, which identified
amended. 84 FR 39980.
DOE subsequently published a notice
of proposed determination (‘‘NOPD’’) on
August 12, 2021, in which DOE initially
determined that current standards for
microwave ovens do not need to be
amended. 86 FR 44298. (‘‘August 2021
NOPD’’) In the August 2021 NOPD, DOE
tentatively determined that there are
technology options that would improve
the efficiency of microwave ovens. 86
FR 44298, 44310. Based on the analysis
conducted for the August 2021 NOPD,
DOE estimated that amended standards
for microwave oven standby power at
the maximum technologically feasible
(‘‘max-tech’’) level would result in 0.1
quads of energy saved over a 30-year
period (representing an estimated 8
percent reduction in site energy use of
microwave ovens). 86 FR 44298, 44310.
In evaluating the significance of the
estimated energy savings for the August
2021 NOPD, DOE applied a two-part
numeric threshold test that was then
applicable under section 6(b) of
appendix A to 10 CFR part 430 subpart
C (Jan. 1, 2021 edition). Specifically, the
threshold required that an energy
conservation standard result in a 0.30
quads reduction in site energy use over
a 30-year analysis period or a 10-percent
reduction in site energy use over that
same period. See 85 FR 8626, 8670 (Feb.
14, 2020). In the August 2021 NOPD,
DOE stated that the estimated site
energy savings at the max-tech level was
under the 0.3-quads/10-percent
threshold and tentatively determined
that amended energy conservation
standards for microwave oven standby
power would not result in significant
conservation of energy. 86 FR 44298,
44310. DOE also noted that the two-part
numeric threshold was under
reconsideration. 86 FR 44298, 44302.
On December 13, 2021, DOE
published in the Federal Register a final
rule that amended appendix A to 10
CFR part 430 subpart C (‘‘appendix A’’).
86 FR 70892 (‘‘December 2021 Final
Rule’’). The December 20201 Final Rule,
in part, removed the numeric threshold
in section 6(b) of appendix A for
determining when the significant energy
savings criterion is met, reverting to
DOE’s prior practice of making such
determinations on a case-by-case basis.
86 FR 70892.
After the publication of the NOPD,
DOE conducted investigative testing and
manufacturer discussions, and updated
the engineering analysis to be used in a
subsequently published supplemental
notice of proposed rulemaking
(‘‘SNOPR’’) on August 24, 2022. 87 FR
52282. (‘‘August 2022 SNOPR’’) In the
August 2022 SNOPR, DOE revised the
efficiency levels, manufacturer selling
price (‘‘MSP’’)-efficiency relationships,
and LCC and PBP analyses to evaluate
the economic impacts of potential
energy conservation standards for
microwave ovens on individual
consumers. The amended energy
conservation standards for microwave
ovens proposed in the August 2022
SNOPR are shown in Table II.2. DOE
requested comment on these proposed
standards and associated analyses and
results.
TABLE II.2—AUGUST 2022 SNOPR
PROPOSED ENERGY CONSERVATION
STANDARDS
FOR
MICROWAVE
OVENS
Maximum
allowable
average
standby power
(watts)
Product class
PC 1: Microwave-Only
Ovens and Countertop
Convection Microwave
Ovens.
PC 2: Built-In and Over-theRange Convection Microwave Ovens.
0.6 W.
1.0 W.
DOE held a public meeting on
October 11, 2022, to solicit feedback
from stakeholders concerning the
August 2022 SNOPR, and received 5
comments in response to the August
2022 SNOPR from the interested parties
listed in Table II.3.
TABLE II.3—AUGUST 2022 SNOPR WRITTEN COMMENTS
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Commenter(s)
Abbreviation
Appliance Standards Awareness Project, American Council for an Energy-Efficient
Economy, Consumer Federation of America, National Consumer Law Center,
Natural Resources Defense Council, Northwest Energy Efficiency Alliance.
Association of Home Appliance Manufacturers ........................................................
Center for Climate and Energy Solutions, Institute for Policy Integrity at New York
University School of Law, Natural Resources Defense Council, Sierra Club,
Union of Concerned Scientists, Institute for Policy Integrity.
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Comment
number in
the docket
Commenter type
The Joint Commenters.
31
Efficiency Organizations.
AHAM .....................
C2ES ......................
28
29
Trade Association.
Efficiency Organizations.
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39919
TABLE II.3—AUGUST 2022 SNOPR WRITTEN COMMENTS—Continued
Commenter(s)
Abbreviation
Whirlpool Corporation ................................................................................................
Whirlpool .................
A parenthetical reference at the end of
a comment quotation or paraphrase
provides the location of the item in the
public record.13 To the extent that
interested parties have provided written
comments that are substantively
consistent with any oral comments
provided during the October 11, 2022
webinar, DOE cites the written
comments throughout this final rule.
Any oral comments provided during the
webinar that are not substantively
addressed by written comments are
summarized and cited separately
throughout this final rule.
III. General Discussion
DOE developed this final rule after
considering oral and written comments,
data, and information from interested
parties that represent a variety of
interests. The following discussion
addresses issues raised by these
commenters.
A. Scope of Coverage
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This final rule covers those consumer
products that meet the definition of
‘‘microwave oven’’ as codified at 10 CFR
430.2, which defines ‘‘microwave oven’’
as a category of cooking products which
is a household cooking appliance
consisting of a compartment designed to
cook or heat food by means of
microwave energy, including
microwave ovens with or without
thermal elements designed for surface
browning of food and convection
microwave ovens. This includes any
microwave oven(s) component of a
combined cooking product. Any
product meeting the definition of
microwave oven is included in DOE’s
scope of coverage.
For this final rule, DOE considered
the two product classes of microwave
ovens prescribed in the current energy
conservation standards: (1) MicrowaveOnly Ovens and Countertop Convection
Microwave Ovens, and (2) Built-In and
Over-the-Range Convection Microwave
Ovens.
13 The parenthetical reference provides a
reference for information located in the docket of
DOE’s rulemaking to develop energy conservation
standards for microwave ovens. (Docket No. EERE–
2017–BT–STD–0023, which is maintained at
www.regulations.gov). The references are arranged
as follows: (commenter name, comment docket ID
number, page of that document).
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For these two classes of microwave
ovens, DOE’s current test procedure
measures the energy consumption in
standby mode and off mode only.
Consequently, DOE’s current energy
conservation standards for microwave
ovens are also expressed in terms of
standby mode and off mode power.
There are currently no active mode
energy conservation standards; nor is
there a prescribed test procedure for
measuring the active mode energy use
or efficiency (e.g., cooking efficiency) of
microwave ovens.
The Joint Commenters commented
that adopting a standard for active mode
energy consumption could achieve
‘‘significantly greater’’ savings than
proposed standby power standards, and
that DOE should develop a test
procedure and standards for active
mode power consumption. (Joint
Commenters, No. 31 at p. 2) DOE
previously rejected developing an active
mode test procedure in the microwave
oven test procedure final rule published
on March 30, 2022, (‘‘March 2022 TP
Final Rule’’) due to undue burden on
manufacturers and the lack of an
available test procedure that accounts
for the efficiency improvements of
inverter microwave ovens. 87 FR 18261.
As there is no test procedure for
measuring the active mode efficiency of
a microwave oven, and since
development of such a test procedure is
out of the scope of this document, DOE
is not currently proposing to adopt an
active mode energy usage standard.
See section IV.2 of this document for
discussion of the product classes
analyzed in this final rule.
B. Test Procedure
EPCA sets forth generally applicable
criteria and procedures for DOE’s
adoption and amendment of test
procedures. (42 U.S.C. 6293)
Manufacturers of covered products must
use these test procedures to certify to
DOE that their product complies with
energy conservation standards and to
quantify the efficiency of their product.
DOE will finalize a test procedure
establishing methodologies used to
evaluate proposed energy conservation
standards prior to publication of a
NOPR proposing new or amended
energy conservation standards. Section
8(d)(1) of appendix A. As discussed,
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Comment
number in
the docket
30
Commenter type
Manufacturer.
DOE amended the test procedure for
microwave ovens, set forth in appendix
I, in the March 2022 TP Final Rule.
DOE’s current energy conservation
standards for microwave ovens are
expressed in terms of watts of standby
power. (See 10 CFR 430.23(j)(3).)
C. Technological Feasibility
1. General
In each energy conservation standards
rulemaking, DOE conducts a screening
analysis based on information gathered
on all current technology options and
prototype designs that could improve
the efficiency of the products or
equipment that are the subject of the
rulemaking. As the first step in such an
analysis, DOE develops a list of
technology options for consideration in
consultation with manufacturers, design
engineers, and other interested parties.
DOE then determines which of those
means for improving efficiency are
technologically feasible. DOE considers
technologies incorporated in
commercially available products or in
working prototypes to be
technologically feasible. Sections
6(b)(3)(i) and 7(b)(1) of appendix A.
After DOE has determined that
particular technology options are
technologically feasible, it further
evaluates each technology option in
light of the following additional
screening criteria: (1) practicability to
manufacture, install, and service; (2)
adverse impacts on product utility or
availability; (3) adverse impacts on
health or safety and (4) unique-pathway
proprietary technologies. Sections
6(b)(3)(ii) through (v) and sections
7(b)(2) through (5) of appendix A.
Section IV.B of this document discusses
the results of the screening analysis for
microwave ovens, particularly the
designs DOE considered, those it
screened out, and those that are the
basis for the standards considered in
this rulemaking. For further details on
the screening analysis for this
rulemaking, see chapter 4 of the final
rule TSD.
2. Maximum Technologically Feasible
Levels
When DOE proposes to adopt an
amended standard for a type or class of
covered product, it must determine the
maximum improvement in energy
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efficiency or maximum reduction in
energy use that is technologically
feasible for such product. (42 U.S.C.
6295(p)(1)) Accordingly, in the
engineering analysis, DOE determined
the maximum technologically feasible
(‘‘max-tech’’) improvements in energy
efficiency for microwave ovens, using
the design parameters for the most
efficient products available on the
market or in working prototypes. The
max-tech levels that DOE determined
for this rulemaking are described in
section IV.C of this document and in
chapter 5 of the final rule TSD.
D. Energy Savings
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1. Determination of Savings
For each trial standard level (‘‘TSL’’),
DOE projected energy savings from
application of the TSL to microwave
ovens purchased in the 30-year period
that begins in the year of compliance
with the amended standards (2026–
2055).14 The savings are measured over
the entire lifetime of products
purchased in the 30-year analysis
period. DOE quantified the energy
savings attributable to each TSL as the
difference in energy consumption
between each standards case and the nonew-standards case. The no-newstandards case represents a projection of
energy consumption that reflects how
the market for a product would likely
evolve in the absence of amended
energy conservation standards.
DOE used its national impact analysis
(‘‘NIA’’) spreadsheet models to estimate
national energy savings (‘‘NES’’) from
potential amended standards for
microwave ovens. The NIA spreadsheet
model (described in section IV.H of this
document) calculates energy savings in
terms of site energy, which is the energy
directly consumed by products at the
locations where they are used. For
electricity, DOE reports national energy
savings in terms of primary energy
savings, which is the savings in the
energy that is used to generate and
transmit the site electricity. For natural
gas, the primary energy savings are
considered to be equal to the site energy
savings. DOE also calculates NES in
terms of FFC energy savings. The FFC
metric includes the energy consumed in
extracting, processing, and transporting
primary fuels (i.e., coal, natural gas,
petroleum fuels), and thus presents a
more complete picture of the impacts of
14 Each TSL is composed of specific efficiency
levels for each product class. The TSLs considered
for this rule are described in section V.A of this
document. DOE also presents a sensitivity analysis
that considers impacts for products shipped in a 9year period.
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energy conservation standards.15 DOE’s
approach is based on the calculation of
an FFC multiplier for each of the energy
types used by covered products or
equipment. For more information on
FFC energy savings, see section IV.H.2
of this document.
2. Significance of Savings
To adopt any new or amended
standards for a covered product, DOE
must determine that such action would
result in significant energy savings. (42
U.S.C. 6295(o)(3)(B))
The significance of energy savings
offered by a new or amended energy
conservation standard cannot be
determined without knowledge of the
specific circumstances surrounding a
given rulemaking. For example, some
covered products and equipment have
most of their energy consumption occur
during periods of peak energy demand.
The impacts of these products on the
energy infrastructure can be more
pronounced than products with
relatively constant demand. In
evaluating the significance of energy
savings, DOE considers differences in
primary energy and FFC effects for
different covered products and
equipment when determining whether
energy savings are significant. Primary
energy and FFC effects include the
energy consumed in electricity
production (depending on load shape),
in distribution and transmission, and in
extracting, processing, and transporting
primary fuels (i.e., coal, natural gas,
petroleum fuels), and thus present a
more complete picture of the impacts of
energy conservation standards.
Accordingly, DOE evaluates the
significance of energy savings on a caseby-case basis. As stated, the standard
levels adopted in this final rule are
projected to result in national FFC
energy savings of 0.06 quads, the
equivalent of the electricity use of 1.6
million homes in one year. DOE has
determined the energy savings from the
standard levels adopted in this final rule
are ‘‘significant’’ within the meaning of
42 U.S.C. 6295(o)(3)(B).
E. Economic Justification
1. Specific Criteria
As noted previously, EPCA provides
seven factors to be evaluated in
determining whether a potential energy
conservation standard is economically
justified. (42 U.S.C. 6295(o)(2)(B)(i)(I)–
(VII)) The following sections discuss
15 The FFC metric is discussed in DOE’s
statement of policy and notice of policy
amendment. 76 FR 51282 (Aug. 18, 2011), as
amended at 77 FR 49701 (Aug. 17, 2012).
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how DOE has addressed each of those
seven factors in this rulemaking.
a. Economic Impact on Manufacturers
and Consumers
In determining the impacts of
potential amended standards on
manufacturers, DOE conducts a
Manufacturer Impact Analysis (‘‘MIA’’),
as discussed in section IV.J of this
document. DOE uses an annual cashflow approach to determine the
quantitative impacts. This step includes
both a short-term assessment—based on
the cost and capital requirements during
the period between when a regulation is
issued and when entities must comply
with the regulation—and a long-term
assessment over a 30-year period. The
industry-wide impacts analyzed include
(1) INPV, which values the industry on
the basis of expected future cash flows;
(2) cash flows by year; (3) changes in
revenue and income; and (4) other
measures of impact, as appropriate.
Second, DOE analyzes and reports the
impacts on different types of
manufacturers, including impacts on
small manufacturers. Third, DOE
considers the impact of standards on
domestic manufacturer employment and
manufacturing capacity, as well as the
potential for standards to result in plant
closures and loss of capital investment.
Finally, DOE takes into account
cumulative impacts of various DOE
regulations and other regulatory
requirements on manufacturers.
For individual consumers, measures
of economic impact include the changes
in LCC and payback period (‘‘PBP’’)
associated with new or amended
standards. These measures are
discussed further in the following
section. For consumers in the aggregate,
DOE also calculates the national net
present value of the consumer costs and
benefits expected to result from
particular standards. DOE also evaluates
the impacts of potential standards on
identifiable subgroups of consumers
that may be affected disproportionately
by a standard.
b. Savings in Operating Costs Compared
To Increase in Price (LCC and PBP)
EPCA requires DOE to consider the
savings in operating costs throughout
the estimated average life of the covered
product in the type (or class) compared
to any increase in the price of, or in the
initial charges for, or maintenance
expenses of, the covered product that
are likely to result from a standard. (42
U.S.C. 6295(o)(2)(B)(i)(II)) DOE conducts
this comparison in its LCC and PBP
analysis.
The LCC is the sum of the purchase
price of a product (including its
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installation) and the operating cost
(including energy, maintenance, and
repair expenditures) discounted over
the lifetime of the product. The LCC
analysis requires a variety of inputs,
such as product prices, product energy
consumption, energy prices,
maintenance and repair costs, product
lifetime, and discount rates appropriate
for consumers. To account for
uncertainty and variability in specific
inputs, such as product lifetime and
discount rate, DOE uses a distribution of
values, with probabilities attached to
each value.
The PBP is the estimated amount of
time (in years) it takes consumers to
recover the increased purchase cost
(including installation) of a moreefficient product through lower
operating costs. DOE calculates the PBP
by dividing the change in purchase cost
due to a more-stringent standard by the
change in annual operating cost for the
year that standards are assumed to take
effect.
For its LCC and PBP analysis, DOE
assumes that consumers will purchase
the covered products in the first year of
compliance with new or amended
standards. The LCC savings for the
considered efficiency levels are
calculated relative to the case that
reflects projected market trends in the
absence of new or amended standards.
DOE’s LCC and PBP analysis is
discussed in further detail in section
IV.F of this document.
c. Energy Savings
Although significant conservation of
energy is a separate statutory
requirement for adopting an energy
conservation standard, EPCA requires
DOE, in determining the economic
justification of a standard, to consider
the total projected energy savings that
are expected to result directly from the
standard. (42 U.S.C. 6295(o)(2)(B)(i)(III))
As discussed in section IV.E of this
document, DOE uses the NIA
spreadsheet models to project national
energy savings.
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d. Lessening of Utility or Performance of
Products
In establishing product classes, and in
evaluating design options and the
impact of potential standard levels, DOE
evaluates potential standards that would
not lessen the utility or performance of
the considered products. (42 U.S.C.
6295(o)(2)(B)(i)(IV)) Based on data
available to DOE, the standards adopted
in this document would not reduce the
utility or performance of the products
under consideration in this rulemaking.
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e. Impact of Any Lessening of
Competition
EPCA directs DOE to consider the
impact of any lessening of competition,
as determined in writing by the
Attorney General, that is likely to result
from a standard. (42 U.S.C.
6295(o)(2)(B)(i)(V)) It also directs the
Attorney General to determine the
impact, if any, of any lessening of
competition likely to result from a
proposed standard and to transmit such
determination to the Secretary within 60
days of the publication of a proposed
rule, together with an analysis of the
nature and extent of the impact. (42
U.S.C. 6295(o)(2)(B)(ii)) To assist the
Department of Justice (‘‘DOJ’’) in making
such a determination, DOE transmitted
copies of the August 2022 SNOPR and
the SNOPR TSD to the Attorney General
for review, with a request that the DOJ
provide its determination on this issue.
In its assessment letter responding to
DOE, DOJ concluded that the proposed
energy conservation standards for
microwave ovens are unlikely to have a
significant adverse impact on
competition. DOE is publishing the
Attorney General’s assessment at the
end of this final rule.
f. Need for National Energy
Conservation
DOE also considers the need for
national energy and water conservation
in determining whether a new or
amended standard is economically
justified. (42 U.S.C. 6295(o)(2)(B)(i)(VI))
The energy savings from the adopted
standards are likely to provide
improvements to the security and
reliability of the Nation’s energy system.
Reductions in the demand for electricity
also may result in reduced costs for
maintaining the reliability of the
Nation’s electricity system. DOE
conducts a utility impact analysis to
estimate how standards may affect the
Nation’s needed power generation
capacity, as discussed in section IV.M of
this document.
DOE maintains that environmental
and public health benefits associated
with the more efficient use of energy are
important to take into account when
considering the need for national energy
conservation. The adopted standards are
likely to result in environmental
benefits in the form of reduced
emissions of air pollutants and
greenhouse gases (‘‘GHGs’’) associated
with energy production and use. DOE
conducts an emissions analysis to
estimate how potential standards may
affect these emissions, as discussed in
section IV.K of this document; the
estimated emissions impacts are
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39921
reported in section V.B.6 of this
document. DOE also estimates the
economic value of emissions reductions
resulting from the considered TSLs, as
discussed in section IV.L of this
document.
g. Other Factors
In determining whether an energy
conservation standard is economically
justified, DOE may consider any other
factors that the Secretary deems to be
relevant. (42 U.S.C. 6295(o)(2)(B)(i)(VII))
To the extent DOE identifies any
relevant information regarding
economic justification that does not fit
into the other categories described
previously, DOE could consider such
information under ‘‘other factors.’’
2. Rebuttable Presumption
As set forth in 42 U.S.C.
6295(o)(2)(B)(iii), EPCA creates a
rebuttable presumption that an energy
conservation standard is economically
justified if the additional cost to the
consumer of a product that meets the
standard is less than three times the
value of the first year’s energy savings
resulting from the standard, as
calculated under the applicable DOE
test procedure. DOE’s LCC and PBP
analyses generate values used to
calculate the effects that proposed
energy conservation standards would
have on the payback period for
consumers. These analyses include, but
are not limited to, the 3-year payback
period contemplated under the
rebuttable-presumption test. In addition,
DOE routinely conducts an economic
analysis that considers the full range of
impacts to consumers, manufacturers,
the Nation, and the environment, as
required under 42 U.S.C.
6295(o)(2)(B)(i). The results of this
analysis serve as the basis for DOE’s
evaluation of the economic justification
for a potential standard level (thereby
supporting or rebutting the results of
any preliminary determination of
economic justification). The rebuttable
presumption payback calculation is
discussed in section IV.F of this
document.
IV. Methodology and Discussion of
Related Comments
This section addresses the analyses
DOE has performed for this rulemaking
with regard to microwave ovens.
Separate subsections address each
component of DOE’s analyses.
DOE used several analytical tools to
estimate the impact of the standards
considered in this document. The first
tool is a spreadsheet that calculates the
LCC savings and PBP of potential
amended or new energy conservation
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standards. The national impacts
analysis uses a second spreadsheet set
that provides shipments projections and
calculates national energy savings and
net present value of total consumer
costs and savings expected to result
from potential energy conservation
standards. DOE uses the third
spreadsheet tool, the Government
Regulatory Impact Model (‘‘GRIM’’), to
assess manufacturer impacts of potential
standards. These three spreadsheet tools
are available on the DOE website for this
rulemaking: www1.eere.energy.gov/
buildings/appliance_standards/
product.aspx/productid/48.
Additionally, DOE used output from the
latest version of the Energy Information
Administration’s (‘‘EIA’s’’) Annual
Energy Outlook (‘‘AEO’’) for the
emissions and utility impact analyses.
1. Market and Technology Assessment
DOE develops information in the
market and technology assessment that
provides an overall picture of the
market for the products concerned,
including the purpose of the products,
the industry structure, manufacturers,
market characteristics, and technologies
used in the products. This activity
includes both quantitative and
qualitative assessments, based primarily
on publicly-available information. The
subjects addressed in the market and
technology assessment for this
rulemaking include (1) a determination
of the scope of the rulemaking and
product classes, (2) manufacturers and
industry structure, (3) existing
efficiency programs, (4) shipments
information, (5) market and industry
trends, and (6) technologies or design
options that could improve the energy
efficiency of microwave ovens. The key
findings of DOE’s market assessment are
summarized in the following sections.
See chapter 3 of the final rule TSD for
further discussion of the market and
technology assessment.
AHAM commented that it disagrees
with DOE addressing European
efficiency programs as a part of its
analysis for the August 2022 SNOPR.
AHAM stated that DOE is improperly
making direct comparisons to the
European market and should not look to
Europe or any other jurisdiction for
guidance without first understanding
the differences between products in
those markets and those in the United
States. (AHAM, No. 28 at p. 10) In
response to AHAM’s comment, DOE
notes that its analysis of foreign
regulatory programs is only to reduce
additional manufacturer burden in
complying with conflicting standards.
DOE did not find any conflicting foreign
regulatory programs, nor did it develop
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trial standards levels based on any
foreign regulations. In the case of this
rulemaking, foreign regulations had no
bearing on DOE’s analysis.
2. Product Classes
When evaluating and establishing
energy conservation standards, DOE
may establish separate standards for a
group of covered products (i.e., establish
a separate product class) if DOE
determines that separate standards are
justified based on the type of energy
used, or if DOE determines that a
product’s capacity or other
performance-related feature justifies a
different standard. (42 U.S.C. 6295(q)) In
making a determination whether a
performance-related feature justifies a
different standard, DOE must consider
such factors as the utility of the feature
to the consumer and other factors DOE
determines are appropriate. (Id.)
Any product meeting the definition of
a microwave oven, as codified in 10
CFR 430.2, is included in DOE’s scope
of coverage. ‘‘Microwave oven’’ is
defined as a category of cooking
products which is a household cooking
appliance consisting of a compartment
designed to cook or heat food by means
of microwave energy, including
microwave ovens with or without
thermal elements designed for surface
browning of food and convection
microwave ovens. This includes any
microwave oven(s) component of a
combined cooking product.
For this proposal, DOE considered the
two product classes of microwave ovens
prescribed in the current energy
conservation standards: (1) MicrowaveOnly Ovens and Countertop Convection
Microwave Ovens, and (2) Built-In and
Over-the-Range Convection Microwave
Ovens.
For these two classes of microwave
ovens, DOE’s current test procedure
measures the energy consumption in
standby mode and off mode only.
Consequently, DOE’s current energy
conservation standards for microwave
ovens are also expressed in terms of
standby mode and off mode power.
There are currently no active mode
energy conservation standards nor a
prescribed test procedure for measuring
the active mode energy use or efficiency
(e.g., cooking efficiency) of microwave
ovens.
In response to the August 2022
SNOPR, AHAM and Whirlpool
requested that DOE consider changing
microwave oven product classes to align
with the three general chassis designs:
countertop, built-in, and over-the-range.
AHAM commented that the feature sets,
design requirements, consumer use
patterns, and standby powers are more
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correlated to chassis type than the
presence of convection functionality.
(AHAM, No. 28 at p. 12) AHAM further
stated that, on a shipment-weighted
average basis, countertop models
consume 0.6 W of standby power,
followed by over-the-range models, and
built-in models consuming 0.81 W and
1.65 W of standby power, respectively.
(AHAM, No. 28 at p. 13) Whirlpool
added that task lights, exhaust fans, and
environmental sensors are some of the
unique features of many over-the-range
microwave ovens. (Whirlpool, No. 30 at
p. 6).
In the June 2013 Final Rule, DOE
discussed its rationale for establishing
the current product class structure. In
that rulemaking, DOE acknowledged
that over-the-range microwave ovens
contain additional relays for
components that are not found in
countertop units, such as exhaust or
cooling fans and cooktop lighting.
However, these components were not
found in DOE’s analysis to require larger
power supplies that would affect
standby power consumption, and thus
would not warrant a separate product
class for over-the-range microwave-only
ovens from countertop microwave
ovens. 78 FR 36328. For this
rulemaking, DOE’s teardown and
analyses of the Compliance Certification
Database (‘‘CCD 16’’) showed that
microwave ovens have a wide variety of
features independent of chassis type.
DOE found various sensors, display
types, and connectivity features in overthe-range, built-in and countertop
microwave ovens. As such, DOE
determines that performance-related
features are fully reflected by the
current product class structure.
Additionally, AHAM claims via its
shipment-weighted average standby
power consumption data that the only
meaningful differentiation for product
classes is installation configuration.
AHAM however did not provide
shipments data with sufficient
granularity to contradict DOE’s previous
data and conclusions (i.e., to justify
eliminating product class differentiation
on the basis of convection features and
instead defining product classes solely
by installation configuration). As a
result, DOE is unable to rely on AHAM’s
data to revise the product classes.
Further, DOE is not aware of, nor did
AHAM provide, any data demonstrating
that consumer utility varies by chassis
type and has impacts on energy use that
would justify establishing separate
product classes. As a result, DOE is
16 Available at www.regulations.doe.gov/
certification-data.
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opting to maintain its current product
class structure.
TABLE IV.2—ESTIMATED MARKET
DISTRIBUTION OF MICROWAVE OVENS
3. Technology Options
In the preliminary market analysis
and technology assessment for the
August 2022 SNOPR, DOE identified
four technology options initially
determined to improve the efficiency of
microwave ovens, as measured by the
DOE test procedure:
TABLE IV.1—MICROWAVE OVEN
TECHNOLOGY OPTIONS
Technology option
Standby
Standby
Lower-power display technologies.
Cooking sensors with no standby
power requirement.
More efficient power supply and
control board options.
Automatic power-down of most
power-consuming components,
including the clock display.
Standby
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In support of the analysis for its
August 2022 SNOPR, DOE purchased
and tested 33 microwave ovens
representing the two proposed product
classes, and the results confirmed that
microwave oven models currently on
the market can achieve standby power
consumption values in-between the very
low levels enabled by automatic powerdown microwave ovens and the
proposed levels (i.e., 0.6 W for Product
Class 1 and 1.0 W for Product Class 2).
87 FR 52283. Further, DOE’s testing
suggested that microwave ovens are
frequently rated conservatively, such
that their certified standby power level
is higher than actual values obtained
when tested in accordance with
appendix I. Therefore, DOE was unable
to accurately assess the relationship
between specific standby power levels
and utilized technology options based
on data from the CCD. Instead, DOE
used the measured standby power levels
of microwave oven models in its test
sample as a proxy to determine the
representative distribution of standby
power levels among microwave ovens
on the market, as shown in Table IV.2.
Details of the methodology and results
from DOE’s investigative testing are
included in chapter 3 and chapter 5 of
the SNOPR TSD as well as the final rule
TSD.17
17 The final rule TSD as well as the SNOPR TSD
are available on the docket, www.regulations.gov/
document/EERE-2017-BT-STD-0023-0022.
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Market share
(%)
Microwave-Only Ovens and Countertop
Convection Microwave Ovens
1 ............................................
0.8 .........................................
0.6 .........................................
0.4 .........................................
15
45
29
11
Built-in and Over-the-Range Convection
Microwave Ovens
Mode
Standby
Standby power
(W)
2.2 .........................................
1.5 .........................................
1 ............................................
0.5 .........................................
0
36
59
5
AHAM commented that it disagreed
with DOE’s use of tested values rather
than CCD reported values in the August
2022 SNOPR, a practice it says
undermines the practice of
conservatively reporting standby power
to allow some ‘‘buffer’’ to ensure
consumers are getting what they are
promised. (AHAM, No. 28 at p. 9)
AHAM further commented that
conservative rating ensures compliance
with applicable standards by providing
a safety factor to account for
unavoidable variation in the
manufacturing process. DOE notes that
its tested values were often much lower
than the reported values in the CCD,
with differences as great as 1.43 W
(approximately 65 percent) for Product
Class 2 microwave ovens and 0.6192 W
(approximately 61 percent) for Product
Class 1 microwave ovens. DOE
determines these current ratings to be
significantly more conservative than is
necessary, considering electronics
manufacturing processes are sufficiently
advanced. Furthermore, DOE did not
see any variation in standby power
greater than 0.1 W in the duplicate test
units.
AHAM additionally commented that
the products that use significantly less
power than rated undermine the need
for new standards, as there is little to
gain. (AHAM, No. 28 at p. 9)
DOE reiterates that its analysis uses
an efficiency distribution based on
tested values that shows the existing
market to be more efficient compared to
that based on overly conservative rated
values. As discussed further in section
V.C.1 of this document, DOE’s analysis
demonstrates that despite the use of a
more efficient distribution in its
analysis as a starting point, the benefits
of the standard exceed, to a great extent,
the burdens at TSL 2 and an amended
standard set at this level for microwave
ovens would be economically justified.
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Additionally, AHAM’s comment
underscores the importance of testing
units rather than relying solely on data
from the CCD.
As part of the analysis for the August
2022 SNOPR, DOE subsequently tore
down all 33 microwave ovens, but was
unable to isolate a unique set of
technology options associated with each
standby power level. As such, DOE
concluded that models demonstrating
lower standby power consumption than
the current energy conservation
standards are not implementing specific
technology options; rather, they are
incorporating a comprehensive, systemlevel control board redesign that
prioritizes standby power performance
from the ground up. Examples of
possible redesign strategies include (1)
the replacement of microcontrollers
with modern ones that demonstrate
significantly lower quiescent current
consumption and (2) firmware that
emphasizes the shutting down of any
subassemblies that are not in use while
idle. DOE estimated that while these
improvements would not contribute to
the incremental manufacturer
production cost (‘‘MPC’’) of a control
board, the redesign would result in
significant conversion costs for
manufacturers as they attempt to bring
their microwave oven models into
compliance with any proposed
standards. See section IV.J.2.a of this
document.
In the August 2022 SNOPR, DOE
requested feedback on its tentative
conclusion that reducing the standby
power consumption of a microwave
oven would require a whole-board
redesign, and that manufacturers would
incur a one-time conversion cost
without any additional MPC. AHAM
and Whirlpool agreed with DOE’s
assessment that standby power
reduction is a system-level redesign
challenge, and that standby power often
cannot be reduced with simple
component changes. (AHAM, No. 28 at
p. 5; Whirlpool, No. 30 at p. 6) AHAM
and Whirlpool disagreed with DOE’s
conclusion that redesign would not
impact overall MPC of a given product.
Whirlpool commented that the new
classes of microprocessors, display
backlight circuits, display deep sleep
technologies, and power switches may
be necessary to reach higher
efficiencies, and that this will add to the
MPC for more efficient microwave
ovens. (Whirlpool, No. 30 at p. 7)
AHAM commented that changes to the
control board may require
manufacturers to evaluate and replace
or remove components affected by the
control board (e.g., displays, sensors,
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and clock) to reach amended standard
levels. (AHAM, No. 28 at p. 5)
In response to AHAM and
Whirlpool’s comments, DOE notes that
the analysis of the 33 microwave ovens
noted above included product
teardowns and establishing costed bill
of materials. DOE examined the
datasheets for components used in each
design but was unable to establish a
strong relationship between the use of
better components and a microwave
oven’s overall standby performance.
DOE found that while standby
performance could be improved by
opting for a better component, such as
in the case of microcontrollers with
deep sleep states, the cost differentials
were often zero or negative. In all
situations, DOE found that overall
circuit design rather than component
selection itself had a greater impact on
standby performance cost. In the
absence of additional cost data showing
a clear MPC-efficiency relationship,
DOE maintains its conclusion that any
system-level redesign would not
contribute to an incremental MPC
increase.
B. Screening Analysis
DOE uses the following five screening
criteria to determine which technology
options are suitable for further
consideration in an energy conservation
standards rulemaking:
(1) Technological feasibility.
Technologies that are not incorporated
in commercial products or in working
prototypes will not be considered
further.
(2) Practicability to manufacture,
install, and service. If it is determined
that mass production and reliable
installation and servicing of a
technology in commercial products
could not be achieved on the scale
necessary to serve the relevant market at
the time of the projected compliance
date of the standard, then that
technology will not be considered
further.
(3) Impacts on product utility or
product availability. If it is determined
that a technology would have a
significant adverse impact on the utility
of the product for significant subgroups
of consumers or would result in the
unavailability of any covered product
type with performance characteristics
(including reliability), features, sizes,
capacities, and volumes that are
substantially the same as products
generally available in the United States
at the time, it will not be considered
further.
(4) Adverse impacts on health or
safety. If it is determined that a
technology would have significant
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adverse impacts on health or safety, it
will not be considered further.
(5) Unique-Pathway Proprietary
Technologies. If a design option utilizes
proprietary technology that represents a
unique pathway to achieving a given
efficiency level, that technology will not
be considered further due to the
potential for monopolistic concerns.
Sections 6(b)(3) and 7(b) of appendix
A.
In sum, if DOE determines that a
technology, or a combination of
technologies, fails to meet one or more
of the listed five criteria, it will be
excluded from further consideration in
the engineering analysis. The reasons
for eliminating any technology are
discussed in the following sections.
The subsequent sections include
DOE’s evaluation of each technology
option against the screening analysis
criteria, and whether DOE determined
that a technology option should be
excluded (‘‘screened out’’) based on the
screening criteria.
1. Screened-Out Technologies
DOE considers whether a technology
option will adversely impact consumer
utility and product availability. To that
end, DOE has previously stated it is
uncertain the extent to which
consumers value the function of a
continuous display clock, but that loss
of such function may result in
significant loss of consumer utility. 78
FR 36316, 36362. Consistent with this
prior concern, DOE has screened out
‘‘automatic power-down’’ as a
technology option due to its impact on
consumer utility in this final rule.
2. Remaining Technologies
Through a review of each technology,
DOE concludes that all of the other
identified technologies listed in section
IV.B.2 of this document meet all five
screening criteria to be examined further
as design options in DOE’s final rule
analysis. In summary, DOE did not
screen out the following technology
options:
(1) Lower-power display technologies;
(2) Cooking sensors with no standby
power requirement; and
(3) More efficient power supply and
control board options.
DOE determines that these technology
options are technologically feasible
because they are being used or have
previously been used in commerciallyavailable products or working
prototypes. DOE also finds that all of the
remaining technology options meet the
other screening criteria (i.e., practicable
to manufacture, install, and service and
do not result in adverse impacts on
consumer utility, product availability,
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health, or safety). For additional details,
see chapter 4 of the final rule TSD.
AHAM and Whirlpool asserted that
DOE’s revised standards will cause an
unacceptable loss of product
functionality, and that future features
will not be able to be added to
microwave ovens due to feature power
draw and DOE’s practice of
undermining conservative ratings.
(AHAM, No. 28 at pp. 3–4, 8; Whirlpool,
No. 30 at p. 5) AHAM provided a
confidential list of various features that
it states would be impossible to
implement at DOE’s updated standards.
(AHAM, No. 28 at p. 4) AHAM
additionally commented that
manufacturers will also be unable to
incorporate indoor air quality (‘‘IAQ’’)
sensors, which may be required by
future state building codes and could be
impossible to implement due to EPCA’s
backsliding provision. (Id. at pp. 3, 13)
AHAM and Whirlpool commented that
other sensors may also need to be
removed as well, driving consumers to
use less efficient methods of cooking,
and Whirlpool added that it was not
aware of any humidity sensors that do
not impact standby power. (AHAM, No.
28 at p. 4; Whirlpool, No. 30 at pp. 4,
7) Finally, AHAM stated that updated
microwave oven standby power
standards could lead to a loss of
connectivity features in microwave
ovens. (AHAM, No 28 at p. 3)
The Joint Commenters commented
that they were able to find many
Product Class 1 18 units from various
manufacturers with reported powers
below 0.6 W that incorporated sensor
technologies. (Joint Commenters, No. 31
at p. 3)
In response to these comments, DOE
concludes that IAQ monitoring sensors
(smoke and carbon monoxide(‘‘CO’’))
are technologically mature enough to be
implemented without any significant
impact to microwave oven standby
power budgets due to the prevalence
and maturity of low-power smoke and
carbon monoxide detectors required by
most state building codes.19 DOE
researched additional sensors that might
be applicable for use in microwave
ovens, and found low-power options for
IAQ, such as the Bosch BME688, with
an average current consumption of 0.1
milliamps (‘‘mA’’) at 3.6 volts (‘‘V’’) in
low power mode, and the Renesas
ZMOD4410 with an average power
consumption of 0.16 milliwatts in ultralow power mode. Similarly, DOE found
18 Product Class 1 comprises microwave-only
ovens and countertop convection microwave ovens.
19 DOE found that the First Alert BRK PRC710
and Kidde P3010CU combination smoke and CO
detectors include sealed batteries meant to last 10
years.
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flame detection sensors, such as the
Kemet QFS series, with an average
current draw of 3.5 microamps (‘‘mA’’) at
3.6 V and PM sensors, such as the
Sensirion SPS30, with an idle current
draw of 330 mA and a sleep current
draw of 50 mA.
Regarding AHAM’s comment that
updated standards impact connectivity
features, DOE notes that section 2.1.1 of
appendix I instructs that if a microwave
oven can communicate through a
network (e.g., Bluetooth® or internet
connection), the network function is
disabled for the duration of standby
mode and off mode testing, if it is
possible to disable it by means provided
in the manufacturer’s user manual.
Furthermore, DOE’s testing did not find
any correlation between presence of
connected features and standby power
consumption. Similarly, DOE did not
find any standby power impact from
humidity sensors in the microwave
ovens tested and torn down. An
additional review of available humidity
sensors showed multiple models
without a listed electrical warm-up
time, as well as sensors with power
requirements less than 0.005 W (e.g.
review of datasheets for humidity
sensors from component manufacturers
such as Reneas, Amphenol, and Texas
Instrument shows typical supply
currents in the range of 1 to 200 mA).
With regards to loss of features and
functionality, DOE notes that many of
the features discussed confidentially by
AHAM were already present in the
microwave ovens torn down by DOE
and therefore were captured by DOE in
its analysis. DOE also determines that
those features discussed by AHAM that
were not seen in DOE’s teardown
analysis would not impact standby
power, as the microwave oven would
not be in standby mode while those
features are activated. Instead, the
features would be disconnected, turned
off, or put into a quiescent state 20 in
order to place the microwave oven in
standby mode for testing. As such, DOE
determines that amending standards
would neither impact the types of
sensors that can be used in microwave
oven designs nor adversely impact
consumer utility.
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C. Engineering Analysis
The purpose of the engineering
analysis is to establish the relationship
between the efficiency and cost of
microwave ovens. There are two
elements to consider in the engineering
20 In electronics design, Quiescent state or
Quiescent mode is defined as a state of inactivity
or dormancy, with attributes of very low current
draw.
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analysis; the selection of efficiency
levels to analyze (i.e., the ‘‘efficiency
analysis’’) and the determination of
product cost at each efficiency level
(i.e., the ‘‘cost analysis’’). In determining
the performance of higher-efficiency
microwave ovens, DOE considers
technologies and design option
combinations not eliminated by the
screening analysis. For each product
class, DOE estimates the baseline cost,
as well as the incremental cost for the
product/equipment at efficiency levels
above the baseline. The output of the
engineering analysis is a set of costefficiency ‘‘curves’’ that are used in
downstream analyses (i.e., the LCC and
PBP analyses and the NIA).
1. Efficiency Analysis
DOE typically uses one of two
approaches to develop energy efficiency
levels for the engineering analysis: (1)
relying on observed efficiency levels in
the market (i.e., the efficiency-level
approach), or (2) determining the
incremental efficiency improvements
associated with incorporating specific
design options to a baseline model (i.e.,
the design-option approach). Using the
efficiency-level approach, the efficiency
levels established for the analysis are
determined based on the market
distribution of existing products (in
other words, based on the range of
efficiencies and efficiency level
‘‘clusters’’ that already exist on the
market). Using the design option
approach, the efficiency levels
established for the analysis are
determined through detailed
engineering calculations and/or
computer simulations of the efficiency
improvements from implementing
specific design options that have been
identified in the technology assessment.
DOE may also rely on a combination of
these two approaches. For example, the
efficiency-level approach (based on
actual products on the market) may be
extended using the design option
approach to ‘‘gap fill’’ levels (to bridge
large gaps between other identified
efficiency levels) and/or to extrapolate
to the ‘‘max-tech’’ level (particularly in
cases where the ‘‘max-tech’’ level
exceeds the maximum efficiency level
currently available on the market).
In this rulemaking, DOE applied the
efficiency-level approach. As discussed,
DOE was unable to use the designoption approach because it did not
identify specific design options
associated with each standby power
level.
a. Baseline Efficiency/Energy Use
For each product class, DOE generally
selects a baseline model as a reference
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point against which to measure changes
resulting from energy conservation
standards. The baseline model in each
product class represents the
characteristics of a product typical of
that class (e.g., capacity, physical size).
Generally, a baseline model is one that
just meets current energy conservation
standards, or, if no standards are in
place, the baseline is typically the most
common or least efficient unit on the
market.
For microwave-only ovens and
countertop convection microwave ovens
(‘‘Product Class 1’’), the baseline
standby power level is equal to the
current standard of 1.0 W. For the builtin and over-the-range convection
microwave ovens product class
(‘‘Product Class 2’’), the baseline
standby power consumption used for
the analysis is equal to the current
standard of 2.2 W. This maximum
allowable average standby power
consumption for Product Class 2 is
higher than that allowed for Product
Class 1 microwave ovens because, in the
June 2013 Final Rule, DOE concluded
that built-in and over-the-range
convection microwave ovens require a
larger power supply to support
additional features, such as an exhaust
fan, additional relays, and additional
lights, and that the larger power supply
contributes to a higher standby power
consumption. 78 FR 36316, 36328.
Nonetheless, DOE expects that certain
available design options for reducing
standby power consumption for Product
Class 2 microwave ovens would be
similar to those for Product Class 1
microwave ovens.
b. Higher Efficiency Levels
Using the efficiency-level approach,
the higher efficiency levels established
for the analysis are determined based on
the market distribution of existing
products (in other words, based on the
range of efficiencies and efficiency level
‘‘clusters’’ that already exist on the
market). As noted in section IV.A.2 of
this document, DOE’s testing suggests
that microwave ovens are frequently
rated conservatively, such that their
certified standby power level is higher
than actual values obtained when tested
in accordance with appendix I. DOE
therefore used the measured standby
power levels of microwave oven models
in its test sample as a proxy to
determine the representative
distribution of standby power levels
among microwave ovens currently on
the market, as shown in Table IV.2.
According to this efficiency
distribution, 85 percent of Product Class
1 microwave ovens achieve a standby
power consumption lower than the
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current standard of 1.0 W, with 45
percent of the market estimated to be
achieving 0.8 W, 29 percent achieving
0.6 W, and 11 percent achieving 0.4 W,
all without the use of automatic powerdown. For Product Class 1, therefore,
DOE analyzed three efficiency levels
(‘‘ELs’’) above the baseline, which
correspond to these three standby power
levels, as shown in Table IV.3.
The test results also showed that all
of the Product Class 2 test units
achieved a standby power consumption
in the range of 0.5 W to 1.5 W, lower
than the current standard of 2.2 W. As
such, DOE analyzed higher efficiency
levels for this product class at standby
power values evenly distributed within
that range: EL 1 at 1.5 W, EL 2 at 1.0
W, and EL 3 (max-tech) at 0.5 W. DOE
estimates that there are currently no
built-in and over-the-range convection
microwave ovens in the market at the
baseline standby power consumption of
2.2 W.
In summary, DOE analyzed the
following efficiency levels for this rule:
TABLE IV.3—ANALYZED EFFICIENCY
LEVELS
FOR
MICROWAVE-ONLY
OVENS AND COUNTERTOP CONVECTION MICROWAVE OVENS
Efficiency level
Standby power
(W)
Baseline ................................
1 ............................................
2 ............................................
3 (Max-Tech) ........................
1.00
0.8
0.6
0.4
TABLE IV.4—ANALYZED EFFICIENCY
LEVELS FOR BUILT-IN AND OVERTHE-RANGE CONVECTION MICROWAVE OVENS
Efficiency level
Standby power
(W)
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Baseline ................................
1 ............................................
2 ............................................
3 (Max-Tech) ........................
2.2
1.5
1.0
0.5
The Joint Commenters requested that
DOE analyze an additional efficiency
level above max-tech, citing a number of
microwave ovens in the CCD with
reported standby powers of less than 0.3
W. The Joint Commenters further stated
that many of these microwave ovens do
not utilize the screened-out automatic
power-down technology option, making
this a viable efficiency level for
manufacturers.
With regard to the Joint Commenters
request, DOE’s review of the market has
shown that the majority of the
microwave ovens at or below 0.3 W
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utilize other screened-out technology
options (no clock, no display, and
automatic power-down) to achieve a
low standby power, and that an EL
above max-tech would require designing
microwave ovens with a significant
impact to consumer utility. Also, as
discussed further in section V.C of this
document, DOE has determined that
there is uncertainty as to whether or not
a standard at max-tech would stifle
innovation and risk impacting customer
utility. Accordingly, DOE has elected
not to analyze an efficiency level above
the max-tech discussed in the August
2022 SNOPR.
AHAM and Whirlpool commented
that electromagnetic interference
(‘‘EMI’’) filtration boards draw a
significant amount of power that DOE’s
analysis did not take into account.
(AHAM, No. 28 at p. 6; Whirlpool, No.
30, at pp. 2–3) Furthermore, AHAM
stated that EMI filters that draw less
power than those currently in use may
not be as effective at filtering out
conducted electromagnetic fields
(‘‘EMF’’). Whirlpool stated that effective
filter designs can account for up to 0.3
W of standby power in a microwave
oven. (Whirlpool, No. 30 at p. 4) AHAM
commented that a survey of the current
market found filter board power
contributions of 0.17 W for countertop
microwave ovens, 0.22 W for over-therange microwave ovens, and 0.08 W for
built-in microwave ovens (AHAM, No.
28 at p. 6).
As detailed in chapter 5 of the final
rule TSD, DOE conducted a number of
additional standby power tests on a
sample of nine microwave ovens from
both product classes after removing
their input power filtration boards.
Tested units included inverter
microwave ovens, which tend to have
more expensive and complex filtration
boards, and units with different sensors
and WiFi functionality.
DOE found that the sampled power
filtration boards, on average, account for
only 0.012 W of power during standby
testing, calculated as the difference
between the standby power with the
filter installed and the standby power
without the filter installed. This average
measured value of 0.012 W is
approximately 25 times less than
Whirlpool’s estimate (0.3 W) and about
10 times less than the shipmentweighted average of AHAM’s reported
values (0.173 W) using shipment
weights provided by Whirlpool in its
comments. (Whirlpool, No. 30 at p. 6)
DOE conducted a single-tailed T-test to
determine whether AHAM’s reported
mean differs in a statistically significant
way from the measured mean. The
resulting p-value rejected the null
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hypothesis (i.e., the difference is indeed
statistically significant and not due to
sampling artifices). Whirlpool
commented that DOE’s tested models
may not utilize the highest levels of
filtering. (Whirlpool, No. 30 at p. 4)
Since neither AHAM nor Whirlpool
provided any further information
identifying brands and models used to
arrive at these values, DOE cannot verify
the comments that EMI filtration boards
take up a significant amount of a
microwave’s standby power budget, nor
that DOE’s tests were not representative
of the market.
DOE performed additional teardown
analysis of power filter boards from
tested microwave ovens. All boards
were passive filtration boards that
utilize (1) a selection of capacitors and
a common mode choke for mains power
filtration; (2) a safety capacitor bleed
resistor used to discharge capacitors that
might otherwise shock a user when
unplugging the unit from the wall; and
(3) In some cases, a metal oxide varistor
likely for voltage transient suppression.
The primary standby power draw of this
circuit is the always-connected bleeder
resistor, which can be further
eliminated with minimal impact to EMI
filtration quality by using any number of
automatic safety capacitor discharge
circuits. However, this approach to
reducing standby power with an
automatic safety capacitor discharge
circuit would only be relevant and
meaningful if the power consumption of
EMI filters with regular bleed resistors
were significant. As discussed
previously, DOE’s testing showed power
consumption of EMI filters to be a
fraction of what AHAM and Whirlpool
commented. The use of automatic
capacitor discharge circuits would
therefore not be meaningful and/or
necessary.
Additionally, AHAM commented that
microwave ovens account for 40.51
percent of consumer-reported nuisance
trips when connected to a mains line
with an arc-fault circuit interrupter
(‘‘AFCI’’) circuit breaker. (AHAM, No.
28 at p. 8) AHAM stated that
manufacturers traditionally outfit
microwave ovens with EMI filters
designed to only meet emissions limits
established by the Federal
Communications Commission (‘‘FCC’’)
in 47 CFR part 15 and 47 CFR part 18
(referred to as ‘‘Part 15’’ and ‘‘Part 18’’),
and that actual limits for avoiding
accidental ‘‘nuisance’’ tripping are
much more stringent and require EMI
filters that consume more power.
(AHAM, No. 28 at pp. 6–8) With
increasing use of AFCIs in homes,
Whirlpool commented that DOE must
account for the additional power draw
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of AFCI-compliant EMI filters when
amending standards or risk losing other
features that provide consumer utility.
(Whirlpool, No. 30 at p. 4)
DOE researched guidance for
appliance manufacturers on ensuring
compatibility with AFCI outlets. As part
of its efforts to promote the use of
AFCIs, the National Electrical
Manufacturer’s Association (‘‘NEMA’’)
has published guidelines 21 for
appliance manufacturers that wish to
design appliances that are compatible
with AFCI outlets. These guidelines
were developed by the Molded Case
Circuit Breaker Product Group of the
Low Voltage Distribution Equipment
Section of NEMA. At the time of
publication, this group included ABB
Control, Inc.; Eaton Corporation;
General Electric; Siemens Industry, Inc.;
and Schneider Electric USA, all
manufacturers of AFCIs. Although it is
unclear how many of these members
participated in the development of
NEMA’s guidance, DOE has not found
contradicting guidance from any AFCI
manufacturers.
NEMA’s white paper describes the
emission limits recommendations for
appliance manufacturers. Specifically,
NEMA recommends that manufacturers
meet Part 15 requirements for Class B
devices, even if appliances are not
subject to these regulations. DOE notes
that the Part 15 requirements for
conducted emissions of Class B devices
are the same as the Part 18 requirements
for consumer devices other than
induction cooking ranges and ultrasonic
equipment. Thus, if manufacturers are
designing microwave ovens to meet Part
18 requirements as AHAM states, they
are following the leading industry
guidance for avoiding AFCI nuisance
tripping.
Although AHAM commented that
AFCIs are being improperly tripped by
normal microwave use, DOE recognizes
that there are many potential sources of
arcing in a microwave oven that may be
difficult for consumers to recognize,
potentially leading to an over-reporting
of nuisance tripping. Unwanted arcing
can occur during cooking if there are
materials that reflect microwaves; the
microwave is improperly loaded (ran
empty or nearly empty); or there is a
stalled stirrer blade or non-rotating
antenna, which may not be visible to the
consumer, resulting in reflected
microwaves. In all three of these cases,
the AFCI is performing its function
correctly by detecting arcs and
preventing further power draw, though
consumers may not be aware that these
arcs are occurring. Microwave ovens
also rely on a number of relays to
control various functionality. Relays, if
not properly implemented, can also be
prone to producing excessive arcing that
may trip AFCIs. Thus, AFCIs can
correctly trip from detected arcs that
may be invisible to consumers.
In sum, DOE does not find that future
EMI filter board designs would
substantively alter the standby power
levels that microwave ovens can achieve
and concludes, therefore, that EMI
filtration board power draw will not
prohibit future innovation in microwave
ovens. Further, DOE determined that
microwave ovens are already meeting
the leading guidance for avoiding
nuisance tripping and will continue to
do so as long as manufacturers design
according to mandatory FCC standards.
2. Cost Analysis
The cost analysis portion of the
engineering analysis is conducted using
one or a combination of cost
approaches. The selection of cost
approach depends on a suite of factors,
including the availability and reliability
of public information, characteristics of
the regulated product, and the
availability and timeliness of
purchasing the microwave oven on the
market. The cost approaches are
summarized as follows:
• Physical teardowns: Under this
approach, DOE physically dismantles a
commercially available product,
component-by-component, to develop a
detailed bill of materials for the product.
• Catalog teardowns: In lieu of
physically deconstructing a product,
DOE identifies each component using
parts diagrams (available from
manufacturer websites or appliance
repair websites, for example) to develop
the bill of materials for the product.
• Price surveys: If neither a physical
nor catalog teardown is feasible (for
example, for tightly integrated products
such as fluorescent lamps, which are
infeasible to disassemble and for which
parts diagrams are unavailable) or costprohibitive and otherwise impractical
(e.g., large commercial boilers), DOE
conducts price surveys using publicly
available pricing data published on
major online retailer websites and/or by
soliciting prices from distributors and
other commercial channels.
For microwave ovens, DOE attempted
to estimate the MPC of attaining each
efficiency level using the physical
teardowns approach described
previously. As stated in section IV.A.2
of this document, DOE tore down all 33
microwave ovens in its test sample but
was unable to isolate a unique set of
technology options associated with each
standby power level. As such, DOE
concludes that models demonstrating
lower standby power consumption than
the current energy conservation
standards are not implementing specific
technology options, but rather
incorporate a comprehensive systemlevel control board design that
prioritizes standby power performance
from the ground up. Examples of
possible design strategies include the
replacement of microcontrollers and
switch mode controllers with modern
ones that demonstrate significantly
lower quiescent current consumption at
no additional cost compared to those
found in inefficient systems and
firmware that emphasizes the shutting
down of all subassemblies that are not
in use while idle. DOE estimates that,
while these improvements would not
contribute to an increase in the MPC of
a control board (i.e., incremental MPC of
$0), the redesign would result in
conversion costs for manufacturers as
they bring their microwave oven models
into compliance with any proposed
standards. See section IV.J.2.a of this
document. To account for
manufacturers’ non-production costs
and profit margin, DOE applies a
multiplier (the manufacturer markup) to
the MPC. The resulting MSP is the price
at which the manufacturer distributes a
unit into commerce. DOE developed an
average manufacturer markup by
examining the annual Securities and
Exchange Commission (‘‘SEC’’) 10–K
reports filed by publicly-traded
manufacturers primarily engaged in
household cooking appliance
manufacturing and whose combined
product range includes microwave
ovens.
3. Cost-Efficiency Results
The results of the engineering analysis
are reported as cost-efficiency data (or
‘‘curves’’) in the form of MPC (in
dollars) versus standby power
consumption (in W). For the reasons
discussed in sections IV.A.2 and IV.C.2
of this document, DOE estimated an
incremental MPC of $0 at all higher
efficiency levels, compared to the
baseline MPC, for both of the product
classes, as shown in Table IV.5 and
Table IV.6 of this document. See chapter
5 of the final rule TSD for additional
detail on the engineering analysis.
21 National Electrical Manufacturer’s Association.
Recommendations on AFCI/Home Electrical
Product Compatibility. 2011. Rosslyn, VA.
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TABLE IV.5—ANALYZED EFFICIENCY LEVELS AND INCREMENTAL MANUFACTURER PRODUCTION COSTS FOR MICROWAVEONLY OVENS AND COUNTERTOP CONVECTION MICROWAVE OVENS
Standby power
(W)
Efficiency level
Baseline ...................................................................................................................................................................
1 ...............................................................................................................................................................................
2 ...............................................................................................................................................................................
3 ...............................................................................................................................................................................
1.00
0.8
0.6
0.4
Incremental
MPC
(2021$)
........................
0.0
0.0
0.0
TABLE IV.6—ANALYZED EFFICIENCY LEVELS AND INCREMENTAL MANUFACTURER PRODUCTION COSTS FOR BUILT-IN AND
OVER-THE-RANGE CONVECTION MICROWAVE OVENS
Standby power
(W)
Efficiency level
Baseline ...................................................................................................................................................................
1 ...............................................................................................................................................................................
2 ...............................................................................................................................................................................
3 ...............................................................................................................................................................................
D. Markups Analysis
The markups analysis develops
appropriate markups (e.g., retailer
markups, distributor markups,
contractor markups) in the distribution
chain and sales taxes to convert the
MSP estimates derived in the
engineering analysis to consumer prices,
which are then used in the LCC and PBP
analysis. At each step in the distribution
channel, companies mark up the price
of the product to cover business costs
and profit margin.
For microwave ovens, DOE further
developed baseline and incremental
markups for each link in the
distribution chain (after the product
leaves the manufacturer). Baseline
markups are applied to the price of
products with baseline efficiency, while
incremental markups are applied to the
difference in price between baseline and
higher-efficiency models (the
incremental cost increase). The
incremental markup is typically less
than the baseline markup and is
designed to maintain similar per-unit
operating profit before and after new or
amended standards.22
DOE relied on economic data from the
U.S. Census Bureau to estimate average
baseline and incremental markups.
Specifically, DOE used the 2017 Annual
Retail Trade Survey for the ‘‘electronics
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22 Because
the projected price of standardscompliant products is typically higher than the
price of baseline products, using the same markup
for the incremental cost and the baseline cost would
result in higher per-unit operating profit. While
such an outcome is possible, DOE maintains that in
markets that are reasonably competitive, it is
unlikely that standards would lead to a sustainable
increase in profitability in the long run.
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and appliance stores’’ sector to develop
retailer markups.23
Chapter 6 of the final rule TSD
provides details on DOE’s development
of markups for microwave ovens.
E. Energy Use Analysis
The purpose of the energy use
analysis is to determine the annual
energy consumption of microwave
ovens at different efficiencies in
representative U.S. single-family homes,
multi-family residences, and mobile
homes, and to assess the energy savings
potential of increased microwave ovens
efficiency. The energy use analysis
estimates the range of energy use of
microwave ovens in the field (i.e., as
they are actually used by consumers).
The energy use analysis provides the
basis for other analyses DOE performed,
particularly assessments of the energy
savings and the savings in consumer
operating costs that could result from
adoption of amended or new standards.
For this final rule, DOE used the same
methodology as that described in
section IV.D of the August 2022 SNOPR.
In the June 2013 Final Rule, DOE
determined the average hours of
operation for microwave ovens to be
44.9 hours per year.24 25 To calibrate the
average annual operating hours, DOE
primarily used data from the EIA’s 2020
Residential Energy Consumption Survey
23 US Census Bureau, Annual Retail Trade
Survey. 2017. www.census.gov/programs-surveys/
arts.html.
24 Uniform Test Method for Measuring the Energy
Consumption of Cooking Products. 10 CFR part 430,
subpart B, appendix I, www.law.cornell.edu/cfr/
text/10/appendix-I_to_subpart_B_of_part_430.
25 Williams, et al. 2012. Surveys of Microwave
Ovens in U.S. Homes. LBNL–5947E www.osti.gov/
biblio/1172657.
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1.5
1.00
0.5
Incremental
MPC
(2021$)
........................
$0.0
$0.0
$0.0
(‘‘RECS’’).26 RECS 2020 provides
information on the frequency of
microwave oven usage per week for
each household. DOE calculated the
RECS microwave oven usage factor for
each household in the sample by
dividing the weighted-average usage
based on the entire RECS samples. DOE
then multiplied the usage factor by the
annual operating hours (i.e., 44.9 hours)
for each household in the RECS. DOE
subtracted field microwave ovens
operating hours from the total number
of hours in a year and multiplied that
difference by the standby mode power
usage at each efficiency level to
determine annual standby mode and off
mode energy consumption.
Chapter 7 of the final rule TSD
provides details on DOE’s energy use
analysis for microwave ovens.
F. Life-Cycle Cost and Payback Period
Analysis
DOE conducted LCC and PBP
analyses to evaluate the economic
impacts on individual consumers of
potential energy conservation standards
for microwave ovens. The effect of new
or amended energy conservation
standards on individual consumers
usually involves a reduction in
operating cost and an increase in
purchase cost. DOE used the following
two metrics to measure consumer
impacts:
• The LCC is the total consumer
expense of an appliance or product over
the life of that product, consisting of
26 U.S. Department of Energy-Energy Information
Administration, Residential Energy Consumption
Survey, 2020 Public Use Microdata Files, 2015.
Washington, DC. Available online at:
www.eia.doe.gov/emeu/recs/recspubuse20/
pubuse20.html.
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total installed cost (manufacturer selling
price, distribution chain markups, sales
tax, and installation costs) plus
operating costs (expenses for energy use,
maintenance, and repair). To compute
the operating costs, DOE discounts
future operating costs to the time of
purchase and sums them over the
lifetime of the product.
• The PBP is the estimated amount of
time (in years) it takes consumers to
recover the increased purchase cost
(including installation) of a moreefficient product through lower
operating costs. DOE calculates the PBP
by dividing the change in purchase cost
at higher efficiency levels by the change
in annual operating cost for the year that
amended or new standards are assumed
to take effect.
For any given efficiency level, DOE
measures the change in LCC relative to
the LCC in the no-new-standards case,
which reflects the estimated efficiency
distribution of microwave ovens in the
absence of new or amended energy
conservation standards. In contrast, the
PBP for a given efficiency level is
measured relative to the baseline
product.
For each considered efficiency level
in each product class, DOE calculated
the LCC and PBP for a nationally
representative set of housing units. As
stated previously, DOE developed
household samples from the RECS 2020.
For each sample household, DOE
determined the energy consumption for
the microwave ovens and the
appropriate energy price. By developing
a representative sample of households,
the analysis captured the variability in
energy consumption and energy prices
associated with the use of microwave
ovens.
Inputs to the calculation of total
installed cost include the cost of the
product—which includes MPCs,
manufacturer markups, retailer and
distributor markups, and sales taxes—
and installation costs. Inputs to the
calculation of operating expenses
include annual energy consumption,
energy prices and price projections,
repair and maintenance costs, product
lifetimes, and discount rates. DOE
created distributions of values for
product lifetime, discount rates, and
sales taxes, with probabilities attached
to each value, to account for their
uncertainty and variability.
The computer model DOE uses to
calculate the LCC relies on a Monte
Carlo simulation to incorporate
uncertainty and variability into the
analysis. The Monte Carlo simulations
randomly sample input values from the
probability distributions and microwave
ovens user samples. For this
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rulemaking, the Monte Carlo approach
is implemented in MS Excel together
with the Crystal BallTM add-on.27 The
model calculated the LCC for products
at each efficiency level for 10,000
housing units per simulation run. The
analytical results include a distribution
of 10,000 data points showing the range
of LCC savings for a given efficiency
level relative to the no-new-standards
case efficiency distribution. In
performing an iteration of the Monte
Carlo simulation for a given consumer,
product efficiency is chosen based on its
probability. If the chosen product
efficiency is greater than or equal to the
efficiency of the standard level under
consideration, the LCC calculation
reveals that a consumer is not impacted
by the standard level. By accounting for
consumers who already purchase moreefficient products, DOE avoids
overstating the potential benefits from
increasing product efficiency. DOE
calculated the LCC and PBP for
consumers of microwave ovens as if
each were to purchase a new product in
the first year of required compliance
with new or amended standards.
Amended standards apply to microwave
ovens manufactured 3 years after the
date on which any new or amended
standard is published. (42 U.S.C.
6295(g)(10)(B)) Therefore, DOE used
2026 as the first year of compliance with
any amended standards for microwave
ovens.
Table IV.5 summarizes the approach
and data DOE used to derive inputs to
the LCC and PBP calculations. The
subsections that follow provide further
discussion. Details of the spreadsheet
model, and of all the inputs to the LCC
and PBP analyses, are contained in
chapter 8 of the final rule TSD and its
appendices.
39929
TABLE IV.5—SUMMARY OF INPUTS AND
METHODS FOR THE LCC AND PBP
ANALYSIS *—Continued
Inputs
Source/method
Annual Energy
Use.
The total annual energy use
multiplied by the hours per
year. Average number of
hours based on field data.
Variability: Based on the
RECS 2020.
Electricity: Based on EEI
2021.
Variability: Regional energy
prices determined for nine
regions.
Based on AEO2022 price
projections.
Assumed no change with efficiency level.
Energy Prices
Energy Price
Trends.
Repair and
Maintenance
Costs.
Product Lifetime.
Discount Rates
Compliance
Date.
Average: 10.78 years.
Approach involves identifying
all possible debt or asset
classes that might be used
to purchase the considered appliances, or might
be affected indirectly. Primary data source was the
Federal Reserve Board’s
Survey of Consumer Finances.
2026.
* Not used for PBP calculation. References
for the data sources mentioned in this table
are provided in the sections following the table
or in chapter 8 of the final rule TSD.
1. Product Cost
To calculate consumer product costs,
DOE multiplied the MPCs developed in
the engineering analysis by the markups
described previously (along with sales
taxes). DOE used different markups for
baseline products and higher-efficiency
products, because DOE applies an
incremental markup to the increase in
TABLE IV.5—SUMMARY OF INPUTS AND MSP associated with higher-efficiency
METHODS FOR THE LCC AND PBP products.
Economic literature and historical
ANALYSIS *
data suggest that the real costs of many
products may trend downward over
Inputs
Source/method
time according to ‘‘learning’’ or
Product Cost .. Derived by multiplying MPCs ‘‘experience’’ curves. An experience
by manufacturer and recurve analysis implicitly includes
tailer markups and sales
factors such as efficiencies in labor,
tax, as appropriate. Used
capital investment, automation,
historical data to derive a
materials prices, distribution, and
price scaling index to
economies of scale at an industry-wide
project product costs.
Installation
Assumed no change with ef- level. To derive the learning rate
parameter for microwave ovens, DOE
Costs.
ficiency level.
obtained historical Producer Price Index
(‘‘PPI’’) data for microwave ovens from
27 Crystal BallTM is a commercially-available
the Bureau of Labor Statistics (‘‘BLS’’).
software tool to facilitate the creation of these types
of models by generating probability distributions
A PPI for ‘‘Household Cooking
and summarizing results within Excel, available at
Appliance Manufacturing: Electric
www.oracle.com/technetwork/middleware/
(Including Microwave) Household
crystalball/overview/ (last accessed
Ranges, Ovens, Surface Cooking Units,
December 13, 2022).
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
and Equipment’’ was available for the
time period between 1972 and 2020.28
Inflation-adjusted price indices were
calculated by dividing the PPI series by
the gross domestic product index from
the Bureau of Economic Analysis for the
same years. Using data from 1972–2020,
the estimated learning rate (defined as
the fractional reduction in price
expected from each doubling of
cumulative production) is 10.7 percent.
2. Installation Cost
Installation cost includes labor,
overhead, and any miscellaneous
materials and parts needed to install the
product. DOE used data from 2022 to
estimate the baseline installation cost
for microwave ovens. DOE found no
evidence that installation costs would
be impacted with increased efficiency
levels.
3. Annual Energy Consumption
For each sampled household, DOE
determined the energy consumption for
a microwave oven at different efficiency
levels using the approach described
previously in section IV.E of this
document.
4. Energy Prices
Because marginal electricity price
more accurately captures the
incremental savings associated with a
change in energy use from higher
efficiency, it provides a better
representation of incremental change in
consumer costs than average electricity
prices. Therefore, DOE applied average
electricity prices for the energy use of
the product purchased in the no-newstandards case, and marginal electricity
prices for the incremental change in
energy use associated with the other
efficiency levels considered.
DOE derived electricity prices in 2022
using data from Edison Electric Institute
(‘‘EEI’’) Typical Bills and Average Rates
reports.29 Based upon comprehensive,
industry-wide surveys, this semi-annual
report presents typical monthly electric
bills and average kilowatt-hour costs to
the customer as charged by investorowned utilities. For the residential
sector, DOE calculated electricity prices
using the methodology described in
Coughlin and Beraki (2018).30 For the
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28 U.S.
Bureau of Labor Statistics, PPI Industry
Data, Major household appliance manufacturers,
Product series ID: PCU 33522033522011. Data series
available at: www.bls.gov/ppi/.
29 Edison Electric Institute. Typical Bills and
Average Rates Report. 2020. Winter 2020, Summer
2020: Washington, DC
30 Coughlin, K. and B. Beraki.2018. Residential
Electricity Prices: A Review of Data Sources and
Estimation Methods. Lawrence Berkeley National
Lab. Berkeley, CA. Report No. LBNL–2001169.
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commercial sector, DOE calculated
electricity prices using the methodology
described in Coughlin and Beraki
(2019).31
DOE’s methodology allows electricity
prices to vary by sector, region, and
season. In the analysis, variability in
electricity prices is chosen to be
consistent with the way the consumer
economic and energy use characteristics
are defined in the LCC analysis. For
microwave ovens, DOE derived
electricity prices in 2022 using data
from EEI. DOE used the EEI data to
define a marginal price as the ratio of
the change in the bill to the change in
energy consumption. See chapter 8 of
the final rule TSD for details.
To estimate energy prices in future
years, DOE multiplied the 2020 energy
prices by the projection of annual
average price changes for each of the
nine census divisions from the
Reference case in AEO2022, which has
an end year of 2050.32 To estimate price
trends after 2050, the 2046–2050
average was used for all subsequent
years.
5. Maintenance and Repair Costs
Repair costs are associated with
repairing or replacing product
components that have failed in an
appliance; maintenance costs are
associated with maintaining the
operation of the product. Typically,
small incremental increases in product
efficiency entail no, or only minor,
changes in repair and maintenance costs
compared to baseline efficiency
products. In this final rule analysis,
DOE included no changes in
maintenance or repair costs for
microwave ovens that exceed baseline
efficiency.
6. Product Lifetime
For microwave ovens, DOE developed
a distribution of lifetimes from which
specific values are assigned to the
appliances in the samples. DOE
conducted an analysis of actual lifetime
in the field using a combination of
historical shipments data, the stock of
the considered appliances in the
American Housing Survey, and
responses in RECS on the age of the
ees.lbl.gov/publications/residential-electricityprices-review.
31 Coughlin, K. and B. Beraki. 2019. Nonresidential Electricity Prices: A Review of Data
Sources and Estimation Methods. Lawrence
Berkeley National Lab. Berkeley, CA. Report No.
LBNL–2001203. ees.lbl.gov/publications/nonresidential-electricity-prices.
32 U.S. Department of Energy—Energy
Information Administration. Annual Energy
Outlook 2018 with Projections to 2050. Washington,
DC. Available at www.eia.gov/forecasts/aeo/ (last
accessed December 13, 2022).
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appliances in the homes. The data
allowed DOE to estimate a survival
function, which provides an average
appliance lifetime. This analysis yielded
a lifetime probability distribution with
an average lifetime for microwave ovens
of approximately 10.78 years. See
chapter 8 of the final rule TSD for
further details.
7. Discount Rates
In the calculation of LCC, DOE
applies discount rates appropriate to
households to estimate the present
value of future operating cost savings.
DOE estimated a distribution of
discount rates for microwave ovens
based on the opportunity cost of
consumer funds.
DOE applies weighted average
discount rates calculated from consumer
debt and asset data, rather than marginal
or implicit discount rates.33 The LCC
analysis estimates net present value
over the lifetime of the product, so the
appropriate discount rate will reflect the
general opportunity cost of household
funds, taking this time scale into
account. Given the long time horizon
modeled in the LCC, the application of
a marginal interest rate associated with
an initial source of funds is inaccurate.
Regardless of the method of purchase,
consumers are expected to continue to
rebalance their debt and asset holdings
over the LCC analysis period, based on
the restrictions consumers face in their
debt payment requirements and the
relative size of the interest rates
available on debts and assets. DOE
estimates the aggregate impact of this
rebalancing using the historical
distribution of debts and assets.
To establish residential discount rates
for the LCC analysis, DOE identified all
relevant household debt or asset classes
in order to approximate a consumer’s
opportunity cost of funds related to
appliance energy cost savings. It
estimated the average percentage shares
of the various types of debt and equity
by household income group using data
from the Federal Reserve Board’s
triennial Survey of Consumer
33 The implicit discount rate is inferred from a
consumer purchase decision between two otherwise
identical goods with different first cost and
operating cost. It is the interest rate that equates the
increment of first cost to the difference in net
present value of lifetime operating cost,
incorporating the influence of several factors:
transaction costs; risk premiums and response to
uncertainty; time preferences; and interest rates at
which a consumer is able to borrow or lend. The
implicit discount rate is not appropriate for the LCC
analysis because it reflects a range of factors that
influence consumer purchase decisions, rather than
the opportunity cost of the funds that are used in
purchases.
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
Finances 34 (‘‘SCF’’) starting in 1995 and
ending in 2019. Using the SCF and other
sources, DOE developed a distribution
of rates for each type of debt and asset
by income group to represent the rates
that may apply in the year in which
amended standards would take effect.
DOE assigned each sample household a
specific discount rate drawn from one of
the distributions. The average rate
across all types of household debt and
equity and income groups, weighted by
the shares of each type, is 4.3 percent.
See chapter 8 of the final rule TSD for
further details on the development of
consumer discount rates.
8. Energy Efficiency Distribution in the
No-New-Standards Case
To accurately estimate the share of
consumers that would be affected by a
potential energy conservation standard
at a particular efficiency level, DOE’s
LCC analysis considered the projected
distribution (market shares) of product
efficiencies under the no-new-standards
39931
case (i.e., the case without amended or
new energy conservation standards).
To estimate the energy efficiency
distribution of microwave ovens for
2026, DOE used data from the
engineering analysis. The estimated
market shares for the no-new-standards
case for microwave ovens are shown in
Table IV.6. See chapter 8 of the final
rule TSD for further information on the
derivation of the efficiency
distributions.
TABLE IV.6—NO-NEW-STANDARDS CASE EFFICIENCY DISTRIBUTION FOR MICROWAVE OVENS IN 2026
Product class 1:
microwave-only and
countertop convection
microwave ovens
TSL
Standby power
(W)
Baseline .........
1 .....................
2 .....................
3 .....................
Market share
(%)
1.00
0.8
0.6
0.4
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In response to the August 2023
SNOPR, AHAM stated that the CCD is
not an accurate determination of
efficiency distributions. (AHAM, No. 28
at p. 10) DOE agrees that shipmentweighted efficiency distributions would
be preferable to shares based on model
counts, but such data were not available
for microwave ovens, and there is no
firm basis to make an adjustment to the
model count market shares. DOE’s
approach may well overstate the market
share of higher-efficiency products in
the absence of new standards, but this
would mean that the energy and
economic benefits estimated by DOE for
new standards are minimum amounts.
The justification for the adopted
standards would be even stronger if
DOE were able to use actual shipment
data for the model counts.
The LCC Monte Carlo simulations
draw from the efficiency distributions
and randomly assign an efficiency to the
microwave oven purchased by each
sample household in the no-newstandards case. The resulting percent
shares within the sample match the
market shares in the efficiency
distributions.
9. Payback Period Analysis
The payback period is the amount of
time (expressed in years) it takes the
consumer to recover the additional
installed cost of more-efficient products,
34 U.S. Board of Governors of the Federal Reserve
System. Survey of Consumer Finances. 1995, 1998,
2001, 2004, 2007, 2010, 2013, 2016, and 2019.
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Standby power
(W)
15
45
29
11
2.20
1.5
1.0
0.5
compared to baseline products, through
energy cost savings. Payback periods
that exceed the life of the product mean
that the increased total installed cost is
not recovered in reduced operating
expenses.
The inputs to the PBP calculation for
each efficiency level are the change in
total installed cost of the product and
the change in the first-year annual
operating expenditures relative to the
baseline. DOE refers to this as a ‘‘simple
PBP’’ because it does not consider
changes over time in operating cost
savings. The PBP calculation uses the
same inputs as the LCC analysis when
deriving first-year operating costs.
As noted previously, EPCA
establishes a rebuttable presumption
that a standard is economically justified
if the Secretary finds that the additional
cost to the consumer of purchasing a
product complying with an energy
conservation standard level will be less
than three times the value of the first
year’s energy savings resulting from the
standard, as calculated under the
applicable test procedure. (42 U.S.C.
6295(o)(2)(B)(iii)) For each considered
efficiency level, DOE determined the
value of the first year’s energy savings
by calculating the energy savings in
accordance with the applicable DOE test
procedure, and multiplying those
savings by the average energy price
projection for the year in which
Available at www.Federalreserve.gov/econresdata/
scf/scfindex.htm (last accessed December 13, 2022).
35 DOE uses data on manufacturer shipments as
a proxy for national sales, as aggregate data on sales
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Market share
(%)
0
36
59
5
compliance with the amended standards
would be required.
G. Shipments Analysis
DOE uses projections of annual
product shipments to calculate the
national impacts of potential amended
or new energy conservation standards
on energy use, NPV, and future
manufacturer cash flows.35 The
shipments model takes an accounting
approach, tracking market shares of
each product class and the vintage of
units in the stock. Stock accounting uses
product shipments as inputs to estimate
the age distribution of in-service
product stocks for all years. The age
distribution of in-service product stocks
is a key input to calculations of both the
NES and NPV, because operating costs
for any year depend on the age
distribution of the stock.
Total shipments for microwave ovens
are developed by considering the
demand from replacements for units in
stock that fail and the demand from new
installations in newly constructed
homes. DOE calculated shipments due
to replacements using the retirement
function developed for the LCC analysis
and historical data from AHAM. DOE
calculated shipments due to new
installations using estimates from the
microwave oven saturation rate in new
homes in RECS 2020 and projections of
new housing starts from AEO2022. See
are lacking. In general, one would expect a close
correspondence between shipments and sales.
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
chapter 9 of the final rule TSD for
details.
For this final rule analysis, DOE used
data from a market research report and
estimated the market share for built-in
and over-the-range convection
microwave ovens at 4 percent.36
DOE considers the impacts on
shipments from changes in product
purchase price and operating cost
associated with higher energy efficiency
levels using a price elasticity and an
efficiency elasticity. DOE employs a 0.2percent efficiency elasticity rate and a
price elasticity of ¥0.45 in its
shipments model.37 The market impact
is defined as the difference between the
product of price elasticity of demand
and the change in price due to a
standard level, and the product of the
efficiency elasticity and the change in
operating costs due to a standard level.
H. National Impact Analysis
The NIA assesses the NES and the
NPV from a national perspective of total
consumer costs and savings that would
be expected to result from new or
amended standards at specific efficiency
levels.38 (‘‘Consumer’’ in this context
refers to consumers of the product being
regulated.) DOE calculates the NES and
NPV for the potential standard levels
considered based on projections of
annual product shipments, along with
the annual energy consumption and
total installed cost data from the energy
use and LCC analyses. For the present
analysis, DOE projected the energy
savings, operating cost savings, product
costs, and NPV of consumer benefits
over the lifetime of microwave ovens
sold from 2026 through 2055.
DOE evaluates the impacts of new or
amended standards by comparing a case
without such standards with standardscase projections. The no-new-standards
case characterizes energy use and
consumer costs for each product class in
the absence of new or amended energy
conservation standards. For this
projection, DOE considers historical
trends in efficiency and various forces
that are likely to affect the mix of
efficiencies over time. DOE compares
the no-new-standards case with
projections characterizing the market for
each product class if DOE adopted new
or amended standards at specific energy
efficiency levels (i.e., the TSLs or
standards cases) for that class. For the
standards cases, DOE considers how a
given standard would likely affect the
market shares of products with
efficiencies greater than the standard.
DOE uses a spreadsheet model to
calculate the energy savings and the
national consumer costs and savings
from each TSL. Interested parties can
review DOE’s analyses by changing
various input quantities within the
spreadsheet. The NIA spreadsheet
model uses typical values (as opposed
to probability distributions) as inputs.
Table IV.7 summarizes the inputs and
methods DOE used for the NIA analysis
for the final rule. Discussion of these
inputs and methods follows the table.
See chapter 10 of the final rule TSD for
further details.
TABLE IV.7—SUMMARY OF INPUTS AND METHODS FOR THE NATIONAL IMPACT ANALYSIS
Inputs
Method
Shipments ...........................................................
Compliance Date of Standard ............................
Efficiency Trends ................................................
Annual Energy Consumption per Unit ................
Total Installed Cost per Unit ...............................
Annual Energy Cost per Unit ..............................
Annual shipments from shipments model.
2026.
Standards cases: ‘‘Roll up’’ equipment to meet potential efficiency level.
Annual weighted-average values are a function of energy use at each TSL.
Annual weighted-average values are a function of cost at each TSL.
Annual weighted-average values as a function of the annual energy consumption per unit and
energy prices.
Annual values do not change with efficiency level.
AEO2022 projections (to 2050) and extrapolation thereafter.
A time-series conversion factor based on AEO2022.
Three and seven percent.
2023.
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Repair and Maintenance Cost per Unit ..............
Energy Price Trends ...........................................
Energy Site-to-Primary and FFC Conversion .....
Discount Rate .....................................................
Present Year .......................................................
1. Product Efficiency Trends
A key component of the NIA is the
trend in energy efficiency projected for
the no-new-standards case and each of
the standards cases. Section IV.F.8 of
this document describes how DOE
developed an energy efficiency
distribution for the no-new-standards
case (which yields a shipment-weighted
average efficiency) for each of the
considered product classes for the year
of anticipated compliance with an
amended or new standard. To project
the trend in efficiency absent amended
standards for microwave ovens over the
entire shipments projection period, DOE
used the shipments-weighted standby
power (‘‘SWSP’’) as a starting point.
DOE assumed that the shipmentweighted efficiency would not increase
annually for the microwave oven
product classes. The approach is further
described in chapter 10 of the final rule
TSD.
For the standards cases, DOE used a
‘‘roll-up’’ scenario to establish the
shipment-weighted efficiency for the
year that standards are assumed to
become effective (2026). In this
scenario, the market shares of products
in the no-new-standards case that do not
meet the standard under consideration
would ‘‘roll up’’ to meet the new
standard level, and the market share of
products above the standard would
remain unchanged.
36 Euromonitor International. 2021. Air treatment
products in the U.S. December.
37 Fujita, K. (2015) Estimating Price Elasticity
using Market-Level Appliance Data. Lawrence
Berkeley National Laboratory, LBNL–188289.
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2. National Energy Savings
The national energy savings analysis
involves a comparison of national
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energy consumption of the considered
products between each TSL and the case
with no new or amended energy
conservation standards. DOE calculated
the national energy consumption by
multiplying the number of units (stock)
of each product (by vintage or age) by
the unit energy consumption (also by
vintage). DOE calculated annual NES
based on the difference in national
energy consumption for the no-newstandards case and for each higher
efficiency standard case. DOE estimated
energy consumption and savings based
on site energy and converted the
electricity consumption and savings to
primary energy (i.e., the energy
consumed by power plants to generate
site electricity) using annual conversion
factors derived from AEO2022.
38 The
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Cumulative energy savings are the sum
of the NES for each year over the
timeframe of the analysis.
Use of higher-efficiency products is
sometimes associated with a direct
rebound effect, which refers to an
increase in utilization of the product
due to the increase in efficiency. DOE
did not find any data on the rebound
effect specific to microwave ovens;
therefore, no rebound was applied.
In 2011, in response to the
recommendations of a committee on
‘‘Point-of-Use and Full-Fuel-Cycle
Measurement Approaches to Energy
Efficiency Standards’’ appointed by the
National Academy of Sciences, DOE
announced its intention to use FFC
measures of energy use and greenhouse
gas and other emissions in the national
impact analyses and emissions analyses
included in future energy conservation
standards rulemakings. 76 FR 51281
(Aug. 18, 2011). After evaluating the
approaches discussed in the August 18,
2011 notice, DOE published a statement
of amended policy in which DOE
explained its determination that EIA’s
National Energy Modeling System
(‘‘NEMS’’) is the most appropriate tool
for its FFC analysis and its intention to
use NEMS for that purpose. 77 FR 49701
(Aug. 17, 2012). NEMS is a public
domain, multi-sector, partial
equilibrium model of the U.S. energy
sector 39 that EIA uses to prepare its
Annual Energy Outlook. The FFC factors
incorporate losses in production and
delivery in the case of natural gas
(including fugitive emissions) and
additional energy used to produce and
deliver the various fuels used by power
plants. The approach used for deriving
FFC measures of energy use and
emissions is described in appendix 10B
of the final rule TSD.
3. Net Present Value Analysis
The inputs for determining the NPV
of the total costs and benefits
experienced by consumers are (1) total
annual installed cost, (2) total annual
operating costs (energy costs and repair
and maintenance costs), and (3) a
discount factor to calculate the present
value of costs and savings. DOE
calculates net savings each year as the
difference between the no-newstandards case and each standards case
in terms of total savings in operating
costs versus total increases in installed
costs. DOE calculates operating cost
savings over the lifetime of each product
shipped during the projection period.
39 For more information on NEMS, refer to The
National Energy Modeling System: An Overview
2009, DOE/EIA–0581(2009), October 2009.
Available at www.eia.gov/forecasts/aeo/index.cfm
(last accessed December 13, 2022).
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As discussed in section IV.F.1 of this
document, DOE developed microwave
oven price trends based on historical
PPI data. DOE applied the same trends
to project prices for each product class
at each considered efficiency level. By
2055, which is the end date of the
projection period, the average
microwave oven price is projected to
drop 11 percent relative to 2021. DOE’s
projection of product prices is described
in appendix 10C of the final rule TSD.
To evaluate the effect of uncertainty
regarding the price trend estimates, DOE
investigated the impact of different
product price projections on the
consumer NPV for the considered TSLs
for microwave ovens. In addition to the
default price trend, DOE considered two
product price sensitivity cases: (1) a
high price decline case based on
‘‘electric household cooking products’’
PPI series from 1993 to 2021 and (2) a
low price decline case based on the
same PPI series from 1972 to 1992. The
derivation of these price trends and the
results of these sensitivity cases are
described in appendix 10C of the final
rule TSD.
The energy cost savings are calculated
using the estimated energy savings in
each year and the projected price of the
appropriate form of energy. To estimate
energy prices in future years, DOE
multiplied the average regional energy
prices by the projection of annual
national-average residential energy price
changes in the Reference case from
AEO2022, which has an end year of
2050. To estimate price trends after
2050, the 2046–2050 average was used
for all years. As part of the NIA, DOE
also analyzed scenarios that used inputs
from variants of the AEO2022 Reference
case that have lower and higher
economic growth. Those cases have
lower and higher energy price trends
compared to the Reference case. NIA
results based on these cases are
presented in appendix 10C of the final
rule TSD.
In considering the consumer welfare
gained due to the direct rebound effect,
DOE accounted for change in consumer
surplus attributed to additional cooling
from the purchase of a more efficient
unit. Overall consumer welfare is
generally understood to be enhanced
from rebound. The net consumer impact
of the rebound effect is included in the
calculation of operating cost savings in
the consumer NPV results. See
appendix 10F of the final rule TSD for
details on DOE’s treatment of the
monetary valuation of the rebound
effect.
In calculating the NPV, DOE
multiplies the net savings in future
years by a discount factor to determine
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their present value. For this final rule,
DOE estimated the NPV of consumer
benefits using both a 3-percent and a 7percent real discount rate. DOE uses
these discount rates in accordance with
guidance provided by the Office of
Management and Budget (‘‘OMB’’) to
Federal agencies on the development of
regulatory analysis.40 The discount rates
for the determination of NPV are in
contrast to the discount rates used in the
LCC analysis, which are designed to
reflect a consumer’s perspective. The 7percent real value is an estimate of the
average before-tax rate of return to
private capital in the U.S. economy. The
3-percent real value represents the
‘‘social rate of time preference,’’ which
is the rate at which society discounts
future consumption flows to their
present value.
I. Consumer Subgroup Analysis
In analyzing the potential impact of
new or amended energy conservation
standards on consumers, DOE evaluates
the impact on identifiable subgroups of
consumers that may be
disproportionately affected by a new or
amended national standard. The
purpose of a subgroup analysis is to
determine the extent of any such
disproportional impacts. DOE evaluates
impacts on particular subgroups of
consumers by analyzing the LCC
impacts and PBP for those particular
consumers from alternative standard
levels. For this final rule, DOE analyzed
the impacts of the considered standard
levels on two subgroups: (1) low-income
households and (2) senior-only
households. The analysis used subsets
of the RECS 2020 sample composed of
households that meet the criteria for the
considered subgroups. DOE used the
LCC and PBP spreadsheet model to
estimate the impacts of the considered
efficiency levels on these subgroups.
Chapter 11 of the final rule TSD
describes the consumer subgroup
analysis.
J. Manufacturer Impact Analysis
1. Overview
DOE performed an MIA to estimate
the financial impacts of amended energy
conservation standards on
manufacturers of microwave ovens and
to estimate the potential impacts of such
standards on employment and
manufacturing capacity. The MIA has
both quantitative and qualitative aspects
and includes analyses of projected
40 United States Office of Management and
Budget. Circular A–4: Regulatory Analysis.
September 17, 2003. Section E. Available at
obamawhitehouse.archives.gov/omb/circulars_
a004_a-4/ (last accessed December 13, 2022).
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industry cash flows, the INPV,
investments in research and
development (‘‘R&D’’) and
manufacturing capital, and domestic
manufacturing employment.
Additionally, the MIA seeks to
determine how amended energy
conservation standards might affect
manufacturing employment, capacity,
and competition, as well as how
standards contribute to overall
regulatory burden. Finally, the MIA
serves to identify any disproportionate
impacts on manufacturer subgroups,
including small business manufacturers.
The quantitative part of the MIA
primarily relies on the Government
Regulatory Impact Model (‘‘GRIM’’), an
industry cash flow model with inputs
specific to this rulemaking. The key
GRIM inputs include data on the
industry cost structure, unit production
costs, product shipments, manufacturer
markups, and investments in R&D and
manufacturing capital required to
produce compliant products. The key
GRIM outputs are the INPV, which is
the sum of industry annual cash flows
over the analysis period, discounted
using the industry-weighted average
cost of capital, and the impact to
domestic manufacturing employment.
The model uses standard accounting
principles to estimate the impacts of
more-stringent energy conservation
standards on a given industry by
comparing changes in INPV and
domestic manufacturing employment
between a no-new-standards case and
the various standards cases (TSLs). To
capture the uncertainty relating to
manufacturer pricing strategies
following amended standards, the GRIM
estimates a range of possible impacts
under different markup scenarios.
The qualitative part of the MIA
addresses manufacturer characteristics
and market trends. Specifically, the MIA
considers such factors as a potential
standard’s impact on manufacturing
capacity, competition within the
industry, the cumulative impact of other
DOE and non-DOE regulations, and
impacts on manufacturer subgroups.
The complete MIA is outlined in
chapter 12 of the final rule TSD.
DOE prepared a profile of the
microwave oven manufacturing
industry based on the market and
technology assessment, current
information from DOE’s CCD, and
information from the June 2013 Final
Rule. (78 FR 36316) This included a topdown analysis of microwave oven
manufacturers that DOE used to derive
preliminary financial inputs for the
GRIM (e.g., revenues; materials, labor,
overhead, and depreciation expenses;
SG&A expenses; and R&D expenses).
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Additionally, DOE prepared a
framework industry cash-flow analysis
to quantify the potential impacts of
amended energy conservation
standards. The GRIM uses several
factors to determine a series of annual
cash flows starting with the
announcement of the standard and
extending over a 30-year period
following the compliance date of the
standard. These factors include annual
expected revenues, costs of sales, SG&A
and R&D expenses, taxes, and capital
expenditures. In general, energy
conservation standards can affect
manufacturer cash flow in three distinct
ways: (1) creating a need for increased
investment, (2) raising production costs
per unit, and (3) altering revenue due to
higher per-unit prices and changes in
sales volumes.
DOE also evaluated subgroups of
manufacturers that may be
disproportionately impacted by
amended standards or that may not be
accurately represented by the average
cost assumptions used to develop the
industry cash flow analysis. Such
manufacturer subgroups may include
small business manufacturers, lowvolume manufacturers, niche players,
and/or manufacturers exhibiting a cost
structure that largely differs from the
industry average. DOE identified one
subgroup for a separate impact analysis:
small business manufacturers. The
small business subgroup is discussed in
section VI.B of this document, ‘‘Review
under the Regulatory Flexibility Act’’
and in chapter 12 of the final rule TSD.
2. Government Regulatory Impact Model
and Key Inputs
DOE uses the GRIM to quantify the
changes in cash flow due to amended
standards that result in a higher or
lower industry value. The GRIM uses a
standard, annual discounted cash-flow
analysis that incorporates manufacturer
costs, markups, shipments, and industry
financial information as inputs. The
GRIM models changes in costs,
distribution of shipments, investments,
and manufacturer margins that could
result from amended energy
conservation standards. The GRIM
spreadsheet uses the inputs to arrive at
a series of annual cash flows, beginning
in 2023 (the base year of the analysis)
and continuing to 2055. DOE calculated
INPVs by summing the stream of annual
discounted cash flows during this
period. For manufacturers of microwave
ovens, DOE used a real discount rate of
8.5 percent, which was the same real
discount rate used in the June 2013
Final Rule and that was verified during
manufacturer interviews for that
rulemakings analysis.
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The GRIM calculates cash flows using
standard accounting principles and
compares changes in INPV between the
no-new-standards case and each
standards case. The difference in INPV
between the no-new-standards case and
a standards case represents the financial
impact of the amended energy
conservation standards on
manufacturers. As discussed previously,
DOE developed critical GRIM inputs
using a number of sources, including
publicly available data, results of the
engineering analysis, and information
used in the June 2013 Final Rule. The
GRIM results are presented in section
V.B.2 of this document. Additional
details about the GRIM, the discount
rate, and other financial parameters can
be found in chapter 12 of the final rule
TSD.
a. Manufacturer Production Costs
Manufacturing more efficient
products is typically more expensive
than manufacturing baseline products
due to the use of more complex
components, which are typically more
costly than baseline components. The
changes in the MPCs of covered
products can affect the revenues, gross
margins, and cash flow of the industry.
As previously stated in the engineering
analysis in section IV.C.3 of this
document, DOE estimated an
incremental MPC of $0 at all efficiency
levels, compared to the baseline MPC.
DOE did not make any changes to the
MPCs from the August 2022 SNOPR.
b. Shipments Projections
The GRIM estimates manufacturer
revenues based on total unit shipment
projections and the distribution of those
shipments by efficiency level. Changes
in sales volumes and efficiency mix
over time can significantly affect
manufacturer finances. For this analysis,
the GRIM uses the NIA’s annual
shipment projections derived from the
shipments analysis from 2023 (the base
year) to 2055 (the end year of the
analysis period). See chapter 9 of the
final rule TSD for additional details.
DOE slightly updated the shipments
analysis from the August 2022 SNOPR.
c. Product and Capital Conversion Costs
Amended energy conservation
standards could cause manufacturers to
incur conversion costs to bring their
production facilities and product
designs into compliance. DOE evaluated
the level of conversion-related
expenditures that would be needed to
comply with each considered efficiency
level in each product class. For the MIA,
DOE classified these conversion costs
into two major groups: (1) product
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conversion costs and (2) capital
conversion costs. Product conversion
costs are investments in research,
development, testing, marketing, and
other non-capitalized costs necessary to
make product designs comply with
amended energy conservation
standards. Capital conversion costs are
investments in property, plant, and
equipment necessary to adapt or change
existing production facilities such that
new compliant product designs can be
fabricated and assembled.
DOE used a bottom-up cost estimate
to arrive at a total industry conversion
cost at each efficiency level for both
product classes. First, DOE estimated
the investments manufacturers are
likely to incur in redesigning a single
microwave oven control board to be able
to meet the analyzed energy
conservation standards. These per-board
conversion costs were based on
manufacturer interviews and include
both per-board capital conversion costs
(e.g., investments in machinery and
tooling) as well as product conversion
costs (e.g., investments in R&D and
testing). Based on manufacturer
feedback, DOE assigned a smaller level
of investment necessary to achieve
lower efficiency levels and a larger level
of investment to achieve higher
efficiency levels.
Next, based on engineering teardowns
and market research, DOE estimated the
total number of unique control boards
used across all covered microwave
ovens. DOE used the percentage of
unique microwave oven models for each
product class that were certified in
DOE’s publicly available CCD to
estimate the number of unique control
boards for each product class. Then
DOE used the efficiency distribution
from the shipments analysis to estimate
the number, for each product class, of
unique control boards specific to each
efficiency level. Once DOE estimated
the number of unique control boards,
DOE used the per-board redesign costs
specific to achieve each analyzed
efficiency level in order to arrive at the
total industry conversion costs.
DOE did not make any changes to the
capital and product conversion costs
estimates used in the August 2022
SNOPR. In general, DOE assumes all
conversion-related investments occur
between the year of publication of the
final rule and the year by which
manufacturers must comply with the
amended standards. The conversion
cost figures used in the GRIM can be
found in section V.B.2 of this document.
See chapter 12 of the final rule TSD for
additional information on the estimated
capital and product conversion costs.
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d. Markup Scenarios
MSPs include direct manufacturing
production costs (i.e., labor, materials,
and overhead estimated in DOE’s MPCs)
and all non-production costs (i.e.,
SG&A, R&D, and interest), along with
profit. To calculate the MSPs in the
GRIM, DOE applied non-production
cost markups to the MPCs estimated in
the engineering analysis for each
product class and efficiency level.
Modifying these markups in the
standards case yields different sets of
impacts on manufacturers. As in the
August 2022 SNOPR, DOE used a
manufacturer markup of 1.298 for both
product classes in the no-new-standards
case. (87 FR 52282, 52296)
For the MIA, DOE modeled two
standards-case markup scenarios to
represent uncertainty regarding the
potential impacts on prices and
profitability for manufacturers following
the implementation of amended energy
conservation standards: (1) a conversion
cost recovery scenario; and (2) a
constant price scenario. These scenarios
lead to different manufacturer markup
values at each TSL that, when applied
to the MPCs, result in varying revenue
and cash flow impacts.
Under the conversion cost recovery
scenario, DOE modeled a scenario in
which manufacturers increase their
manufacturer markups in response to
amended energy conservation
standards. Because DOE’s engineering
analysis assumed there were no
increases in the MPCs at higher
efficiency levels compared to the
baseline MPCs, and that microwave
oven manufacturers would incur
conversion costs to redesign noncompliant models, DOE modeled a
manufacturer markup scenario in which
microwave oven manufacturers attempt
to recover these investments through an
increase in their manufacturer markup.
Therefore, in the standards cases, the
manufacturer markup of models that
would need to be re-designed is a value
larger than the 1.298 manufacturer
markup used in the no-new-standards
case. DOE calibrated these manufacturer
markups for each product class at each
efficiency level to cause manufacturer
INPV in the standards cases to be equal
to the INPV in the no-new-standards
case. Because manufacturer markups
used in this scenario are calculated
using the shipments analysis as inputs
and the shipments analysis was updated
from the August 2022 SNOPR to this
final rule analysis, the calibrated
manufacturer markups used in the
conversion cost recovery scenario for
this final rule analysis are slightly
different than those values that were
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calculated in the August 2022 SNOPR.
However, the methodology used to
calculate these manufacturer markup
values are the same as those used in the
August 2022 SNOPR.
The conversion cost recovery scenario
represents the upper-bound of
manufacturer profitability, as
microwave oven manufacturers are no
worse off, as measured by INPV, with
energy conservation standards than in
the no-new-standards case (i.e., if DOE
did not amend energy conservation
standards).
Under the constant price scenario,
DOE applied the same manufacturer
markup, 1.298, for all efficiency levels
in the no-new-standards case and the
standards cases. Because DOE’s
engineering analysis assumed there
were no increases in the MPCs at higher
efficiency levels and that microwave
oven manufacturers would incur
conversion costs to redesign noncompliant models, microwave oven
manufacturers do not earn any
additional revenue in the standards
cases than in the no-new-standards case,
despite incurring conversion costs to
redesign non-compliant microwave
oven models. The constant price
scenario represents the lower-bound of
manufacturer profitability, as
microwave oven manufacturers incur
conversion costs but do not receive any
additional revenue from these redesign
efforts. The manufacturer markups in
the constant price scenario are the same
as those used in the August 2022
SNOPR.
A comparison of industry financial
impacts under the two markup
scenarios is presented in section V.B.2.a
of this document.
3. Discussion of MIA Comments
AHAM commented on the August
2022 SNOPR that DOE correctly decided
to incorporate conversion costs into the
LCC analysis as part of the August 2022
SNOPR. However, AHAM stated that
DOE should amortize these conversion
costs over a 6-year period instead of
amortizing these conversion costs over a
30-year period, which is what was done
in the August 2022 SNOPR. (AHAM,
No. 28 at p. 11)
In the SNOPR analysis, DOE used the
GRIM to calculate a higher manufacturer
markup in the standards cases that
results in an equivalent manufacturer
INPV in the standards cases compared
to the no-new-standards case. The
conversion cost recovery scenario is the
manufacturer markup scenario
incorporated into all downstream
analyses, including the LCC analysis, in
the standards cases. In this scenario,
manufacturers make investments, both
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in machinery and tooling (capital
conversion costs) and in redesign and
testing (product conversion costs), prior
to the compliance date of energy
conservation standards. After
compliance with energy conservation
standards manufacturers increase their
manufacturer markup, thereby
increasing revenue and free cash flow
for the remainder of the 30-year analysis
period. Amortizing these conversion
costs over a 6-year period would create
a scenario where manufacturer INPV
increases in all analyzed TSLs in the
standards cases compared to the nonew-standards case. DOE maintains that
amortizing these conversion costs over
the 30-year analysis period reflects an
accurate upper-bound to industry
profitability in the standards cases as
manufacturers do not lose INPV in the
conversion cost recovery scenario in the
standards cases compared to the nonew-standards case.
K. Emissions Analysis
The emissions analysis consists of
two components. The first component
estimates the effect of potential energy
conservation standards on power sector
and site (where applicable) combustion
emissions of CO2, NOX, SO2, and Hg.
The second component estimates the
impacts of potential standards on
emissions of two additional greenhouse
gases, CH4 and N2O, as well as the
reductions in emissions of other gases
due to ‘‘upstream’’ activities in the fuel
production chain. These upstream
activities comprise extraction,
processing, and transporting fuels to the
site of combustion.
The analysis of electric power sector
emissions of CO2, NOX, SO2, and Hg
uses emissions intended to represent the
marginal impacts of the change in
electricity consumption associated with
amended or new standards. The
methodology is based on results
published for the AEO, including a set
of side cases that implement a variety of
efficiency-related policies. The
methodology is described in appendix
13A in the final rule TSD. The analysis
presented in this final rule uses
projections from AEO2022. Power sector
emissions of CH4 and N2O from fuel
combustion are estimated using
Emission Factors for Greenhouse Gas
Inventories published by the
Environmental Protection Agency
(EPA).41
FFC upstream emissions, which
include emissions from fuel combustion
during extraction, processing, and
41 Available at www.epa.gov/sites/production/
files/2021-04/documents/emission-factors_
apr2021.pdf (last accessed December 13, 2022).
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transportation of fuels, and ‘‘fugitive’’
emissions (direct leakage to the
atmosphere) of CH4 and CO2, are
estimated based on the methodology
described in chapter 15 of the final rule
TSD.
The emissions intensity factors are
expressed in terms of physical units per
MWh or MMBtu of site energy savings.
For power sector emissions, specific
emissions intensity factors are
calculated by sector and end use. Total
emissions reductions are estimated
using the energy savings calculated in
the national impact analysis.
1. Air Quality Regulations Incorporated
in DOE’s Analysis
DOE’s no-new-standards case for the
electric power sector reflects the AEO,
which incorporates the projected
impacts of existing air quality
regulations on emissions. AEO2022
generally represents current legislation
and environmental regulations,
including recent government actions,
that were in place at the time of
preparation of AEO2022, including the
emissions control programs discussed in
the following paragraphs.42
SO2 emissions from affected electric
generating units (‘‘EGUs’’) are subject to
nationwide and regional emissions capand-trade programs. Title IV of the
Clean Air Act sets an annual emissions
cap on SO2 for affected EGUs in the 48
contiguous States and the District of
Columbia (‘‘DC’’). (42 U.S.C. 7651 et
seq.) SO2 emissions from numerous
States in the eastern half of the United
States are also limited under the CrossState Air Pollution Rule (‘‘CSAPR’’). 76
FR 48208 (Aug. 8, 2011). CSAPR
requires these States to reduce certain
emissions, including annual SO2
emissions, and went into effect as of
January 1, 2015 and has been
subsequently updated.43 AEO2022
42 For further information, see the Assumptions to
AEO2022 report that sets forth the major
assumptions used to generate the projections in the
Annual Energy Outlook. Available at www.eia.gov/
outlooks/aeo/assumptions/ (last accessed December
13, 2022).
43 CSAPR requires States to address annual
emissions of SO2 and NOX, precursors to the
formation of fine particulate matter (‘‘PM2.5’’)
pollution, in order to address the interstate
transport of pollution with respect to the 1997 and
2006 PM2.5 National Ambient Air Quality Standards
(‘‘NAAQS’’). CSAPR also requires certain States to
address the ozone season (May-September)
emissions of NOX, a precursor to the formation of
ozone pollution, in order to address the interstate
transport of ozone pollution with respect to the
1997 ozone NAAQS. 76 FR 48208 (Aug. 8, 2011).
EPA subsequently issued a supplemental rule that
included an additional five States in the CSAPR
ozone season program; 76 FR 80760 (Dec. 27, 2011)
(Supplemental Rule). In 2021, EPA issued the
Revised CSAPR Update for the 2008 Ozone NAAQs
(Revised CSAPR Update) promulgating EGU NOX
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incorporates implementation of CSAPR,
including the Revised CSAPR Update
issued in April 2021. 86 FR 23054.
Compliance with CSAPR is flexible
among EGUs and is enforced through
the use of tradable emissions
allowances. Under existing EPA
regulations, for States subject to SO2
emissions limits under CSAPR, any
excess SO2 emissions allowances
resulting from the lower electricity
demand caused by the adoption of an
efficiency standard could be used to
permit offsetting increases in SO2
emissions by another regulated EGU.
Beginning in 2016, SO2 emissions
began to fall as a result of the Mercury
and Air Toxics Standards (‘‘MATS’’) for
power plants. 77 FR 9304 (Feb. 16,
2012). In the MATS final rule, EPA
established a standard for hydrogen
chloride as a surrogate for acid gas
hazardous air pollutants (‘‘HAP’’), and
also established a standard for SO2 (a
non-HAP acid gas) as an alternative
equivalent surrogate standard for acid
gas HAP. The same controls are used to
reduce HAP and non-HAP acid gas;
thus, SO2 emissions are being reduced
as a result of the control technologies
installed on coal-fired power plants to
comply with the MATS requirements
for acid gas. Because of the emissions
reductions under the MATS, it is
unlikely that excess SO2 emissions
allowances resulting from the lower
electricity demand would be needed or
used to permit offsetting increases in
SO2 emissions by another regulated
EGU. Therefore, energy conservation
standards that decrease electricity
generation will generally reduce SO2
emissions. DOE estimated SO2
emissions reduction using emissions
factors based on AEO2022.
CSAPR also established limits on NOX
emissions for numerous States in the
eastern half of the United States. Energy
conservation standards would have
little effect on NOX emissions in those
States covered by CSAPR emissions
limits if excess NOX emissions
allowances resulting from the lower
electricity demand could be used to
permit offsetting increases in NOX
emissions from other EGUs. In such
cases, NOX emissions would remain
near the limit even if electricity
generation goes down. A different case
could possibly result, depending on the
configuration of the power sector in the
different regions and the need for
allowances, such that NOX emissions
might not remain at the limit in the case
of lower electricity demand. In this case,
energy conservation standards might
ozone season emission budgets for 12 states. 86 FR
23054, 23059 (Apr. 30, 2021).
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reduce NOX emissions in covered
States. Despite this possibility, DOE has
chosen to be conservative in its analysis
and has maintained the assumption that
standards will not reduce NOX
emissions in States covered by CSAPR.
Standards would be expected to reduce
NOX emissions in the States not covered
by CSAPR. DOE used AEO2022 data to
derive NOX emissions factors for the
group of States not covered by CSAPR.
The MATS limit mercury emissions
from power plants, but they do not
include emissions caps and, as such,
DOE’s energy conservation standards
would be expected to slightly reduce Hg
emissions. DOE estimated mercury
emissions reduction using emissions
factors based on AEO2022, which
incorporates the MATS.
L. Monetizing Emissions Impacts
As part of the development of this
final rule, for the purpose of complying
with the requirements of Executive
Order 12866, DOE considered the
estimated monetary benefits from the
reduced emissions of CO2, CH4, N2O,
NOX, and SO2 that are expected to result
from each of the TSLs considered. In
order to make this calculation analogous
to the calculation of the NPV of
consumer benefit, DOE considered the
reduced emissions expected to result
over the lifetime of products shipped in
the projection period for each TSL. This
section summarizes the basis for the
values used for monetizing the
emissions benefits and presents the
values considered in this final rule.
On March 16, 2022, the Fifth Circuit
Court of Appeals (No. 22–30087)
granted the Federal government’s
emergency motion for stay pending
appeal of the February 11, 2022,
preliminary injunction issued in
Louisiana v. Biden, No. 21–cv–1074–
JDC–KK (W.D. La.). As a result of the
Fifth Circuit’s order, the preliminary
injunction is no longer in effect,
pending resolution of the Federal
government’s appeal of that injunction
or a further court order. Among other
things, the preliminary injunction
enjoined the defendants in that case
from ‘‘adopting, employing, treating as
binding, or relying upon’’ the interim
estimates of the social cost of
greenhouse gases—which were issued
by the Interagency Working Group on
the Social Cost of Greenhouse Gases on
February 26, 2021—to monetize the
benefits of reducing greenhouse gas
emissions. As reflected in this rule, DOE
has reverted to its approach prior to the
injunction and presents monetized
benefits where appropriate and
permissible under law. DOE requests
comment on how to address the climate
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benefits and other non-monetized
effects of the proposal.
AHAM commented that DOE should
not use the social cost of carbon and
other monetization of emissions
reductions benefits in its analysis of the
factors EPCA requires DOE to balance to
determine the appropriate standard.
AHAM commented that while it may be
acceptable for DOE to continue its
current practice of examining the social
cost of carbon and monetization of other
emissions reductions benefits as
informational so long as the underlying
interagency analysis is transparent and
vigorous, the monetization analysis
should not impact the TSLs DOE selects
as a new or amended standard. (AHAM,
No. 28 at p. 13)
As stated in section III.F.1.f of this
document, DOE maintains that
environmental and public health
benefits associated with the more
efficient use of energy, including those
connected to global climate change, are
important to take into account when
considering the need for national energy
conservation, which is one of the factors
that EPCA requires DOE to evaluate in
determining whether a potential energy
conservation standard is economically
justified. See 42 U.S.C.
6295(o)(2)(B)(i)(VI). In addition,
Executive Order 13563, which was reaffirmed on January 21, 2021, stated that
each agency must, among other things:
‘‘select, in choosing among alternative
regulatory approaches, those approaches
that maximize net benefits (including
potential economic, environmental,
public health and safety, and other
advantages; distributive impacts; and
equity).’’ For these reasons, DOE
includes monetized emissions
reductions in its evaluation of potential
standard levels. As previously stated,
however, DOE would reach the same
conclusion presented in this final
rulemaking in the absence of the social
cost of greenhouse gases.
1. Monetization of Greenhouse Gas
Emissions
DOE estimates the monetized benefits
of the reductions in emissions of CO2,
CH4, and N2O by using a measure of the
social cost of each pollutant (e.g., SC–
CO2). These estimates represent the
monetary value of the net harm to
society associated with a marginal
increase in emissions of these pollutants
in a given year, or the benefit of
avoiding that increase. These estimates
are intended to include (but are not
limited to) climate-change-related
changes in net agricultural productivity,
human health, property damages from
increased flood risk, disruption of
energy systems, risk of conflict,
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39937
environmental migration, and the value
of ecosystem services.
DOE exercises its own judgment in
presenting monetized climate benefits
as recommended by applicable
Executive orders, and DOE would reach
the same conclusion presented in this
final rulemaking in the absence of the
social cost of greenhouse gases. That is,
the social costs of greenhouse gases,
whether measured using the February
2021 interim estimates presented by the
Interagency Working Group on the
Social Cost of Greenhouse Gases (IWG)
or by another means, did not affect the
rule ultimately proposed by DOE.
DOE estimated the global social
benefits of CO2, CH4, and N2O
reductions (i.e., SC–GHGs) using the
estimates presented in the Technical
Support Document: Social Cost of
Carbon, Methane, and Nitrous Oxide
Interim Estimates under Executive
Order 13990, published in February
2021 by the IWG. The SC–GHGs is the
monetary value of the net harm to
society associated with a marginal
increase in emissions in a given year, or
the benefit of avoiding that increase. In
principle, SC–GHGs includes the value
of all climate change impacts, including
(but not limited to) changes in net
agricultural productivity, human health
effects, property damage from increased
flood risk and natural disasters,
disruption of energy systems, risk of
conflict, environmental migration, and
the value of ecosystem services. The
SC–GHGs therefore reflects the societal
value of reducing emissions of the gas
in question by one metric ton. The SC–
GHGs is the theoretically appropriate
value to use in conducting benefit-cost
analyses of policies that affect CO2, N2O,
and CH4 emissions. As a member of the
IWG involved in the development of the
February 2021 SC–GHG TSD, DOE
agrees that the interim SC–GHG
estimates represent the most appropriate
estimate of the SC–GHG until revised
estimates have been developed
reflecting the latest, peer-reviewed
science.
The SC–GHGs estimates presented
here were developed over many years
using a transparent process, peerreviewed methodologies, the best
science available at the time of that
process, and with input from the public.
Specifically, in 2009, the IWG, which
included DOE and other executive
branch agencies and offices, was
established to ensure that agencies were
using the best available science and to
promote consistency in the social cost of
carbon (SC–CO2) values used across
agencies. The IWG published SC–CO2
estimates in 2010 that were developed
from an ensemble of three widely cited
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integrated assessment models (IAMs)
that estimate global climate damages
using highly aggregated representations
of climate processes and the global
economy combined into a single
modeling framework. The three IAMs
were run using a common set of input
assumptions in each model for future
population, economic, and CO2
emissions growth, as well as
equilibrium climate sensitivity—a
measure of the globally averaged
temperature response to increased
atmospheric CO2 concentrations. These
estimates were updated in 2013 based
on new versions of each IAM. In August
2016, the IWG published estimates of
the social cost of methane (SC–CH4) and
nitrous oxide (SC–N2O) using
methodologies that are consistent with
the methodology underlying the SC–
CO2 estimates. The modeling approach
that extends the IWG SC–CO2
methodology to non-CO2 GHGs has
undergone multiple stages of peer
review. The SC–CH4 and SC–N2O
estimates were developed by Marten et
al.44 and underwent a standard doubleblind peer review process prior to
journal publication. In 2015, as part of
the response to public comments
received to a 2013 solicitation for
comments on the SC–CO2 estimates, the
IWG announced a National Academies
of Sciences, Engineering, and Medicine
review of the SC–CO2 estimates to offer
advice on how to approach future
updates to ensure that the estimates
continue to reflect the best available
science and methodologies. In January
2017, the National Academies released
their final report, Valuing Climate
Damages: Updating Estimation of the
Social Cost of Carbon Dioxide, and
recommended specific criteria for future
updates to the SC–CO2 estimates, a
modeling framework to satisfy the
specified criteria, and both near-term
updates and longer-term research needs
pertaining to various components of the
estimation process.45 Shortly thereafter,
in March 2017, President Trump issued
Executive Order 13783, which
disbanded the IWG, withdrew the
previous TSDs, and directed agencies to
ensure SC–CO2 estimates used in
regulatory analyses are consistent with
the guidance contained in OMB’s
Circular A–4, ‘‘including with respect to
44 Marten, A. L., E. A. Kopits, C. W. Griffiths, S.
C. Newbold, and A. Wolverton. Incremental CH4
and N2O mitigation benefits consistent with the US
Government’s SC–CO2 estimates. Climate Policy.
2015. 15(2): pp. 272–298.
45 National Academies of Sciences, Engineering,
and Medicine. Valuing Climate Damages: Updating
Estimation of the Social Cost of Carbon Dioxide.
2017. The National Academies Press: Washington,
DC.
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the consideration of domestic versus
international impacts and the
consideration of appropriate discount
rates’’ (E.O. 13783, Section 5(c)).
Benefit-cost analyses following E.O.
13783 used SC–GHG estimates that
attempted to focus on the U.S.-specific
share of climate change damages as
estimated by the models and were
calculated using two discount rates
recommended by Circular A–4, 3
percent and 7 percent. All other
methodological decisions and model
versions used in SC–GHG calculations
remained the same as those used by the
IWG in 2010 and 2013, respectively.
On January 20, 2021, President Biden
issued Executive Order 13990, which reestablished the IWG and directed it to
ensure that the U.S. Government’s
estimates of the social cost of carbon
and other greenhouse gases reflect the
best available science and the
recommendations of the National
Academies (2017). The IWG was tasked
with first reviewing the SC–GHG
estimates currently used in Federal
analyses and publishing interim
estimates within 30 days of the E.O. that
reflect the full impact of GHG
emissions, including by taking global
damages into account. The interim SC–
GHG estimates published in February
2021 are used here to estimate the
climate benefits for this proposed
rulemaking. The E.O. instructs the IWG
to undertake a fuller update of the SC–
GHG estimates by January 2022 that
takes into consideration the advice of
the National Academies (2017) and
other recent scientific literature. The
February 2021 SC–GHG TSD provides a
complete discussion of the IWG’s initial
review conducted under E.O.13990. In
particular, the IWG found that the SC–
GHG estimates used under E.O. 13783
fail to reflect the full impact of GHG
emissions in multiple ways.
First, the IWG found that the SC–GHG
estimates used under E.O. 13783 fail to
fully capture many climate impacts that
affect the welfare of U.S. citizens and
residents, and those impacts are better
reflected by global measures of the SC–
GHG. Examples of omitted effects from
the E.O. 13783 estimates include: (1)
direct effects on U.S. citizens, assets,
and investments located abroad; (2)
supply chains;(3) U.S. military assets
and interests abroad; (4) tourism; and (5)
spillover pathways, such as economic
and political destabilization and global
migration, that can lead to adverse
impacts on U.S. national security,
public health, and humanitarian
concerns. In addition, assessing the
benefits of U.S. GHG mitigation
activities requires consideration of how
those actions may affect mitigation
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activities by other countries, as those
international mitigation actions will
provide a benefit to U.S. citizens and
residents by mitigating climate impacts
that affect U.S. citizens and residents. A
wide range of scientific and economic
experts have emphasized the issue of
reciprocity as support for considering
global damages of GHG emissions. If the
United States does not consider impacts
on other countries, it is difficult to
convince other countries to consider the
impacts of their emissions on the United
States The only way to achieve an
efficient allocation of resources for
emissions reduction on a global basis—
and so benefit the U.S. and its citizens—
is for all countries to base their policies
on global estimates of damages. As a
member of the IWG involved in the
development of the February 2021 SC–
GHG TSD, DOE agrees with this
assessment and, therefore, in this
proposed rule, DOE centers attention on
a global measure of SC–GHG. This
approach is the same as that taken in
DOE regulatory analyses from 2012
through 2016. A robust estimate of
climate damages that accrue only to U.S.
citizens and residents does not currently
exist in the literature. As explained in
the February 2021 SC–GHG TSD,
existing estimates are both incomplete
and underestimate total damages that
accrue to the citizens and residents of
the U.S. because they do not fully
capture the regional interactions and
spillovers discussed above, nor do they
include all of the important physical,
ecological, and economic impacts of
climate change recognized in the
literature. As noted in the February
2021 SC–GHG TSD, the IWG will
continue to review developments in the
literature, including more robust
methodologies for estimating a U.S.specific SC–GHG value and exploring
ways to better inform the public of the
full range of carbon impacts. As a
member of the IWG, DOE will continue
to follow developments in the literature
pertaining to this issue.
Second, the IWG found that the use of
the social rate of return on capital (7
percent under current OMB Circular A–
4 guidance) to discount the future
benefits of reducing GHG emissions
inappropriately underestimates the
impacts of climate change for the
purposes of estimating the SC–GHG.
Consistent with the findings of the
National Academies (2017) and the
economic literature, the IWG continued
to conclude that the consumption rate of
interest is the theoretically appropriate
discount rate in an intergenerational
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context 46 and recommended that
discount rate uncertainty and relevant
aspects of intergenerational ethical
considerations be accounted for in
selecting future discount rates.
Furthermore, the damage estimates
developed for use in the SC–GHG are
estimated in consumption-equivalent
terms, and so an application of OMB
Circular A–4’s guidance for regulatory
analysis would then use the
consumption discount rate to calculate
the SC–GHG. DOE agrees with this
assessment and will continue to follow
developments in the literature
pertaining to this issue. DOE also notes
that while OMB Circular A–4, as
published in 2003, recommends using 3
percent and 7 percent discount rates as
‘‘default’’ values, Circular A–4 also
reminds agencies that ‘‘different
regulations may call for different
emphases in the analysis, depending on
the nature and complexity of the
regulatory issues and the sensitivity of
the benefit and cost estimates to the key
assumptions.’’ On discounting, Circular
A–4 recognizes that ‘‘special ethical
considerations arise when comparing
benefits and costs across generations,’’
and Circular A–4 acknowledges that
analyses may appropriately ‘‘discount
future costs and consumption
benefits. . .at a lower rate than for
intragenerational analysis.’’ In the 2015
Response to Comments on the Social
Cost of Carbon for Regulatory Impact
Analysis, OMB, DOE, and the other IWG
members recognized that ‘‘Circular A–4
is a living document’’ and ‘‘the use of
7 percent is not considered appropriate
for intergenerational discounting. There
46 Interagency Working Group on Social Cost of
Carbon. Social Cost of Carbon for Regulatory Impact
Analysis under Executive Order 12866. 2010.
United States Government. Available at
www.epa.gov/sites/default/files/2016-12/
documents/scc_tsd_2010.pdf (last accessed April
15, 2022). Interagency Working Group on Social
Cost of Carbon. Technical Update of the Social Cost
of Carbon for Regulatory Impact Analysis Under
Executive Order 12866. 2013 Available at
www.federalregister.gov/documents/2013/11/26/
2013-28242/technical-support-document-technicalupdate-of-the-social-cost-of-carbon-for-regulatoryimpact (last accessed April 15, 2022). Interagency
Working Group on Social Cost of Greenhouse Gases,
United States Government. Technical Support
Document: Technical Update on the Social Cost of
Carbon for Regulatory Impact Analysis-Under
Executive Order 12866. August 2016. Available at
www.epa.gov/sites/default/files/2016-12/
documents/sc_co2_tsd_august_2016.pdf (last
accessed January 18, 2022). Interagency Working
Group on Social Cost of Greenhouse Gases, United
States Government. Addendum to Technical
Support Document on Social Cost of Carbon for
Regulatory Impact Analysis under Executive Order
12866: Application of the Methodology to Estimate
the Social Cost of Methane and the Social Cost of
Nitrous Oxide. August 2016. Available at
www.epa.gov/sites/default/files/2016-12/
documents/addendum_to_sc-ghg_tsd_august_
2016.pdf (last accessed January 18, 2022).
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is wide support for this view in the
academic literature, and it is recognized
in Circular A–4 itself.’’ Thus, DOE
concludes that a 7-percent discount rate
is not appropriate to apply to value the
social cost of greenhouse gases
presented in this analysis.
To calculate the present and
annualized values of climate benefits,
DOE uses the same discount rate as the
rate used to discount the value of
damages from future GHG emissions, for
internal consistency. That approach to
discounting follows the same approach
that the February 2021 SC–GHG TSD
recommends ‘‘to ensure internal
consistency—i.e., future damages from
climate change using the SC–GHG at 2.5
percent should be discounted to the
base year of the analysis using the same
2.5 percent rate.’’ DOE has also
consulted the National Academies’ 2017
recommendations on how SC–GHG
estimates can ‘‘be combined in RIAs
with other cost and benefits estimates
that may use different discount rates.’’
The National Academies reviewed
several options, including ‘‘presenting
all discount rate combinations of other
costs and benefits with [SC–GHG]
estimates.’’
As a member of the IWG involved in
the development of the February 2021
SC–GHG TSD, DOE agrees with the
above assessment and will continue to
follow developments in the literature
pertaining to this issue. While the IWG
is working to assess how best to
incorporate the latest peer-reviewed
science to develop an updated set of
SC–GHG estimates, it set the interim
estimates to be the most recent estimates
developed by the IWG prior to the group
being disbanded in 2017. The estimates
rely on the same models and
harmonized inputs and are calculated
using a range of discount rates. As
explained in the February 2021 SC–
GHG TSD, the IWG has recommended
that agencies revert to the same set of
four values drawn from the SC–GHG
distributions based on three discount
rates as were used in regulatory analyses
between 2010 and 2016 and were
subject to public comment. For each
discount rate, the IWG combined the
distributions across models and
socioeconomic emissions scenarios
(applying equal weight to each) and
then selected a set of four values
recommended for use in benefit-cost
analyses: an average value resulting
from the model runs for each of three
discount rates (2.5 percent, 3 percent,
and 5 percent), plus a fourth value,
selected as the 95th percentile of
estimates based on a 3-percent discount
rate. The fourth value was included to
provide information on potentially
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39939
higher-than-expected economic impacts
from climate change. DOE agrees with
the update explained in the February
2021 SC–GHG TSD, which reflects the
immediate need to have an operational
SC–GHG—for use in regulatory benefitcost analyses and other applications—
that was developed using a transparent
process, peer-reviewed methodologies,
and the science available at the time of
that process. Those estimates were
subject to public comment in the
context of dozens of proposed
rulemakings as well as in a dedicated
public comment period in 2013.
A number of limitations and
uncertainties are associated with the
SC–GHG estimates. First, the current
scientific and economic understanding
of discounting approaches suggests
discount rates appropriate for
intergenerational analysis in the context
of climate change are likely to be less
than 3 percent, near 2 percent or
lower.47 Second, the IAMs used to
produce these interim estimates do not
include all of the important physical,
ecological, and economic impacts of
climate change recognized in the
climate change literature; furthermore,
the science underlying their ‘‘damage
functions’’—i.e., the core parts of the
IAMs that map global mean temperature
changes and other physical impacts of
climate change into economic (both
market and nonmarket) damages—lags
behind the most recent research. For
example, limitations include the
incomplete treatment of catastrophic
and non-catastrophic impacts in the
integrated assessment models, their
incomplete treatment of adaptation and
technological change, the incomplete
way in which inter-regional and
intersectoral linkages are modeled,
uncertainty in the extrapolation of
damages due to high temperatures, and
the inadequate representation of the
relationship between the discount rate
and uncertainty in economic growth
over long time horizons. Likewise, the
socioeconomic and emissions scenarios
used as inputs to the models do not
reflect new information from the last
decade of scenario generation or the full
range of projections. The modeling
limitations do not all work in the same
direction in terms of their influence on
the SC–CO2 estimates. However, as
discussed in the February 2021 SC–GHG
47 Interagency Working Group on Social Cost of
Greenhouse Gases (IWG). 2021. Technical Support
Document: Social Cost of Carbon, Methane, and
Nitrous Oxide Interim Estimates under Executive
Order 13990. February. United States Government.
Available at www.whitehouse.gov/briefing-room/
blog/2021/02/26/a-return-to-science-evidencebased-estimates-of-the-benefits-of-reducing-climatepollution/.
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TSD, the IWG has recommended that,
taken together, the limitations suggest
that the interim SC–GHG estimates used
in this final rule likely underestimate
the damages from GHG emissions. DOE
concurs with this assessment.
DOE’s derivations of the SC–CO2, SC–
N2O, and SC–CH4 values used for this
rule are discussed in the following
sections, and the results of DOE’s
analyses estimating the benefits of the
reductions in emissions of these GHGs
are presented in section V.B.6 of this
document.
The C2ES commented that DOE
appropriately applies the social cost
estimates developed by the IWG to its
analysis of emissions reduction benefits
generated by the proposed rule. The
C2ES commented that DOE should
expand upon its rationale for adopting
a global damages valuation and for the
range of discount rates it applies to
climate effects, as there are additional
legal, economic, and policy reasons for
such methodological decisions that can
further bolster DOE’s support for these
choices. C2ES added that DOE should
consider conducting a sensitivity
analysis using a sound domestic-only
social cost estimate as a backstop, and
should explicitly conclude that the rule
is cost-benefit justified even using a
domestic-only valuation that may still
undercount climate benefits. The C2ES
urged DOE to consider providing an
additional sensitivity analysis using
discount rates lower than 2.5 percent for
climate impacts. (C2ES, No. 29 at p. 2)
DOE maintains that the reasons for
using global measures of the SC–GHG
previously discussed are sufficient for
the purposes of this rulemaking. DOE
notes that further discussion of this
topic is contained in the February 2021
SC–GHG TSD, and DOE agrees with the
assessment therein. Regarding
conducting sensitivity analysis using a
domestic-only social cost estimate, DOE
agrees with the assessment in the
February 2021 SC–GHG TSD that the
only currently available quantitative
characterization of domestic damages
from GHG emissions is both incomplete
and an underestimate of the share of
total damages that accrue to the citizens
and residents of the United States.
Therefore, it would be of questionable
value to conduct the suggested
sensitivity analysis at this time. DOE
considered performing sensitivity
analysis using discount rates lower than
2.5 percent for climate impacts, as
suggested by the IWG, but it concluded
that such analysis would not add
meaningful information in the context
of this rulemaking.
a. Social Cost of Carbon
The SC–CO2 values used for this final
rule were based on the values developed
for the IWG’s February 2021 TSD. Table
IV.8 shows the updated sets of SC–CO2
estimates from the IWG’s TSD in 5-year
increments from 2020 to 2050. The full
set of annual values that DOE used is
presented in appendix 14–A of the final
rule TSD. For purposes of capturing the
uncertainties involved in regulatory
impact analysis, DOE has determined it
is appropriate to include all four sets of
SC–CO2 values, as recommended by the
IWG.48
TABLE IV.8.—ANNUAL SC–CO2 VALUES FROM 2021 INTERAGENCY UPDATE, 2020–2050
[2020$ per Metric Ton CO2]
Discount rate and statistic
Year
5% Average
2020
2025
2030
2035
2040
2045
2050
.................................................................................................................
.................................................................................................................
.................................................................................................................
.................................................................................................................
.................................................................................................................
.................................................................................................................
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For 2051 to 2070, DOE used SC–CO2
estimates published by EPA, adjusted to
2020$.49 These estimates are based on
methods, assumptions, and parameters
identical to the 2020–2050 estimates
published by the IWG (which were
based on EPA modeling). DOE expects
additional climate benefits to accrue for
any longer-life furnaces after 2070, but
a lack of available SC–CO2 estimates for
emissions years beyond 2070 prevents
DOE from monetizing these potential
benefits in this analysis.
DOE multiplied the CO2 emissions
reduction estimated for each year by the
48 For example, the February 2021 SC–GHG TSD
discusses how the understanding of discounting
approaches suggests that discount rates appropriate
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3% Average
14
17
19
22
25
28
32
SC–CO2 value for that year in each of
the four cases. DOE adjusted the values
to 2021$ using the implicit price
deflator for gross domestic product
(‘‘GDP’’) from the Bureau of Economic
Analysis. To calculate a present value of
the stream of monetary values, DOE
discounted the values in each of the
four cases using the specific discount
rate that had been used to obtain the
SC–CO2 values in each case.
51
56
62
67
73
79
85
2.5% Average
3%
95th percentile
76
83
89
96
103
110
116
152
169
187
206
225
242
260
b. Social Cost of Methane and Nitrous
Oxide
The SC–CH4 and SC–N2O values used
for this final rule were based on the
values developed for the February 2021
SC–GHG TSD. Table IV.9 shows the
updated sets of SC–CH4 and SC- N2O
estimates from the latest interagency
update in 5-year increments from 2020
to 2050. The full set of annual values
used is presented in appendix 14A of
the final rule TSD. To capture the
uncertainties involved in regulatory
impact analysis, DOE has determined it
is appropriate to include all four sets of
SC–CH4 and SC- N2O values, as
recommended by the IWG. DOE derived
values after 2050 using the approach
described above for the SC–CO2.
for intergenerational analysis in the context of
climate change may be lower than 3 percent.
49 See EPA, Revised 2023 and Later Model Year
Light-Duty Vehicle GHG Emissions Standards:
Regulatory Impact Analysis, Washington, DC,
December 2021. Available at nepis.epa.gov/Exe/
ZyPDF.cgi?Dockey=P1013ORN.pdf (last accessed
January 13, 2023). (last accessed January 20, 2023).
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
TABLE IV.9.—ANNUAL SC–CH4 AND SC–N2O VALUES FROM 2021 INTERAGENCY UPDATE, 2020–2050
[2020$ per metric ton]
SC–CH4
SC–N2O
Discount rate and statistic
Discount rate and statistic
Year
5%
Average
2020
2025
2030
2035
2040
2045
2050
..
..
..
..
..
..
..
3%
Average
670 ...............
800 ...............
940 ...............
1,100 ............
1,300 ............
1,500 ............
1,700 ............
2.5%
Average
1,500
1,700
2,000
2,200
2,500
2,800
3,100
2,000
2,200
2,500
2,800
3,100
3,500
3,800
2. Monetization of Other Emissions
Impacts
For the final rule, DOE estimated the
monetized value of NOX and SO2
emissions reductions from electricity
generation using benefit-per-ton
estimates for that sector from the EPA’s
Benefits Mapping and Analysis
Program.50 DOE used EPA’s values for
PM2.5-related benefits associated with
NOX and SO2 and for ozone-related
benefits associated with NOX for 2025
and 2030, and 2040, calculated with
discount rates of 3 percent and 7
percent. DOE used linear interpolation
to define values for the years not given
in the 2025 to 2040 range; for years
beyond 2040 the values are held
constant. DOE combined the EPA
benefit per ton estimates with regional
information on electricity consumption
and emissions to define weightedaverage national values for NOX and
SO2 as a function of sector (see.
appendix 14B of the final rule TSD).
DOE multiplied the site emissions
reduction (in tons) in each year by the
associated $/ton values, and then
discounted each series using discount
rates of 3 percent and 7 percent as
appropriate.
lotter on DSK11XQN23PROD with RULES2
M. Utility Impact Analysis
The utility impact analysis estimates
the changes in installed electrical
capacity and generation projected to
result for each considered TSL. The
analysis is based on published output
from the NEMS associated with
AEO2022. NEMS produces the AEO
Reference case, as well as a number of
side cases that estimate the economywide impacts of changes to energy
supply and demand. For the current
analysis, impacts are quantified by
50 Estimating the Benefit per Ton of Reducing
PM2.5 Precursors from 21 Sectors. Available at
www.epa.gov/benmap/estimating-benefit-tonreducing-pm25-precursors-21-sectors.
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3%
95th
percentile
5%
Average
3,900
4,500
5,200
6,000
6,700
7,500
8,200
5,800
6,800
7,800
9,000
10,000
12,000
13,000
comparing the levels of electricity sector
generation, installed capacity, fuel
consumption and emissions in the
AEO2022 Reference case and various
side cases. Details of the methodology
are provided in the appendices to
chapters 13 and 15 of the final rule TSD.
The output of this analysis is a set of
time-dependent coefficients that capture
the change in electricity generation,
primary fuel consumption, installed
capacity, and power sector emissions
due to a unit reduction in demand for
a given end use. These coefficients are
multiplied by the stream of electricity
savings calculated in the NIA to provide
estimates of selected utility impacts of
potential new or amended energy
conservation standards.
N. Employment Impact Analysis
DOE considers employment impacts
in the domestic economy as one factor
in selecting a standard. Employment
impacts from new or amended energy
conservation standards include both
direct and indirect impacts. Direct
employment impacts are any changes in
the number of employees of
manufacturers of the products subject to
standards, their suppliers, and related
service firms. The MIA addresses those
impacts. Indirect employment impacts
are changes in national employment
that occur due to the shift in
expenditures and capital investment
caused by the purchase and operation of
more-efficient appliances. Indirect
employment impacts from standards
consist of the net jobs created or
eliminated in the national economy,
other than in the manufacturing sector
being regulated, caused by (1) reduced
spending by consumers on energy, (2)
reduced spending on new energy supply
by the utility industry, (3) increased
consumer spending on the products to
which the new standards apply and
other goods and services, and (4) the
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3%
Average
18,000
21,000
23,000
25,000
28,000
30,000
33,000
2.5%
Average
27,000
30,000
33,000
36,000
39,000
42,000
45,000
3%
95th
percentile
48,000
54,000
60,000
67,000
74,000
81,000
88,000
effects of those three factors throughout
the economy.
One method for assessing the possible
effects on the demand for labor of such
shifts in economic activity is to compare
sector employment statistics developed
by the BLS. BLS regularly publishes its
estimates of the number of jobs per
million dollars of economic activity in
different sectors of the economy, as well
as the jobs created elsewhere in the
economy by this same economic
activity. Data from BLS indicate that
expenditures in the utility sector
generally create fewer jobs (both directly
and indirectly) than expenditures in
other sectors of the economy.51 There
are many reasons for these differences,
including wage differences and the fact
that the utility sector is more capitalintensive and less labor-intensive than
other sectors. Energy conservation
standards have the effect of reducing
consumer utility bills. Because reduced
consumer expenditures for energy likely
lead to increased expenditures in other
sectors of the economy, the general
effect of efficiency standards is to shift
economic activity from a less laborintensive sector (i.e., the utility sector)
to more labor-intensive sectors (e.g., the
retail and service sectors). Thus, the
BLS data suggest that net national
employment may increase due to shifts
in economic activity resulting from
energy conservation standards.
DOE estimated indirect national
employment impacts for the standard
levels considered in this final rule using
an input/output model of the U.S.
economy called Impact of Sector Energy
51 See U.S. Department of Commerce–Bureau of
Economic Analysis. Regional Multipliers: A User
Handbook for the Regional Input-Output Modeling
System (‘‘RIMS II’’). 1997. U.S. Government Printing
Office: Washington, DC. Available at https://
www.bea.gov/sites/default/files/methodologies/
RIMSII_User_Guide.pdf (last accessed January 20,
2023).
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
Technologies version 4 (‘‘ImSET’’).52
ImSET is a special-purpose version of
the ‘‘U.S. Benchmark National InputOutput’’ (‘‘I–O’’) model, which was
designed to estimate the national
employment and income effects of
energy-saving technologies. The ImSET
software includes a computer-based I–O
model having structural coefficients that
characterize economic flows among 187
sectors most relevant to industrial,
commercial, and residential building
energy use.
DOE notes that ImSET is not a general
equilibrium forecasting model, and that
the uncertainties involved in projecting
employment impacts especially change
in the later years of the analysis.
Because ImSET does not incorporate
price changes, the employment effects
predicted by ImSET may over-estimate
actual job impacts over the long run for
this rule. Therefore, DOE used ImSET
only to generate results for near-term
timeframes, where these uncertainties
are reduced. For more details on the
employment impact analysis, see
chapter 16 of the final rule TSD.
V. Analytical Results and Conclusions
The following section addresses the
results from DOE’s analyses with
respect to the considered energy
conservation standards for microwave
ovens. It addresses the TSLs examined
by DOE, the projected impacts of each
of these levels if adopted as energy
conservation standards for microwave
ovens, and the standards levels that
DOE is adopting in this final rule.
Additional details regarding DOE’s
analyses are contained in the final rule
TSD supporting this document.
A. Trial Standard Levels
In general, DOE typically evaluates
potential amended standards for
products and equipment by grouping
individual efficiency levels for each
class into TSLs. Use of TSLs allows DOE
to identify and consider manufacturer
cost interactions between the product
classes, to the extent that there are such
interactions, and market cross elasticity
from consumer purchasing decisions
that may change when different
standard levels are set.
In the analysis conducted for this
final rule, DOE analyzed the benefits
and burdens of three TSLs for
microwave ovens. DOE developed TSLs
that combine efficiency levels for each
analyzed product class. DOE presents
the results for the TSLs in this
document, while the results for all
efficiency levels that DOE analyzed are
in the final rule TSD.
Table V.1 presents the TSLs and the
corresponding efficiency levels that
DOE has identified for potential
amended energy conservation standards
for microwave ovens. TSL 3 represents
the maximum technologically feasible
(‘‘max-tech’’) energy efficiency for all
product classes. TSL 2 and TSL 1
represent interim energy efficiency
levels between the current standard
level and the max-tech energy efficiency
level.
TABLE V.1—TRIAL STANDARD LEVELS FOR MICROWAVE OVENS
Product class
TSL 1
TSL 2
TSL 3
Maximum allowable average standby power (W)
lotter on DSK11XQN23PROD with RULES2
PC 1: Microwave-Only and Countertop Convection ...................................................................
PC 2: Built-In and Over-the-Range Convection ..........................................................................
0.8
1.5
0.6
1.0
0.4
0.5
DOE constructed the TSLs for this
final rule to include efficiency levels
representative of efficiency levels with
similar characteristics (i.e., using similar
technologies and/or efficiencies, and
having roughly comparable equipment
availability). The use of representative
efficiency levels provided for greater
distinction between the TSLs. While
representative efficiency levels were
included in the TSLs, DOE considered
all efficiency levels as part of its
analysis.53
The Joint Commenters requested DOE
to consider an additional TSL that
evaluates Product Class 1 at a level more
stringent than what DOE proposed in
the August 2022 SNOPR. Specifically,
the Joint Commenters requested that
DOE evaluate a modified TSL with
Product Class 1 at 0.4W and Product
Class 2 at 1.0W, noting that this
approach would alleviate DOE’s
concerns of net cost to consumers while
roughly doubling the national energy
savings relative to the proposed levels.
(Joint Commenters, No. 31 at p. 2)
As discussed in section V.B.2.c of this
document, DOE assumes manufacturers
will meet amended energy conservation
standards for microwave ovens by redesigning the control boards of noncompliant models. DOE estimates that
approximately 89 percent of Product
Class 1 shipments will need to be
redesigned to meet the efficiency levels
of the modified TSL suggested by the
Joint Commenters. This represents a
need to redesign models accounting for
approximately 10.5 million units with
manufacturers expressing concern that a
redesign effort of this extent may not be
possible in a three-year time period.
Manufacturers would most likely stop
offering lower-volume non-compliant
models to consumers, choosing instead
to focus their resources on remodeling
the highest-volume selling models first.
Due to the potential impact on
consumer choice, DOE did not evaluate
the additional TSL suggested by the
Joint Commenters in this rulemaking.
B. Economic Justification and Energy
Savings
52 Livingston, O. V., S. R. Bender, M. J. Scott, and
R. W. Schultz. ImSET 4.0: Impact of Sector Energy
Technologies Model Description and User’s Guide.
2015. Pacific Northwest National Laboratory:
Richland, WA. PNNL–24563.
53 Efficiency levels that were analyzed for this
NOPR are discussed in section IV.C.4 of this
document. Results by efficiency level are presented
in final rule TSD chapters 8, 10, and 12.
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1. Economic Impacts on Individual
Consumers
DOE analyzed the economic impacts
on microwave oven consumers by
looking at the effects that potential
amended standards at each TSL would
have on the LCC and PBP. DOE also
examined the impacts of potential
standards on selected consumer
subgroups. These analyses are discussed
in the following sections.
a. Life-Cycle Cost and Payback Period
In general, higher-efficiency products
affect consumers in two ways: (1)
purchase price increases and (2) annual
operating costs decrease. Inputs used for
calculating the LCC and PBP include
total installed costs (i.e., product price
plus installation costs) and operating
costs (i.e., annual energy use, energy
prices, energy price trends, repair costs,
and maintenance costs). The LCC
calculation also uses product lifetime
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
and a discount rate. Chapter 8 of the
final rule TSD provides detailed
information on the LCC and PBP
analyses.
Table V.2 through Table V.5 show the
LCC and PBP results for the TSLs
considered for each product class. In the
first of each pair of tables, the simple
payback is measured relative to the
baseline product. In the second table,
the impacts are measured relative to the
efficiency distribution in the in the nonew-standards case in the compliance
year (see section IV.F.8 of this
document). Because some consumers
purchase products with higher
efficiency in the no-new-standards case,
the average savings are less than the
difference between the average LCC of
39943
the baseline product and the average
LCC at each TSL. The savings refer only
to consumers who are affected by a
standard at a given TSL. Those who
already purchase a product with
efficiency at or above a given TSL are
not affected. Consumers for whom the
LCC increases at a given TSL experience
a net cost.
TABLE V.2—AVERAGE LCC AND PBP RESULTS FOR PC 1: MICROWAVE-ONLY OVENS AND COUNTERTOP CONVECTION
MICROWAVE OVENS
Average costs
(2021$)
TSL
Standby power
(W)
EL
Installed cost
0
1
2
3
1 .......
2 .......
3 .......
........................
0.8
0.6
0.4
First year’s
operating
cost
$254.16
254.24
254.80
255.57
Lifetime
operating
cost
$1.26
1.02
0.78
0.54
Simple
payback
(years)
LCC
$11.38
9.20
7.02
4.83
$265.54
263.44
261.81
260.40
Average
lifetime
(years)
........................
0.3
1.3
2.0
10.78
10.78
10.78
10.78
Note: The results for each TSL are calculated assuming that all consumers use products at that efficiency level. The PBP is measured relative
to the baseline product.
TABLE V.3—AVERAGE LCC SAVINGS RELATIVE TO THE NO-NEW-STANDARDS CASE FOR PC 1: MICROWAVE-ONLY OVENS
AND COUNTERTOP CONVECTION MICROWAVE OVENS
Life-cycle cost savings
TSL
Efficiency level
1 .............................................................................................................................................
2 .............................................................................................................................................
3 .............................................................................................................................................
Average LCC
savings *
(2021$)
1
2
3
Percent of
consumers
that experience
net cost
$0.25
0.99
2.16
0
5
12
* The savings represent the average LCC for affected consumers.
TABLE V.4—AVERAGE LCC AND PBP RESULTS FOR PC 2: BUILT-IN AND OVER-THE-RANGE CONVECTION MICROWAVE
OVENS
Average costs
(2021$)
TSL
Standby power
(W)
EL
Installed cost
1 .......
2 .......
3 .......
0
1
2
3
........................
1.5
1.0
0.5
$546.11
546.11
547.28
551.36
First year’s
operating
cost
Lifetime
operating
cost
$2.74
1.89
1.29
0.69
Simple
payback
(years)
LCC
$24.75
17.11
11.65
6.19
$570.86
563.22
558.93
557.55
Average
lifetime
(years)
........................
0.0
0.8
2.6
10.78
10.78
10.78
10.78
Note: The results for each TSL are calculated assuming that all consumers use products at that efficiency level. The simple PBP is measured
relative to the baseline product.
TABLE V.5—AVERAGE LCC SAVINGS RELATIVE TO THE NO-NEW-STANDARDS CASE FOR PC 2: BUILT-IN AND OVER-THERANGE CONVECTION MICROWAVE OVENS
lotter on DSK11XQN23PROD with RULES2
Life-cycle cost savings
TSL
EL
1 .............................................................................................................................................
2 .............................................................................................................................................
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Average LCC
savings *
(2021$)
1
2
20JNR2
$0.00
0.83
Percent of
consumers
that experience
net cost
0
7
39944
Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
TABLE V.5—AVERAGE LCC SAVINGS RELATIVE TO THE NO-NEW-STANDARDS CASE FOR PC 2: BUILT-IN AND OVER-THERANGE CONVECTION MICROWAVE OVENS—Continued
Life-cycle cost savings
TSL
EL
3 .............................................................................................................................................
Average LCC
savings *
(2021$)
3
Percent of
consumers
that experience
net cost
1.95
42
* The savings represent the average LCC for affected consumers.
b. Consumer Subgroup Analysis
In the consumer subgroup analysis,
DOE estimated the impact of the
considered TSLs on low-income
households and senior-only households.
Table V.6 and Table V.7 compare the
average LCC savings and PBP at each
efficiency level for the consumer
subgroups with similar metrics for the
entire consumer sample for both
product classes. In most cases, the
average LCC savings and PBP for lowincome households and senior-only
households at the considered efficiency
levels are not substantially different
from the average for all households.
Chapter 11 of the final rule TSD
presents the complete LCC and PBP
results for the subgroups.
TABLE V.6—COMPARISON OF LCC SAVINGS AND PBP FOR CONSUMER SUBGROUPS AND ALL HOUSEHOLDS; PC 1:
MICROWAVE-ONLY OVENS AND COUNTERTOP CONVECTION MICROWAVE OVENS
Average life-cycle cost savings *
(2021$)
TSL
Simple payback period
(years)
Net cost
(%)
EL
Lowincome ‡
1 .................................................
2 .................................................
3 .................................................
1
2
3
$0.25
0.99
2.13
Senioronly §
Nation
$0.25
0.97
2.12
Lowincome
$0.25
0.99
2.16
Senioronly
0.3
1.3
2.0
Nation
0.3
1.3
2.0
0.3
1.3
2.0
Lowincome
0
6
13
Senioronly
Nation
0
5
12
0
5
12
* The savings represent the average LCC for affected consumers.
‡ Low-income households represent 12.5 percent of all households for this product class.
§ Senior-only households represent 24.7 percent of all households for this product class.
TABLE V.7—COMPARISON OF LCC SAVINGS AND PBP FOR CONSUMER SUBGROUPS AND ALL HOUSEHOLDS; PC 2:
BUILT-IN AND OVER-THE-RANGE CONVECTION MICROWAVE OVENS
Average life-cycle cost savings *
(2021$)
TSL
Simple payback period
(years)
Net cost
(%)
EL
Lowincome ‡
1 .................................................
2 .................................................
3 .................................................
1
2
3
$0.00
0.76
1.79
Senioronly §
Nation
$0.00
0.76
1.79
Lowincome
$0.00
0.83
1.95
Senioronly
0.0
0.8
2.6
0.0
0.8
2.6
Nation
0.0
0.8
2.6
Lowincome
0
8
43
Senioronly
0
8
43
Nation
0
7
42
lotter on DSK11XQN23PROD with RULES2
* The savings represent the average LCC for affected consumers.
‡ Low-income households represent 12.5 percent of all households for this product class.
§ Senior-only households represent 24.7 percent of all households for this product class.
c. Rebuttable Presumption Payback
As discussed in section III.E.2 of this
document, EPCA establishes a
rebuttable presumption that an energy
conservation standard is economically
justified if the increased purchase cost
for a product that meets the standard is
less than three times the value of the
first-year energy savings resulting from
the standard. In calculating a rebuttable
presumption payback period for each of
the considered TSLs, DOE used discrete
values, and, as required by EPCA, based
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the energy use calculation on the DOE
test procedures for microwave ovens. In
contrast, the PBPs presented in section
V.B.1.a of this document were
calculated using distributions that
reflect the range of energy use in the
field.
Table V.8 presents the rebuttablepresumption payback periods for the
considered TSLs for microwave ovens.
While DOE examined the rebuttablepresumption criterion, it considered
whether the standard levels considered
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for this rule are economically justified
through a more detailed analysis of the
economic impacts of those levels,
pursuant to 42 U.S.C. 6295(o)(2)(B)(i),
that considers the full range of impacts
to the consumer, manufacturer, Nation,
and environment. The results of that
analysis serve as the basis for DOE to
definitively evaluate the economic
justification for a potential standard
level, thereby supporting or rebutting
the results of any preliminary
determination of economic justification.
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39945
TABLE V.8—REBUTTABLE-PRESUMPTION PAYBACK PERIODS
Product class
1
2
3
(years)
PC 1: Microwave-Only and Countertop Convection ...................................................................
PC 2: Built-In and Over-the-Range Convection ..........................................................................
2. Economic Impacts on Manufacturers
DOE performed an MIA to estimate
the impact of amended energy
conservation standards on
manufacturers of microwave ovens. The
next section describes the expected
impacts on manufacturers at each
considered TSL. Chapter 12 of the final
rule TSD explains the analysis in further
detail.
a. Industry Cash Flow Analysis Results
In this section, DOE provides GRIM
results from the analysis, which
examines changes in the industry that
would result from a standard. The
following tables summarize the
estimated financial impacts (represented
by changes in INPV) of potential
amended energy conservation standards
on manufacturers of microwave ovens,
as well as the conversion costs that DOE
estimates manufacturers of microwave
ovens would incur at each TSL. To
evaluate the range of cash-flow impacts
on the microwave oven industry, DOE
modeled two manufacturer markup
scenarios using different assumptions
that correspond to the range of
anticipated market responses to
amended energy conservation
standards: (1) the conversion cost
recovery scenario and (2) the constant
price scenario.
To assess the lowest magnitude of the
range of potential impacts, DOE
modeled a conversion cost recovery
scenario in which manufacturers are
able to increase their manufacturer
markups in response to amended energy
conservation standards. To assess the
largest magnitude of the range of
potential impacts, DOE modeled a
constant price scenario in which
manufacturers incur conversion costs
but do not receive any additional
revenue from these redesign efforts.
2.1
0.0
2.2
2.2
2.2
2.7
As noted in the MIA methodology
discussion (see section IV.J of this
document), in addition to manufacturer
markup scenarios, the MPCs, shipments,
and conversion cost assumptions also
affect INPV results.
The results in Table V.9 and Table
V.10 present potential INPV impacts for
microwave oven manufacturers. Table
V.9 reflects the lowest magnitude of
potential impacts (conversion cost
recovery scenario), and Table V.10
represents the largest magnitude of
potential impacts (constant price
scenario). In the following discussion,
the INPV results refer to the difference
in industry value between the no-newstandards case and each standards case
that results from the sum of discounted
cash flows from 2023 (the reference
year) through 2055 (the end of the
analysis period).
TABLE V.9—MANUFACTURER IMPACT ANALYSIS RESULTS—CONVERSION COST RECOVERY SCENARIO
No-newstandards
case
Units
INPV .....................................................................
Change in INPV ....................................................
Product Conversion Costs ....................................
Capital Conversion Costs .....................................
Total Conversion Costs ........................................
2021$ millions ...............
2021$ millions ...............
% ...................................
2021$ millions ...............
2021$ millions ...............
2021$ millions ...............
Trial standard level *
1
1,426
........................
........................
........................
........................
........................
2
1,426
0.0
0.0
2.8
2.5
5.3
3
1,426
0.0
0.0
23.6
22.5
46.1
1,426
0.0
0.0
55.0
53.3
108.3
* Parentheses indicate negative values. Numbers may not sum exactly due to rounding.
TABLE V.10—MANUFACTURER IMPACT ANALYSIS RESULTS—CONSTANT PRICE SCENARIO
No-newstandards
case
Units
INPV .....................................................................
Change in INPV ....................................................
Product Conversion Costs ....................................
Capital Conversion Costs .....................................
Total Conversion Costs ........................................
2021$ millions ...............
2021$ millions ...............
% ...................................
2021$ millions ...............
2021$ millions ...............
2021$ millions ...............
Trial standard level *
1
1,426
........................
........................
........................
........................
........................
2
1,422
(4.2)
(0.3)
2.8
2.5
5.3
3
1,389
(37.2)
(2.6)
23.6
22.5
46.1
1,339
(87.5)
(6.1)
55.0
53.3
108.3
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* Parentheses indicate negative values. Numbers may not sum exactly due to rounding.
At TSL 1, DOE estimates impacts on
INPV will range from ¥$4.2 million,
which represents a change of ¥0.3
percent, to no change in INPV. At TSL
1, industry free cash flow decreases to
$98 million, which represents a
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decrease of approximately 2.1 percent,
compared to the no-new-standards case
value of $100 million in 2025, the year
leading up to the compliance date.
TSL 1 would set the energy
conservation standard for both product
classes at EL 1. DOE estimates that 85
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percent of Product Class 1 shipments
and 100 percent of Product Class 2
shipments would already meet or
exceed the efficiency levels required at
TSL 1. DOE expects microwave oven
manufacturers to incur approximately
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$2.8 million in product conversion costs
to redesign and re-test non-compliant
models and approximately $2.5 million
in capital conversion costs to purchase
new tooling and equipment necessary to
produce these redesigned models.
At TSL 2, DOE estimates that impacts
on INPV will range from ¥$37.2
million, which represents a change of
¥2.6 percent, to no change in INPV. At
TSL 2, industry free cash flow decreases
to $82 million, which represents a
decrease of approximately 18.4 percent,
compared to the no-new-standards case
value of $100 million in 2025, the year
leading up to the compliance date.
TSL 2 would set the energy
conservation standard for both product
classes at EL 2. DOE estimates that 40
percent of Product Class 1 shipments
and 64 percent of Product Class 2
shipments would already meet or
exceed the efficiency levels required at
TSL 2. DOE expects microwave oven
manufacturers to incur approximately
$23.6 million in product conversion
costs to redesign and re-test noncompliant models and approximately
$22.5 million in capital conversion costs
to purchase new tooling and equipment
necessary to produce these redesigned
models.
At TSL 3, DOE estimates impacts on
INPV will range from ¥$87.5 million,
which represents a change of ¥6.1
percent, to no change in INPV. At TSL
3, industry free cash flow decreases to
$57 million, which represents a
decrease of approximately 43.3 percent
compared to the no-new-standards case
value of $100 million in 2025, the year
leading up to the compliance date.
TSL 3 would set the energy
conservation standard for both product
classes at max-tech (EL 3). DOE
estimates that 11 percent of Product
Class 1 shipments and 5 percent of
Product Class 2 shipments would
already meet the efficiency levels
required at TSL 3. DOE expects
microwave oven manufacturers to incur
approximately $55.0 million in product
conversion costs to redesign and re-test
non-compliant models and
approximately $53.3 million in capital
conversion costs to purchase new
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tooling and equipment necessary to
produce these redesigned models.
b. Direct Impacts on Employment
DOE estimates that over 95 percent of
microwave oven manufacturing occurs
outside the United States. Furthermore,
none of the analyzed efficiency levels
require additional labor and would not
impact current manufacturing labor
practices. Therefore, DOE estimates that
there will be no direct impacts on
domestic employment at any of the
analyzed TSLs.
c. Impacts on Manufacturing Capacity
DOE assumes manufacturers will
meet amended energy conservation
standards for microwave ovens by redesigning the control boards of noncompliant models. DOE estimates that
approximately 89 percent of Product
Class 1 shipments and 95 percent of
Product Class 2 shipments will need to
be redesigned to meet the efficiency
levels required at TSL 3. This represents
a need to redesign models accounting
for approximately 10.5 million Product
Class 1 units and 0.4 million Product
Class 2 units. Manufacturers have
expressed concern that redesigning 90
percent of all microwave oven models
in a three-year time period might not be
possible.
At TSL 2, DOE estimates that
approximately 60 percent of Product
Class 1 shipments and 36 percent of
Product Class 2 shipments will need to
be redesigned to meet the efficiency
levels; at TSL 1, DOE estimates that
approximately 15 percent of Product
Class 1 shipments and no Product Class
2 shipments will need to be redesigned
to meet the efficiency levels. Both of the
redesign requirements at TSL 1 and TSL
2 are unlikely to cause a significant
capacity concern for most microwave
oven manufacturers.
d. Impacts on Subgroups of
Manufacturers
Small manufacturers, niche
equipment manufacturers, and
manufacturers exhibiting a cost
structure substantially different from the
industry average could be affected
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disproportionately. Using average cost
assumptions developed for an industry
cash-flow estimate is inadequate to
assess differential impacts among
manufacturer subgroups.
For the microwave oven industry,
DOE identified and evaluated the
impact of amended energy conservation
standards on one subgroup—small
manufacturers. The Small Business
Administration (‘‘SBA’’) defines a
‘‘small business’’ as having 1,500
employees or fewer for the North
American Industry Classification
System (‘‘NAICS’’) code 335220, ‘‘Major
Household Appliance
Manufacturing.’’ 54 For a discussion of
the impacts on the small manufacturer
subgroup, see the regulatory flexibility
analysis in section VI.B of this
document and chapter 12 of the final
rule TSD.
e. Cumulative Regulatory Burden
One aspect of assessing manufacturer
burden involves looking at the
cumulative impact of multiple DOE
standards and the regulatory actions of
other Federal agencies and States that
affect the manufacturers of a covered
product or equipment. While any one
regulation may not impose a significant
burden on manufacturers, the combined
effects of several existing or impending
regulations may have serious
consequences for some manufacturers,
groups of manufacturers, or an entire
industry. Multiple regulations affecting
the same manufacturer can strain profits
and lead companies to abandon product
lines or markets with lower expected
future returns than competing products.
For these reasons, DOE conducts an
analysis of cumulative regulatory
burden as part of its rulemakings
pertaining to appliance efficiency.
DOE evaluates product-specific
regulations that will take effect
approximately 3 years before or after the
estimated 2026 compliance date of any
amended energy conservation standards
for microwave ovens. This information
is presented in Table V.11.
54 Available at www.sba.gov/document/supporttable-size-standards (last accessed on Jan. 11, 2023).
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TABLE V.11—COMPLIANCE DATES AND EXPECTED CONVERSION EXPENSES OF FEDERAL ENERGY CONSERVATION
STANDARDS AFFECTING MICROWAVE OVEN MANUFACTURERS
Number of
manufacturers
affected from
today’s rule **
Number of
mfrs *
Federal energy conservation standard
Industry
conversion
costs
(millions$)
Approx.
standards
year
Portable Air Conditioners, 85 FR 1378 (Jan. 10, 2020)
11
2
2025
Room Air Conditioners ‡ ................................................
8
3
2026
Consumer Clothes Dryers, 87 FR 51734 (Aug. 23,
2022) † ........................................................................
15
9
Consumer Conventional Cooking Products, 88 FR
6818 (Feb. 1, 2023) †† ...............................................
34
Residential Clothes Washers, 88 FR 13520 (Mar. 3,
2023) †† ......................................................................
Industry
conversion
costs/product
revenue ***
(%)
$320.9
(2015$)
$24.8
(2021$)
6.7
2027
$149.7
(2020$)
1.8
10
2027
$183.4
(2021$)
1.2
19
5
2027
$690.8
(2021$)
5.2
Refrigerators, Refrigerator-Freezers, and Freezers, 88
FR 12452 (Feb. 27, 2023) †† .....................................
49
12
2027
$1,323.6
(2021$)
3.8
Miscellaneous Refrigeration Products, 88 FR 19382
(Mar. 31, 2023) †† ......................................................
38
7
2029
$126.9
(2021$)
3.1
0.4
* This column presents the total number of manufacturers identified in the energy conservation standard rule contributing to cumulative regulatory burden.
** This column presents the number of manufacturers producing microwave ovens that are also listed as manufacturers in the listed energy
conservation standard contributing to cumulative regulatory burden.
*** This column presents industry conversion costs as a percentage of product revenue during the conversion period. Industry conversion costs
are the upfront investments manufacturers must make to sell compliant products/equipment. The revenue used for this calculation is the revenue
from just the covered product/equipment associated with each row. The conversion period is the time frame over which conversion costs are
made and lasts from the publication year of the final rule to the compliance year of the energy conservation standard. The conversion period
typically ranges from 3 to 5 years, depending on the rulemaking.
‡ At the time of issuance of this microwave ovens rulemaking, the rulemaking has been issued and is pending publication in the Federal Register. Once published, the room air conditioners final rule will be available at: www.regulations.gov/docket/EERE-2014-BT-STD-0059.
†† Indicates a proposed rulemaking. Values could change upon publication of a final rule.
In addition to the rulemakings listed
in Table V.11, DOE has other ongoing
rulemakings for products that
microwave oven manufacturers
produce: dishwashers 55 and
dehumidifiers.56
3. National Impact Analysis
This section presents DOE’s estimates
of the national energy savings and the
NPV of consumer benefits that would
result from each of the TSLs considered
as potential amended standards.
a. Significance of Energy Savings
To estimate the energy savings
attributable to potential amended
standards for microwave ovens, DOE
compared their energy consumption
under the no-new-standards case to
their anticipated energy consumption
under each TSL. The savings are
measured over the entire lifetime of
products purchased in the 30-year
period that begins in the year of
anticipated compliance with amended
standards (2026–2055). Table V.12
presents DOE’s projections of the
national energy savings for each TSL
considered for microwave ovens. The
savings were calculated using the
approach described in section IV.H.2 of
this document.
TABLE V.12—CUMULATIVE NATIONAL ENERGY SAVINGS FOR MICROWAVE OVENS; 30 YEARS OF SHIPMENTS
[2026–2055]
Trial standard level
1
2
3
(quads)
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Primary energy ............................................................................................................................
FFC energy ..................................................................................................................................
0.01
0.01
0.05
0.06
0.12
0.12
OMB Circular A–4 57 requires
agencies to present analytical results,
including separate schedules of the
monetized benefits and costs that show
the type and timing of benefits and
costs. Circular A–4 also directs agencies
55 www.regulations.gov/docket/EERE-2014-BTSTD-0021.
56 www.regulations.gov/docket/EERE-2019-BTSTD-0043.
57 U.S. Office of Management and Budget.
Circular A–4: Regulatory Analysis. September 17,
2003. obamawhitehouse.archives.gov/omb/
circulars_a004_a-4/ (last accessed January 13,
2023).
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to consider the variability of key
elements underlying the estimates of
benefits and costs. For this rulemaking,
DOE undertook a sensitivity analysis
using 9 years, rather than 30 years, of
product shipments. The choice of a 9year period is a proxy for the timeline
in EPCA for the review of certain energy
conservation standards and potential
revision of and compliance with such
revised standards.58 The review
timeframe established in EPCA is
generally not synchronized with the
product lifetime, product manufacturing
cycles, or other factors specific to
microwave ovens. Thus, such results are
presented for informational purposes
only and are not indicative of any
change in DOE’s analytical
methodology. The NES sensitivity
analysis results based on a 9-year
analytical period are presented in Table
V.13. The impacts are counted over the
lifetime of microwave ovens purchased
in 2026–2055.
TABLE V.13—CUMULATIVE NATIONAL ENERGY SAVINGS FOR MICROWAVE OVENS; 9 YEARS OF SHIPMENTS
[2026–2055]
Trial standard level
1
2
3
(quads)
Source energy .............................................................................................................................
FFC energy ..................................................................................................................................
b. Net Present Value of Consumer Costs
and Benefits
DOE estimated the cumulative NPV of
the total costs and savings for
consumers that would result from the
TSLs considered for microwave ovens.
In accordance with OMB’s guidelines on
regulatory analysis,59 DOE calculated
NPV using both a 7-percent and a 3-
0.003
0.003
0.014
0.015
0.034
0.035
percent real discount rate. Table V.14
shows the consumer NPV results with
impacts counted over the lifetime of
products purchased in 2026–2055.
TABLE V.14—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFITS FOR MICROWAVE OVENS; 30 YEARS OF
SHIPMENTS
[2026–2055]
Trial standard level
Discount rate
1
2
3
(billion 2021$)
3 percent ......................................................................................................................................
7 percent ......................................................................................................................................
The NPV results based on the
aforementioned 9-year analytical period
are presented in Table V.15. The
impacts are counted over the lifetime of
products purchased in 2026–2055. As
mentioned previously, such results are
presented for informational purposes
only and are not indicative of any
0.080
0.039
0.353
0.164
0.710
0.320
change in DOE’s analytical methodology
or decision criteria.
TABLE V.15—CUMULATIVE NET PRESENT VALUE OF CONSUMER BENEFITS FOR MICROWAVE OVENS; 9 YEARS OF
SHIPMENTS
[2026–2055]
Trial standard level
Discount rate
1
2
3
(billion 2021$)
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3 percent ......................................................................................................................................
7 percent ......................................................................................................................................
58 EPCA requires DOE to review its standards at
least once every 6 years, and requires, for certain
products, a 3-year period after any new standard is
promulgated before compliance is required, except
that in no case may any new standards be required
within 6 years of the compliance date of the
previous standards. While adding a 6-year review
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to the 3-year compliance period adds up to 9 years,
DOE notes that it may undertake reviews at any
time within the 6-year period and that the 3-year
compliance date may yield to the 6-year backstop.
A 9-year analysis period may not be appropriate
given the variability that occurs in the timing of
standards reviews and the fact that for some
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0.030
0.020
0.127
0.079
0.266
0.160
products, the compliance period is 5 years rather
than 3 years.
59 U.S. Office of Management and Budget.
Circular A–4: Regulatory Analysis. September 17,
2003. obamawhitehouse.archives.gov/omb/
circulars_a004_a-4/ (last accessed December 13,
2022).
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The previous results reflect the use of
a default trend to estimate the change in
price for microwave ovens over the
analysis period (see section IV.F.1 of
this document). DOE also conducted a
sensitivity analysis that considered one
scenario with a lower rate of price
decline than the reference case and one
scenario with a higher rate of price
decline than the reference case. The
results of these alternative cases are
presented in appendix 10C of the final
rule TSD. In the high-price-decline case,
the NPV of consumer benefits is higher
than in the default case. In the lowprice-decline case, the NPV of consumer
benefits is lower than in the default
case.
c. Indirect Impacts on Employment
DOE estimates that amended energy
conservation standards for microwave
ovens will reduce energy expenditures
for consumers of those products, with
the resulting net savings being
redirected to other forms of economic
activity. These expected shifts in
spending and economic activity could
affect the demand for labor. As
described in section IV.N of this
document, DOE used an input/output
model of the U.S. economy to estimate
indirect employment impacts of the
TSLs that DOE considered. There are
uncertainties involved in projecting
employment impacts, especially
changes in the later years of the
analysis. Therefore, DOE generated
results for near-term timeframes (2026–
2031), where these uncertainties are
reduced.
The results suggest that the adopted
standards are likely to have a negligible
impact on the net demand for labor in
the economy. The net change in jobs is
so small that it would be imperceptible
in national labor statistics and might be
offset by other, unanticipated effects on
employment. Chapter 16 of the final
rule TSD presents detailed results
regarding anticipated indirect
employment impacts.
4. Impact on Utility or Performance of
Products
As discussed in section IV.C.1.b of
this document, DOE has concluded that
the standards adopted in this final rule
will not lessen the utility or
performance of the microwave ovens
under consideration in this rulemaking.
Manufacturers of these products
currently offer units that meet or exceed
the adopted standards.
5. Impact of Any Lessening of
Competition
DOE considered any lessening of
competition that would be likely to
result from new or amended standards.
As discussed in section III.E.1.e of this
document, EPCA directs the Attorney
General of the United States (‘‘Attorney
General’’) to determine the impact, if
any, of any lessening of competition
likely to result from a proposed
standard and to transmit such
determination in writing to the
Secretary within 60 days of the
publication of a proposed rule, together
with an analysis of the nature and
extent of the impact. To assist the
Attorney General in making this
determination, DOE provided the
Department of Justice (‘‘DOJ’’) with
copies of the August 2022 SNOPR and
39949
the SNOPR TSD for review. In its
assessment letter responding to DOE,
DOJ concluded that the proposed energy
conservation standards for microwave
ovens are unlikely to have a significant
adverse impact on competition. DOE is
publishing the Attorney General’s
assessment at the end of this final rule.
6. Need of the Nation To Conserve
Energy
Enhanced energy efficiency, where
economically justified, improves the
Nation’s energy security, strengthens the
economy, and reduces the
environmental impacts (costs) of energy
production. Reduced electricity demand
due to energy conservation standards is
also likely to reduce the cost of
maintaining the reliability of the
electricity system, particularly during
peak-load periods. Chapter 15 of the
final rule TSD presents the estimated
impacts on electricity generating
capacity, relative to the no-newstandards case, for the TSLs that DOE
considered in this rulemaking.
Energy conservation resulting from
potential energy conservation standards
for microwave ovens is expected to
yield environmental benefits in the form
of reduced emissions of certain air
pollutants and greenhouse gases. Table
V.16 provides DOE’s estimate of
cumulative emissions reductions
expected to result from the TSLs
considered in this rulemaking. The
emissions were calculated using the
multipliers discussed in section IV.K of
this document. DOE reports annual
emissions reductions for each TSL in
chapter 13 of the final rule TSD.
TABLE V.16—CUMULATIVE EMISSIONS REDUCTION FOR MICROWAVE OVENS SHIPPED IN 2026–2055
Trial standard level
1
2
3
Power Sector Emissions
CO2 (million metric tons) .............................................................................................................
CH4 (thousand tons) ....................................................................................................................
N2O (thousand tons) ....................................................................................................................
SO2 (thousand tons) ....................................................................................................................
NOX (thousand tons) ...................................................................................................................
Hg (tons) ......................................................................................................................................
0.33
0.03
0.00
0.16
0.17
0.00
1.74
0.14
0.02
0.84
0.88
0.01
3.92
0.31
0.04
1.89
1.98
0.01
0.03
2.39
0.00
0.00
0.38
0.00
0.13
12.50
0.00
0.01
2.00
0.00
0.30
28.14
0.00
0.02
4.51
0.00
0.36
2.41
1.87
12.64
4.21
28.45
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Upstream Emissions
CO2 (million metric tons) .............................................................................................................
CH4 (thousand tons) ....................................................................................................................
N2O (thousand tons) ....................................................................................................................
SO2 (thousand tons) ....................................................................................................................
NOX (thousand tons) ...................................................................................................................
Hg (tons) ......................................................................................................................................
Total FFC Emissions
CO2 (million metric tons) .............................................................................................................
CH4 (thousand tons) ....................................................................................................................
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TABLE V.16—CUMULATIVE EMISSIONS REDUCTION FOR MICROWAVE OVENS SHIPPED IN 2026–2055—Continued
Trial standard level
1
2
N2O (thousand tons) ....................................................................................................................
SO2 (thousand tons) ....................................................................................................................
NOX (thousand tons) ...................................................................................................................
Hg (tons) ......................................................................................................................................
As part of the analysis for this rule,
DOE estimated monetary benefits likely
to result from the reduced emissions of
CO2 that DOE estimated for each of the
considered TSLs for microwave ovens.
Section IV.L of this document discusses
the estimated SC–CO2 values that DOE
used. Table V.17 presents the value of
CO2 emissions reduction at each TSL for
each of the SC–CO2 cases. The time-
3
0.00
0.16
0.55
0.00
0.02
0.85
2.88
0.01
0.04
1.91
6.49
0.01
series of annual values is presented for
the selected TSL in chapter 14 of the
final rule TSD.
TABLE V.17—PRESENT VALUE OF CO2 EMISSIONS REDUCTION FOR MICROWAVE OVENS SHIPPED IN 2026–2055
SC–CO2 case
Discount rate and statistics
TSL
5%
3%
2.5%
3%
Average
Average
Average
95th percentile
(million 2021$)
1 .......................................................................................................................
2 .......................................................................................................................
3 .......................................................................................................................
As discussed in section IV.L.2 of this
document, DOE estimated the climate
benefits likely to result from the
reduced emissions of methane and N2O
that DOE estimated for each of the
3.63
19.00
42.78
considered TSLs for microwave ovens.
Table V.18 presents the value of the CH4
emissions reduction at each TSL, and
Table V.19 presents the value of the N2O
emissions reduction at each TSL. The
15.19
79.47
178.91
23.58
123.39
277.80
46.17
241.61
543.96
time-series of annual values is presented
for the selected TSL in chapter 14 of the
final rule TSD.
TABLE V.18—PRESENT VALUE OF METHANE EMISSIONS REDUCTION FOR MICROWAVE OVENS SHIPPED IN 2026–2055
SC–CH4 case
Discount rate and statistics
TSL
5%
3%
2.5%
3%
Average
Average
Average
95th percentile
(million 2021$)
1 .......................................................................................................................
2 .......................................................................................................................
3 .......................................................................................................................
1.11
5.82
13.10
3.22
16.83
37.90
4.46
23.33
52.52
8.51
44.56
100.31
TABLE V.19—PRESENT VALUE OF NITROUS OXIDE EMISSIONS REDUCTION FOR MICROWAVE OVENS SHIPPED IN 2026–
2055
SC–N2O Case
Discount rate and statistics
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TSL
5%
3%
2.5%
3%
Average
Average
Average
95th percentile
(million 2021$)
1 .......................................................................................................................
2 .......................................................................................................................
3 .......................................................................................................................
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0.08
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
DOE is well aware that scientific and
economic knowledge about the
contribution of CO2 and other GHG
emissions to changes in the future
global climate and the potential
resulting damages to the global and U.S.
economy continues to evolve rapidly.
DOE, together with other Federal
agencies, will continue to review
methodologies for estimating the
monetary value of reductions in CO2
and other GHG emissions. This ongoing
review will consider the comments on
this subject that are part of the public
record for this and other rulemakings, as
well as other methodological
assumptions and issues. DOE notes,
however, that the adopted standards
would be economically justified even
without inclusion of monetized benefits
of reduced GHG emissions.
DOE also estimated the monetary
value of the economic benefits
associated with NOX and SO2 emissions
reductions anticipated to result from the
considered TSLs for microwave ovens.
The dollar-per-ton values that DOE used
are discussed in section IV.L of this
document. Table V.20 presents the
present value for NOX emissions
reduction for each TSL calculated using
7-percent and 3-percent discount rates,
and Table V.21 presents similar results
for SO2 emissions reductions. The
results in these tables reflect application
of EPA’s low dollar-per-ton values,
which DOE used to be conservative. The
39951
benefits from the reductions of those
pollutants as well as from the reduction
of direct PM and other co-pollutants
may be significant. DOE has not
included monetary benefits of the
TABLE V.20—PRESENT VALUE OF
NOX EMISSIONS REDUCTION FOR reduction of Hg emissions because the
MICROWAVE OVENS SHIPPED IN amount of reduction is very small.
2026–2055
7. Other Factors
time-series of annual values is presented
for the selected TSL in chapter 14 of the
final rule TSD.
TSL
1 ................
2 ................
3 ................
The Secretary of Energy, in
determining whether a standard is
economically justified, may consider
(million 2021$)
any other factors that the Secretary
10.11
23.20 deems to be relevant. (42 U.S.C.
52.89
121.38 6295(o)(2)(B)(i)(VII)) No other factors
119.07
273.27 were considered in this analysis.
7% Discount
rate
3% Discount
rate
8. Summary of Economic Impacts
TABLE V.21—PRESENT VALUE OF SO2
Table V.22 presents the NPV values
EMISSIONS REDUCTION FOR MICROthat result from adding the estimates of
WAVE OVENS SHIPPED IN 2026–
the economic benefits resulting from
2055
reduced GHG and NOX and SO2
emissions to the NPV of consumer
benefits calculated for each TSL
considered in this rulemaking. The
consumer benefits are domestic U.S.
(million 2021$)
monetary savings that occur as a result
1 ................
4.17
9.26 of purchasing the covered products and
2 ................
21.80
48.47 are measured for the lifetime of
3 ................
49.08
109.13 products shipped in 2026–2055. The
climate benefits associated with reduced
Not all the public health and
GHG emissions resulting from the
environmental benefits from the
adopted standards are global benefits,
reduction of greenhouse gases, NOX,
and are also calculated based on the
and SO2 are captured in the values
lifetime of microwave ovens shipped in
above, and additional unquantified
2026–2055.
TSL
7% Discount
rate
3% Discount
rate
TABLE V.22—CONSUMER NPV COMBINED WITH PRESENT VALUE OF CLIMATE BENEFITS AND HEALTH BENEFITS
Category
TSL 1
TSL 2
TSL 3
Using 3% discount rate for Consumer NPV and Health Benefits (billion 2021$)
5% Average SC–GHG case ........................................................................................................
3% Average SC–GHG case ........................................................................................................
2.5% Average SC–GHG case .....................................................................................................
3% 95th percentile SC–GHG case ..............................................................................................
0.1
0.1
0.1
0.2
0.5
0.6
0.7
0.8
1.1
1.3
1.4
1.7
0.3
0.3
0.4
0.5
0.5
0.7
0.8
1.1
Using 7% discount rate for Consumer NPV and Health Benefits (billion 2021$)
5% Average SC–GHG case ........................................................................................................
3% Average SC–GHG case ........................................................................................................
2.5% Average SC–GHG case .....................................................................................................
3% 95th percentile SC–GHG case ..............................................................................................
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C. Conclusion
When considering new or amended
energy conservation standards, the
standards that DOE adopts for any type
(or class) of covered product must be
designed to achieve the maximum
improvement in energy efficiency that
the Secretary determines is
technologically feasible and
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economically justified. (42 U.S.C.
6295(o)(2)(A)) In determining whether a
standard is economically justified, the
Secretary must determine whether the
benefits of the standard exceed its
burdens by, to the greatest extent
practicable, considering the seven
statutory factors discussed previously.
(42 U.S.C. 6295(o)(2)(B)(i)) The new or
amended standard must also result in
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0.1
0.1
0.1
0.1
significant conservation of energy. (42
U.S.C. 6295(o)(3)(B))
In the August 2022 SNOPR, DOE
proposed energy conservation standards
for microwave ovens at TSL 2, as
constructed for that analysis. The
minimum wattages corresponding to
TSL 2 from the August 2022 SNOPR are
shown in Table V.23. 87 FR 52282 (Aug.
25, 2022).
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TABLE V.23—PROPOSED ENERGY CONSERVATION STANDARDS FOR MICROWAVE OVENS
Maximum
allowable
average standby
power
(watts)
Product class
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PC 1: Microwave-Only Ovens and Countertop Convection Microwave Ovens ............................................................................
PC 2: Built-In and Over-the-Range Convection Microwave Ovens ..............................................................................................
0.6 W
1.0 W
For this final rule, DOE considered
the impacts of amended standards for
microwave ovens at each TSL,
beginning with the maximum
technologically feasible level, to
determine whether that level was
economically justified. Where the maxtech level was not justified, DOE then
considered the next most efficient level
and undertook the same evaluation until
it reached the highest efficiency level
that is both technologically feasible and
economically justified and saves a
significant amount of energy.
To aid the reader as DOE discusses
the benefits and/or burdens of each TSL,
tables in this section present a summary
of the results of DOE’s quantitative
analysis for each TSL. In addition to the
quantitative results presented in the
tables, DOE also considers other
burdens and benefits that affect
economic justification. These include
the impacts on identifiable subgroups of
consumers who may be
disproportionately affected by a national
standard and impacts on employment.
DOE also notes that the economics
literature provides a wide-ranging
discussion of how consumers trade off
upfront costs and energy savings in the
absence of government intervention.
Much of this literature attempts to
explain why consumers appear to
undervalue energy efficiency
improvements. There is evidence that
consumers undervalue future energy
savings as a result of (1) a lack of
information; (2) a lack of sufficient
salience of the long-term or aggregate
benefits; (3) a lack of sufficient savings
to warrant delaying or altering
purchases; (4) excessive focus on the
short term, in the form of inconsistent
weighting of future energy cost savings
relative to available returns on other
investments; (5) computational or other
difficulties associated with the
evaluation of relevant tradeoffs; and (6)
a divergence in incentives (for example,
between renters and owners, or builders
and purchasers). Having less than
perfect foresight and a high degree of
uncertainty about the future, consumers
may trade off these types of investments
at a higher-than-expected rate between
current consumption and uncertain
future energy cost savings.
In DOE’s current regulatory analysis,
potential changes in the benefits and
costs of a regulation due to changes in
consumer purchase decisions are
included in two ways. First, if
consumers forego the purchase of a
product in the standards case, this
decreases sales for product
manufacturers, and the impact on
manufacturers attributed to lost revenue
is included in the MIA. Second, DOE
accounts for energy savings attributable
only to products actually used by
consumers in the standards case; if a
standard decreases the number of
products purchased by consumers, this
decreases the potential energy savings
from an energy conservation standard.
DOE provides estimates of shipments
and changes in the volume of product
purchases in chapter 9 of the final rule
TSD. However, DOE’s current analysis
does not explicitly control for
heterogeneity in consumer preferences,
preferences across subcategories of
products or specific features, or
consumer price sensitivity variation
according to household income.60
While DOE is not prepared at present
to provide a fuller quantifiable
framework for estimating the benefits
and costs of changes in consumer
purchase decisions due to an energy
conservation standard, DOE is
committed to developing a framework
that can support empirical quantitative
tools for improved assessment of the
consumer welfare impacts of appliance
standards. DOE has posted a paper that
discusses the issue of consumer welfare
impacts of appliance energy
conservation standards, and potential
enhancements to the methodology by
which these impacts are defined and
estimated in the regulatory process.61
DOE welcomes comments on how to
more fully assess the potential impact of
energy conservation standards on
consumer choice and how to quantify
this impact in its regulatory analysis in
future rulemakings.
60 P.C. Reiss and M.W. White. Household
Electricity Demand, Revisited. Review of Economic
Studies. 2005. 72(3): pp. 853–883. doi: 10.1111/
0034–6527.00354.
61 Sanstad, A.H. Notes on the Economics of
Household Energy Consumption and Technology
Choice. 2010. Lawrence Berkeley National
Laboratory. Available at www1.eere.energy.gov/
buildings/appliance_standards/pdfs/consumer_ee_
theory.pdf (last accessed July 1, 2021).
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1. Benefits and Burdens of TSLs
Considered for Microwave Ovens
Standards
Table V.24 and Table V.25 summarize
the quantitative impacts estimated for
each TSL for microwave ovens. The
national impacts are measured over the
lifetime of microwave ovens purchased
in the 30-year period that begins in the
anticipated year of compliance with
amended standards (2026–2055). The
energy savings, emissions reductions,
and value of emissions reductions refer
to full-fuel-cycle results. DOE is
presenting monetized benefits in
accordance with the applicable
Executive orders and DOE would reach
the same conclusion presented in this
notice in the absence of the social cost
of greenhouse gases, including the
Interim Estimates presented by the
Interagency Working Group. The
efficiency levels contained in each TSL
are described in section V.A of this
document.
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TABLE V.24—SUMMARY OF ANALYTICAL RESULTS FOR MICROWAVE OVENS TSLS: NATIONAL IMPACTS
Category
TSL 1
TSL 2
TSL 3
Cumulative FFC National Energy Savings
Quads ..........................................................................................................................................
0.01
0.06
0.12
0.36
2.41
0.00
0.55
0.16
0.00
1.87
12.64
0.02
2.88
0.85
0.01
4.21
28.45
0.04
6.49
1.91
0.01
0.43
0.10
0.17
0.70
0.08
0.35
0.62
0.98
0.22
0.38
1.58
0.27
0.71
1.31
0.211
0.097
0.075
0.382
0.047
0.164
0.336
0.475
0.217
0.168
0.860
0.154
0.320
0.706
Cumulative FFC Emissions Reduction
CO2 (million metric tons) .............................................................................................................
CH4 (thousand tons) ....................................................................................................................
N2O (thousand tons) ....................................................................................................................
SO2 (thousand tons) ....................................................................................................................
NOX (thousand tons) ...................................................................................................................
Hg (tons) ......................................................................................................................................
Present Value of Benefits and Costs (3% discount rate, billion 2021$)
Consumer Operating Cost Savings .............................................................................................
Climate Benefits * .........................................................................................................................
Health Benefits ** .........................................................................................................................
Total Benefits † ............................................................................................................................
Consumer Incremental Product Costs ‡ ......................................................................................
Consumer Net Benefits ...............................................................................................................
Total Net Benefits ........................................................................................................................
0.08
0.02
0.03
0.13
0.00
0.08
0.13
Present Value of Benefits and Costs (7% discount rate, billion 2021$)
Consumer Operating Cost Savings .............................................................................................
Climate Benefits * .........................................................................................................................
Health Benefits ** .........................................................................................................................
Total Benefits † ............................................................................................................................
Consumer Incremental Product Costs ‡ ......................................................................................
Consumer Net Benefits ...............................................................................................................
Total Net Benefits ........................................................................................................................
0.040
0.018
0.014
0.073
0.002
0.039
0.072
Note: This table presents the costs and benefits associated with microwave ovens shipped in 2026–2055. These results include benefits to
consumers which accrue after 2055 from the products shipped in 2026–2055.
* Climate benefits are calculated using four different estimates of the SC–CO2, SC–CH4, and SC–N2O. Together, these represent the global
SC–GHG. For presentational purposes of this table, the climate benefits associated with the average SC–GHG at a 3-percent discount rate are
shown, but DOE does not have a single central SC–GHG point estimate. On March 16, 2022, the Fifth Circuit Court of Appeals (No. 22–30087)
granted the Federal government’s emergency motion for stay pending appeal of the February 11, 2022, preliminary injunction issued in Louisiana
v. Biden, No. 21–cv–1074–JDC–KK (W.D. La.). As a result of the Fifth Circuit’s order, the preliminary injunction is no longer in effect, pending
resolution of the Federal government’s appeal of that injunction or a further court order. Among other things, the preliminary injunction enjoined
the defendants in that case from ‘‘adopting, employing, treating as binding, or relying upon’’ the interim estimates of the social cost of greenhouse gases—which were issued by the Interagency Working Group on the Social Cost of Greenhouse Gases on February 26, 2021—to monetize the benefits of reducing greenhouse gas emissions. As reflected in this rule, DOE has reverted to its approach prior to the injunction and
presents monetized benefits where appropriate and permissible under law.
** Health benefits are calculated using benefit-per-ton values for NOX and SO2. DOE is currently only monetizing (for NOX and SO2) PM2.5 precursor health benefits and (for NOX) ozone precursor health benefits, but will continue to assess the ability to monetize other effects such as
health benefits from reductions in direct PM2.5 emissions. The health benefits are presented at real discount rates of 3 and 7 percent. See section IV.L of this document for more details.
† Total and net benefits include consumer, climate, and health benefits. For presentation purposes, total and net benefits for both the 3-percent
and 7-percent cases are presented using the average SC–GHG with 3-percent discount rate.
‡ Costs include incremental equipment costs as well as installation costs.
TABLE V.25—SUMMARY OF ANALYTICAL RESULTS FOR MICROWAVE OVENS TSLS: MANUFACTURER AND CONSUMER
IMPACTS
Category
Industry NPV (million 2021$) (No-new-standards case INPV = 1,426) ....................
Industry NPV (% change) ..........................................................................................
TSL 1
TSL 2
TSL 3
1,422–1,426
(0.3)–0.0
1,389–1,426
(2.6)–0.0
1,339–1,426
(6.1)–0.0
$0.25
$0.00
$0.24
$0.99
$0.83
$0.98
$2.16
$1.95
$2.15
0.3
0.0
0.3
1.3
0.8
1.3
2.0
2.6
2.0
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Consumer Average LCC Savings (2021$)
PC 1 ...........................................................................................................................
PC 2 ...........................................................................................................................
Shipment-Weighted Average * ...................................................................................
Consumer Simple PBP (years)
PC 1 ...........................................................................................................................
PC 2 ...........................................................................................................................
Shipment-Weighted Average * ...................................................................................
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Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
TABLE V.25—SUMMARY OF ANALYTICAL RESULTS FOR MICROWAVE OVENS TSLS: MANUFACTURER AND CONSUMER
IMPACTS—Continued
Category
TSL 1
TSL 2
TSL 3
Percent of Consumers that Experience a Net Cost
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PC 1 ...........................................................................................................................
PC 2 ...........................................................................................................................
Shipment-Weighted Average * ...................................................................................
DOE first considered TSL 3, which
represents the max-tech efficiency
levels. TSL 3 would save an estimated
0.12 quads of energy, an amount that
DOE considers significant. Under TSL 3,
the NPV of consumer benefit would be
$0.32 billion using a discount rate of 7
percent, and $0.71 billion using a
discount rate of 3 percent.
The cumulative emissions reductions
at TSL 3 are 4.21 Mt of CO2, 1.91
thousand tons of SO2, 6.49 thousand
tons of NOX, 0.012 tons of Hg, 28.45
thousand tons of CH4, and 0.04
thousand tons of N2O. The estimated
monetary value of the climate benefits
from reduced GHG emissions
(associated with the average SC–GHG at
a 3-percent discount rate) at TSL 3 is
$0.22 billion. The estimated monetary
value of the health benefits from
reduced SO2 and NOX emissions at TSL
3 is $0.17 billion using a 7-percent
discount rate and $0.38 billion using a
3-percent discount rate.
Using a 7-percent discount rate for
consumer benefits and costs, health
benefits from reduced SO2 and NOX
emissions, and the 3-percent discount
rate case for climate benefits from
reduced GHG emissions, the estimated
total NPV at TSL 3 is $0.71 billion.
Using a 3-percent discount rate for all
benefits and costs, the estimated total
NPV at TSL 3 is $1.31 billion. The
estimated total NPV is provided for
additional information; however, DOE
primarily relies upon the NPV of
consumer benefits when determining
whether a proposed standard level is
economically justified.
At TSL 3, the average LCC impact is
a savings of $2.16 for Product Class 1
and $1.95 for Product Class 2. The
simple payback period is 2.0 years for
Product Class 1 and 2.6 years for
Product Class 2. The fraction of
consumers experiencing a net LCC cost
is 11.7 percent for Product Class 1 and
42.2 percent for Product Class 2.
At TSL 3, the projected change in
manufacturer INPV ranges from a
decrease of approximately $87.5
million, which corresponds to a
decrease of approximately 6.1 percent,
to no change in INPV. At this TSL, free
cash flow is estimated to decrease by
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0%
0%
0%
43.3 percent compared to the no-newstandards case value in the year before
the compliance year. DOE estimates that
industry must invest $108.3 million to
comply with standards set at TSL 3.
DOE estimates that approximately 11
percent of Product Class 1 (microwaveonly oven and countertop convection
microwave oven) shipments and
approximately 5 percent of Product
Class 2 (built-in and over-the-range
convection microwave oven) shipments
would meet the efficiency levels
analyzed at TSL 3, in the no-newstandards case. Redesigning
approximately 90 percent of microwave
ovens models, which represents
approximately 11 million annual
shipments, will significantly strain
manufacturers’ limited resources during
the 3-year compliance period, given the
number of microwave oven models that
need to be redesigned during this timeperiod. It is unclear if most microwave
oven manufacturers will have the
engineering capacity to complete the
necessary redesigns within the 3-year
compliance period. If manufacturers
require more than three years to
redesign all their non-compliant
microwave oven models, they will
likely prioritize redesigns based on sales
volume, which could lead to some
microwave oven models being
temporary or permanent unavailable.
DOE has determined through its
engineering analysis that many of the
features which comprise the full
complement of existing consumer
functionality are implemented in
microwave ovens currently available on
the market at or near the max-tech
efficiency levels at TSL 3. DOE has not,
however, identified or analyzed any
currently available microwave ovens
that include all such features in the
same unit. Furthermore, DOE is aware
of several emerging technologies (e.g.,
television displays and interior cameras)
which would provide additional
consumer utility distinct from existing
products. Although DOE research
suggests that the implementation of
these emerging technologies would not
require a significant amount of standby
power, because microwave ovens that
incorporate them are not yet
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5%
7%
5%
12%
42%
13%
commercially available, DOE is unable
to verify that products that implemented
these technologies along with the
complete set of features that would
maintain full consumer utility could
meet the efficiency levels at TSL 3.
Accordingly, there is uncertainty as to
whether or not a standard at TSL 3 may
stifle innovation and risk impacting
customer utility.
The Secretary concludes that at TSL
3 for microwave ovens, the benefits of
energy savings, positive NPV of
consumer benefits, emission reductions,
and the estimated monetary value of the
emissions reductions would be
outweighed by the uncertainty of
impacts to customer utility and product
innovation and the percentage of
consumers in Product Class 2 that
would experience a net LCC cost.
Consequently, the Secretary has
concluded that TSL 3 is not
economically justified.
DOE then considered TSL 2, which
represents efficiency level 2 for
microwave ovens. TSL 2 would save an
estimated 0.06 quads of energy, an
amount DOE considers significant.
Under TSL 2, the NPV of consumer
benefit would be $0.16 billion using a
discount rate of 7 percent, and $0.35
billion using a discount rate of 3
percent.
The cumulative emissions reductions
at TSL 2 are 1.87 Mt of CO2, 0.85
thousand tons of SO2, 2.88 thousand
tons of NOX, 0.005 tons of Hg, 12.64
thousand tons of CH4, and 0.02
thousand tons of N2O. The estimated
monetary value of the climate benefits
from reduced GHG emissions
(associated with the average SC–GHG at
a 3-percent discount rate) at TSL 2 is
$0.10 billion. The estimated monetary
value of the health benefits from
reduced SO2 and NOX emissions at TSL
2 is $0.07 billion using a 7-percent
discount rate and $0.17 billion using a
3-percent discount rate.
Using a 7-percent discount rate for
consumer benefits and costs, health
benefits from reduced SO2 and NOX
emissions, and the 3-percent discount
rate case for climate benefits from
reduced GHG emissions, the estimated
total NPV at TSL 2 is $0.34 billion.
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Using a 3-percent discount rate for all
benefits and costs, the estimated total
NPV at TSL 2 is $0.62 billion. The
estimated total NPV is provided for
additional information; however, DOE
primarily relies upon the NPV of
consumer benefits when determining
whether a proposed standard level is
economically justified.
At TSL 2, the average LCC impact is
a savings of $0.99 for Product Class 1
and $0.83 for Product Class 2. The
simple payback period is 1.3 years for
Product Class 1 and 0.8 years for
Product Class 2. The fraction of
consumers experiencing a net LCC cost
is 5.1 percent for Product Class 1 and
7.4 percent for Product Class 2.
At TSL 2, the projected change in
manufacturer INPV ranges from a
decrease of approximately $37.2
million, which corresponds to a
decrease of approximately 2.6 percent,
to no change in INPV. At this TSL, free
cash flow is estimated to decrease by
18.4 percent compared to the no-newstandards case value in the year before
the compliance year. DOE estimates that
industry must invest $46.1 million to
comply with standards set at TSL 2.
DOE estimates that approximately 40
percent of Product Class 1 (microwaveonly oven and countertop convection
microwave oven) shipments and
approximately 64 percent of Product
Class 2 (built-in and over-the-range
convection microwave oven) shipments
would meet or exceed the efficiency
levels analyzed at TSL 2, in the no-newstandards case. Manufacturers would be
required to redesign approximately 60
percent of all microwave oven models,
representing 7.3 million annual
shipments, to meet the efficiency levels
required at TSL 2.
DOE has determined that the standby
power requirements of TSL 2 provide
sufficient power budgets for
manufacturers to implement the full
complement of features that currently
provide consumer utility. In addition,
based on DOE’s assessment of the
expected standby power requirements
for identified emerging technologies,
DOE has concluded that the standby
power levels at TSL 2 do not preclude
the implementation of these
technologies or stifle further innovation.
After considering the analysis and
weighing the benefits and burdens, the
Secretary has concluded that a standard
set at TSL 2 for microwave ovens would
be economically justified. At this TSL,
the average LCC savings for both
product classes of microwave ovens is
positive. An estimated 5 percent of
Product Class 1 consumers and 7
percent of Product Class 2 consumers
would experience a net cost. The FFC
national energy savings are significant
and the NPV of consumer benefits is
positive using both a 3-percent and 7percent discount rate. Notably, the
benefits to consumers vastly outweigh
the cost to manufacturers. At TSL 2, the
NPV of consumer benefits, even
measured at the more conservative
discount rate of 7 percent, is over four
times higher than the maximum
estimated manufacturers’ loss in INPV.
The standard levels at TSL 2 are
economically justified even without
weighing the estimated monetary value
of emissions reductions. When those
emissions reductions are included—
representing $0.10 billion in climate
benefits (associated with the average
SC–GHG at a 3-percent discount rate),
and $0.17 billion (using a 3-percent
discount rate) or $0.07 billion (using a
7-percent discount rate) in health
benefits—the rationale becomes stronger
still.
39955
Accordingly, the Secretary has
concluded that TSL 2 would offer the
maximum improvement in efficiency
that is technologically feasible and
economically justified and would result
in the significant conservation of
energy. Although results are presented
here in terms of TSLs, DOE analyzes
and evaluates all possible ELs for each
product class in its analysis. For both
Product Class 1 (microwave-only oven
and countertop convection microwave
oven) and Product Class 2 (built-in and
over-the-range convection microwave
oven), TSL 2 is comprised of the highest
efficiency level below max-tech. The
ELs one level below max-tech,
representing the finalized standard
levels, result in positive LCC savings for
both classes, reduce the number of
consumers experiencing a net cost, and
reduce the decrease in INPV and
conversion costs to the point where
DOE has concluded they are
economically justified, as discussed for
TSL 2 in the preceding paragraphs.
As stated, DOE conducts the walkdown analysis to determine the TSL that
represents the maximum improvement
in energy efficiency that is
technologically feasible and
economically justified as required under
EPCA. The walk-down is not a
comparative analysis, as a comparative
analysis would result in the
maximization of net benefits instead of
energy savings that are technologically
feasible and economically justified,
which would be contrary to the statute.
86 FR 70892, 70908.
Therefore, based on the previous
considerations, DOE adopts the energy
conservation standards for microwave
ovens at TSL 2. The amended energy
conservation standards for microwave
ovens, which are expressed as watts, are
shown in Table V.26.
TABLE V.26—AMENDED ENERGY CONSERVATION STANDARDS FOR MICROWAVE OVENS
Maximum
allowable
average standby
power
(watts)
Product class
PC 1: Microwave-Only Ovens and Countertop Convection Microwave Ovens ............................................................................
PC 2: Built-In and Over-the-Range Convection Microwave Ovens ..............................................................................................
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2. Annualized Benefits and Costs of the
Adopted Standards
The benefits and costs of the adopted
standards can also be expressed in terms
of annualized values. The annualized
net benefit is (1) the annualized national
economic value (expressed in 2020$) of
the benefits from operating products
that meet the adopted standards
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(consisting primarily of operating cost
savings from using less energy), minus
increases in product purchase costs, and
(2) the annualized monetary value of the
climate and health benefits.
Table V.27 shows the annualized
values for microwave ovens under TSL
2, expressed in 2021$. The results under
the primary estimate are as follows.
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0.6
1.0
Using a 7-percent discount rate for
consumer benefits and costs and NOX
and SO2 reductions, and the 3-percent
discount rate case for GHG social costs,
the estimated cost of the adopted
standards for microwave ovens is $4.3
million per year in increased equipment
installed costs, while the estimated
annual benefits are $19.5 million from
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reduced equipment operating costs, $5.2
million in GHG reductions, and $6.9
million from reduced NOX and SO2
emissions. In this case, the net benefit
amounts to $27.3 million per year.
Using a 3-percent discount rate for all
benefits and costs, the estimated cost of
the adopted standards for microwave
ovens is $4.3 million per year in
increased equipment costs, while the
estimated annual benefits are $23.5
million in reduced operating costs, $5.2
million from GHG reductions, and $9.2
million from reduced NOX and SO2
emissions. In this case, the net benefit
amounts to $33.5 million per year.
TABLE V.27—ANNUALIZED BENEFITS AND COSTS OF ADOPTED STANDARDS (TSL 2) FOR MICROWAVE OVENS
Million 2021$/year
Primary
estimate
Low-netbenefits
estimate
High-netbenefits
estimate
3% discount rate
Consumer Operating Cost Savings .............................................................................................
Climate Benefits * .........................................................................................................................
Health Benefits ** .........................................................................................................................
23.5
5.2
9.2
22.2
5.1
9.0
25.0
5.4
9.4
Total Benefits† ......................................................................................................................
Consumer Incremental Product Costs ‡ ......................................................................................
37.9
4.3
36.3
4.4
39.8
4.1
Net Benefits ..........................................................................................................................
33.5
31.9
35.7
Consumer Operating Cost Savings .............................................................................................
Climate Benefits * (3% discount rate) ..........................................................................................
Health Benefits ** .........................................................................................................................
19.5
5.2
6.9
18.6
5.1
6.7
20.5
5.4
7.1
Total Benefits † .....................................................................................................................
Consumer Incremental Product Costs ‡ ......................................................................................
31.6
4.3
30.4
4.3
32.9
4.1
Net Benefits ..........................................................................................................................
27.3
26.0
28.9
7% discount rate
Note: This table presents the costs and benefits associated with microwave ovens shipped in 2026–2055. These results include benefits to
consumers which accrue after 2055 from the products shipped in 2026–2055. The Primary, Low Net Benefits, and High Net Benefits Estimates
utilize projections of energy prices from the AEO2022 Reference case, Low Economic Growth case, and High Economic Growth case, respectively. In addition, incremental equipment costs reflect a medium decline rate in the Primary Estimate, a low decline rate in the Low Net Benefits
Estimate, and a high decline rate in the High Net Benefits Estimate. The methods used to derive projected price trends are explained in sections
IV.F.1 and IV.H.1 of this document. Note that the Benefits and Costs may not sum to the Net Benefits due to rounding.
* Climate benefits are calculated using four different estimates of the global SC–GHG (see section IV.L of this document). For presentational
purposes of this table, the climate benefits associated with the average SC–GHG at a 3-percent discount rate are shown, but the Department
does not have a single central SC–GHG point estimate, and it emphasizes the importance and value of considering the benefits calculated using
all four sets of SC–GHG estimates. On March 16, 2022, the Fifth Circuit Court of Appeals (No. 22–30087) granted the Federal government’s
emergency motion for stay pending appeal of the February 11, 2022, preliminary injunction issued in Louisiana v. Biden, No. 21–cv–1074–JDC–
KK (W.D. La.). As a result of the Fifth Circuit’s order, the preliminary injunction is no longer in effect, pending resolution of the Federal government’s appeal of that injunction or a further court order. Among other things, the preliminary injunction enjoined the defendants in that case from
‘‘adopting, employing, treating as binding, or relying upon’’ the interim estimates of the social cost of greenhouse gases—which were issued by
the Interagency Working Group on the Social Cost of Greenhouse Gases on February 26, 2021—to monetize the benefits of reducing greenhouse gas emissions. As reflected in this rule, DOE has reverted to its approach prior to the injunction and presents monetized benefits where
appropriate and permissible under law.
** Health benefits are calculated using benefit-per-ton values for NOX and SO2. DOE is currently only monetizing (for SO2 and NOX) PM2.5 precursor health benefits and (for NOX) ozone precursor health benefits, but will continue to assess the ability to monetize other effects such as
health benefits from reductions in direct PM2.5 emissions. See section IV.L of this document for more details.
† Total benefits for both the 3-percent and 7-percent cases are presented using the average SC–GHG with 3-percent discount rate, but the
Department does not have a single central SC–GHG point estimate.
‡ Costs include incremental equipment costs as well as installation costs.
VI. Procedural Issues and Regulatory
Review
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A. Review Under Executive Orders
12866, 13563, and 14094
Executive Order (‘‘E.O.’’) 12866,
‘‘Regulatory Planning and Review,’’ 58
FR 51735 (Oct. 4, 1993), as
supplemented and reaffirmed by E.O.
13563, ‘‘Improving Regulation and
Regulatory Review, 76 FR 3821 (Jan. 21,
2011) and E.O. 14094, ‘‘Modernizing
Regulatory Review,’’ 88 FR 21879 (April
11, 2023), requires agencies, to the
extent permitted by law, to (1) propose
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or adopt a regulation only upon a
reasoned determination that its benefits
justify its costs (recognizing that some
benefits and costs are difficult to
quantify); (2) tailor regulations to
impose the least burden on society,
consistent with obtaining regulatory
objectives, taking into account, among
other things, and to the extent
practicable, the costs of cumulative
regulations; (3) select, in choosing
among alternative regulatory
approaches, those approaches that
maximize net benefits (including
potential economic, environmental,
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public health and safety, and other
advantages; distributive impacts; and
equity); (4) to the extent feasible, specify
performance objectives, rather than
specifying the behavior or manner of
compliance that regulated entities must
adopt; and (5) identify and assess
available alternatives to direct
regulation, including providing
economic incentives to encourage the
desired behavior, such as user fees or
marketable permits, or providing
information upon which choices can be
made by the public. DOE emphasizes as
well that E.O. 13563 requires agencies to
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use the best available techniques to
quantify anticipated present and future
benefits and costs as accurately as
possible. In its guidance, the Office of
Information and Regulatory Affairs
(‘‘OIRA’’) in the Office of Management
and Budget (‘‘OMB’’) has emphasized
that such techniques may include
identifying changing future compliance
costs that might result from
technological innovation or anticipated
behavioral changes. For the reasons
stated in this preamble, this final
regulatory action is consistent with
these principles.
Section 6(a) of E.O. 12866 also
requires agencies to submit ‘‘significant
regulatory actions’’ to OIRA for review.
OIRA has determined that this final rule
does not constitute a ‘‘significant
regulatory action’’ under section 3(f) of
E.O. 12866. Accordingly, this action was
not submitted to OIRA for review under
E.O. 12866.
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’’) and a final regulatory
flexibility analysis (‘‘FRFA’’) for any
rule that by law must be proposed for
public comment, unless the agency
certifies that the rule, if promulgated,
will not have a significant economic
impact on a substantial number of small
entities. As required by E.O. 13272,
‘‘Proper Consideration of Small Entities
in Agency Rulemaking,’’ 67 FR 53461
(Aug. 16, 2002), DOE published
procedures and policies on February 19,
2003, to ensure that the potential
impacts of its rules on small entities are
properly considered during the
rulemaking process. 68 FR 7990. DOE
has made its procedures and policies
available on the Office of the General
Counsel’s website (www.energy.gov/gc/
office-general-counsel).
DOE reviewed this final rule under
the provisions of the Regulatory
Flexibility Act and the procedures and
policies published on February 19,
2003. DOE certifies that this final rule
would not have a significant economic
impact on a substantial number of small
entities. The factual basis of this
certification is set forth in the following
paragraphs.
For manufacturers of microwave
ovens, the SBA has set a size threshold,
which defines those entities classified
as ‘‘small businesses’’ for the purposes
of the statute. DOE used the SBA’s small
business size standards to determine
whether any small entities would be
subject to the requirements of the rule.
(See 13 CFR part 121.) The size
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standards are listed by NAICS code and
industry description and are available at
www.sba.gov/document/support-tablesize-standards. Manufacturing
microwave ovens is classified under
NAICS 335220, ‘‘Major Household
Appliance Manufacturing.’’ The SBA
sets a threshold of 1,500 employees or
fewer for an entity to be considered as
a small business for this category.
DOE identified manufacturers using
DOE’s CCD,62 the California Energy
Commission’s Modernized Appliance
Efficiency Database System
(‘‘MAEDbS’’),63 and prior microwave
oven rulemakings. DOE used the
publicly available information and
subscription-based market research
tools (e.g., reports from DB Hoovers 64)
to identify 37 companies that sell
microwave ovens covered by this
rulemaking in the United States. Of
these 37 companies that sell microwave
ovens in the United States, 19 are
private labelers. These private labelers
out-source the manufacturing of the
microwave ovens to other companies.
Therefore, DOE estimates there are 18
original equipment manufacturers
(‘‘OEMs’’) that manufacture microwave
ovens covered by this rulemaking. Of
the 18 OEMs, DOE was not able to
identify any OEMs of microwave ovens
covered by this rulemaking with fewer
than 1,500 total employees (including
parent companies and subsidiaries), and
that are domestically located. Therefore,
DOE did not identify any companies
that meet SBA’s definition of a ‘‘small
business.’’
DOE did not receive any comments on
the August 2022 SNOPR, which stated
that there were not any small businesses
that manufactured microwave ovens
sold in the United States. Therefore,
DOE concludes and certifies that this
final rule would not have a significant
economic impact on a substantial
number of small entities and has not
prepared a FRFA for this rulemaking.
C. Review Under the Paperwork
Reduction Act
Manufacturers of microwave ovens
must certify to DOE that their products
comply with any applicable energy
conservation standards. In certifying
compliance, manufacturers must test
their products according to the DOE test
procedures for microwave ovens,
including any amendments adopted for
62 DOE’s Compliance Certification Database is
available at www.regulations.doe.gov/ccms (last
accessed January 11, 2023).
63 California Energy Commission’s MAEDbS is
available at cacertappliances.energy.ca.gov/
Login.aspx (last accessed January 11, 2023).
64 D&B Hoovers reports can be accessed at:
app.dnbhoovers.com.
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39957
those test procedures. DOE has
established regulations for the
certification and recordkeeping
requirements for all covered consumer
products and commercial equipment,
including microwave ovens. (See
generally 10 CFR part 429). The
collection-of-information requirement
for the certification and recordkeeping
is subject to review and approval by
OMB under the Paperwork Reduction
Act (‘‘PRA’’). This requirement has been
approved by OMB under OMB control
number 1910–1400. Public reporting
burden for the certification is estimated
to average 35 hours per response,
including the time for reviewing
instructions, searching existing data
sources, gathering and maintaining the
data needed, and completing and
reviewing the collection of information.
Notwithstanding any other provision
of the law, no person is required to
respond to, nor shall any person be
subject to a penalty for failure to comply
with, a collection of information subject
to the requirements of the PRA, unless
that collection of information displays a
currently valid OMB Control Number.
D. Review Under the National
Environmental Policy Act of 1969
Pursuant to the National
Environmental Policy Act of 1969
(‘‘NEPA’’), DOE has analyzed this
proposed action rule in accordance with
NEPA and DOE’s NEPA implementing
regulations (10 CFR part 1021). DOE has
determined that this rule qualifies for
categorical exclusion under 10 CFR part
1021, subpart D, appendix B5.1 because
it is a rulemaking that establishes energy
conservation standards for consumer
products or industrial equipment, none
of the exceptions identified in B5.1(b)
apply, no extraordinary circumstances
exist that require further environmental
analysis, and it meets the requirements
for application of a categorical
exclusion. See 10 CFR 1021.410.
Therefore, DOE has determined that
promulgation of this rule is not a major
Federal action significantly affecting the
quality of the human environment
within the meaning of NEPA, and does
not require an environmental
assessment or an environmental impact
statement.
E. Review Under Executive Order 13132
E.O. 13132, ‘‘Federalism,’’ 64 FR
43255 (Aug. 10, 1999), imposes certain
requirements on Federal agencies
formulating and implementing policies
or regulations that preempt State law or
that have federalism implications. The
Executive order requires agencies to
examine the constitutional and statutory
authority supporting any action that
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would limit the policymaking discretion
of the States and to carefully assess the
necessity for such actions. The
Executive order also requires agencies to
have an accountable process to ensure
meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications. On March 14, 2000, DOE
published a statement of policy
describing the intergovernmental
consultation process it will follow in the
development of such regulations. 65 FR
13735. DOE has examined this rule and
has determined that it would not have
a substantial direct effect on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government. EPCA governs and
prescribes Federal preemption of State
regulations as to energy conservation for
the products that are the subject of this
final rule. States can petition DOE for
exemption from such preemption to the
extent, and based on criteria, set forth in
EPCA. (42 U.S.C. 6297) Therefore, no
further action is required by Executive
Order 13132.
F. Review Under Executive Order 12988
With respect to the review of existing
regulations and the promulgation of
new regulations, section 3(a) of E.O.
12988, ‘‘Civil Justice Reform,’’ imposes
on Federal agencies the general duty to
adhere to the following requirements:
(1) eliminate drafting errors and
ambiguity, (2) write regulations to
minimize litigation, (3) provide a clear
legal standard for affected conduct
rather than a general standard, and (4)
promote simplification and burden
reduction. 61 FR 4729 (Feb. 7, 1996).
Regarding the review required by
section 3(a) and section 3(b) of E.O.
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 E.O. 12988
requires executive agencies to review
regulations in light of applicable
standards in section 3(a) and section
3(b) to determine whether they are met
or it is unreasonable to meet one or
more of them. DOE has completed the
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required review and determined that, to
the extent permitted by law, this final
rule meets the relevant standards of E.O.
12988.
G. Review Under the Unfunded
Mandates Reform Act of 1995
Title II of the Unfunded Mandates
Reform Act of 1995 (‘‘UMRA’’) requires
each Federal agency to assess the effects
of Federal regulatory actions on State,
local, and Tribal governments and the
private sector. Public Law 104–4, Sec.
201 (codified at 2 U.S.C. 1531). For a
regulatory action likely to result in a
rule that may cause the expenditure by
State, local, and Tribal governments, in
the aggregate, or by the private sector of
$100 million or more in any one year
(adjusted annually for inflation), section
202 of UMRA requires a Federal agency
to publish a written statement that
estimates the resulting costs, benefits,
and other effects on the national
economy. (2 U.S.C. 1532(a), (b)) The
UMRA also requires a Federal agency to
develop an effective process to permit
timely input by elected officers of State,
local, and Tribal governments on a
‘‘significant intergovernmental
mandate,’’ and requires an agency plan
for giving notice and opportunity for
timely input to potentially affected
small governments before establishing
any requirements that might
significantly or uniquely affect them. On
March 18, 1997, DOE published a
statement of policy on its process for
intergovernmental consultation under
UMRA. 62 FR 12820. DOE’s policy
statement is also available at
www.energy.gov/sites/prod/files/gcprod/
documents/umra_97.pdf.
DOE has concluded that this final rule
may require expenditures of $100
million or more in any one year by the
private sector. Such expenditures may
include (1) investment in research and
development and in capital
expenditures by microwave ovens
manufacturers in the years between the
final rule and the compliance date for
the new standards and (2) incremental
additional expenditures by consumers
to purchase higher-efficiency
microwave ovens, starting at the
compliance date for the applicable
standard.
Section 202 of UMRA authorizes a
Federal agency to respond to the content
requirements of UMRA in any other
statement or analysis that accompanies
the final rule. (2 U.S.C. 1532(c)) The
content requirements of section 202(b)
of UMRA relevant to a private sector
mandate substantially overlap the
economic analysis requirements that
apply under section 325(o) of EPCA and
Executive Order 12866. The
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SUPPLEMENTARY INFORMATION section and
the TSD for this final rule respond to
those requirements.
Under section 205 of UMRA, the
Department is obligated to identify and
consider a reasonable number of
regulatory alternatives before
promulgating a rule for which a written
statement under section 202 is required.
(2 U.S.C. 1535(a)) DOE is required to
select from those alternatives the most
cost-effective and least burdensome
alternative that achieves the objectives
of the rule unless DOE publishes an
explanation for doing otherwise, or the
selection of such an alternative is
inconsistent with law. In accordance
with 42 U.S.C. 6295(m), this final rule
establishes amended energy
conservation standards for microwave
ovens that are designed to achieve the
maximum improvement in energy
efficiency that DOE has determined to
be both technologically feasible and
economically justified, as required by
6295(o)(2)(A) and 6295(o)(3)(B). A full
discussion of the alternatives
considered by DOE is presented in
chapter 17 of the TSD for this final rule.
H. Review Under the Treasury and
General Government Appropriations
Act, 1999
Section 654 of the Treasury and
General Government Appropriations
Act, 1999 (Pub. L. 105–277) requires
Federal agencies to issue a Family
Policymaking Assessment for any rule
that may affect family well-being. This
rule would not have any impact on the
autonomy or integrity of the family as
an institution. Accordingly, DOE has
concluded that it is not necessary to
prepare a Family Policymaking
Assessment.
I. Review Under Executive Order 12630
Pursuant to E.O. 12630,
‘‘Governmental Actions and Interference
with Constitutionally Protected Property
Rights,’’ 53 FR 8859 (March 18, 1988),
DOE has determined that this rule
would not result in any takings that
might require compensation under the
Fifth Amendment to the U.S.
Constitution.
J. Review Under the Treasury and
General Government Appropriations
Act, 2001
Section 515 of the Treasury and
General Government Appropriations
Act, 2001 (44 U.S.C. 3516, note)
provides for Federal agencies to review
most disseminations of information to
the public under information quality
guidelines established by each agency
pursuant to general guidelines issued by
OMB. OMB’s guidelines were published
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at 67 FR 8452 (Feb. 22, 2002), and
DOE’s guidelines were published at 67
FR 62446 (Oct. 7, 2002). Pursuant to
OMB Memorandum M–19–15,
Improving Implementation of the
Information Quality Act (April 24,
2019), DOE published updated
guidelines which are available at
www.energy.gov/sites/prod/files/2019/
12/f70/DOE%20Final%20
Updated%20IQA%20Guidelines
%20Dec%202019.pdf. DOE has
reviewed this final rule under the OMB
and DOE guidelines and has concluded
that it is consistent with applicable
policies in those guidelines.
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K. Review Under Executive Order 13211
E.O. 13211, ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use,’’ 66
FR 28355 (May 22, 2001), requires
Federal agencies to prepare and submit
to OIRA at OMB, a Statement of Energy
Effects for any significant energy action.
A ‘‘significant energy action’’ is defined
as any action by an agency that
promulgates or is expected to lead to
promulgation of a final rule, and that (1)
is a significant regulatory action under
Executive Order 12866, or any successor
order; and (2) is likely to have a
significant adverse effect on the supply,
distribution, or use of energy, or (3) is
designated by the Administrator of
OIRA as a significant energy action. For
any significant energy action, the agency
must give a detailed statement of any
adverse effects on energy supply,
distribution, or use should the proposal
be implemented, and of reasonable
alternatives to the action and their
expected benefits on energy supply,
distribution, and use.
DOE has concluded that this
regulatory action, which sets forth
amended energy conservation standards
for microwave ovens, is not a significant
energy action because the standards are
not likely to have a significant adverse
effect on the supply, distribution, or use
of energy, nor has it been designated as
such by the Administrator at OIRA.
Accordingly, DOE has not prepared a
Statement of Energy Effects on this final
rule.
L. Information Quality
On December 16, 2004, OMB, in
consultation with the Office of Science
and Technology Policy (‘‘OSTP’’),
issued its Final Information Quality
Bulletin for Peer Review (‘‘the
Bulletin’’). 70 FR 2664 (Jan. 14, 2005).
The Bulletin establishes that certain
scientific information shall be peer
reviewed by qualified specialists before
it is disseminated by the Federal
Government, including influential
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scientific information related to agency
regulatory actions. The purpose of the
Bulletin is to enhance the quality and
credibility of the Government’s
scientific information. Under the
Bulletin, the energy conservation
standards rulemaking analyses are
‘‘influential scientific information,’’
which the Bulletin defines as ‘‘scientific
information the agency reasonably can
determine will have, or does have, a
clear and substantial impact on
important public policies or private
sector decisions.’’ 70 FR 2664, 2667.
In response to OMB’s Bulletin, DOE
conducted formal peer reviews of the
energy conservation standards
development process and the analyses
that are typically used and prepared a
report describing that peer review.65
Generation of this report involved a
rigorous, formal, and documented
evaluation using objective criteria and
qualified and independent reviewers to
make a judgment as to the technical/
scientific/business merit, the actual or
anticipated results, and the productivity
and management effectiveness of
programs and/or projects. Because
available data, models, and
technological understanding have
changed since 2007, DOE has engaged
with the National Academy of Sciences
to review DOE’s analytical
methodologies to ascertain whether
modifications are needed to improve
DOE’s analyses. DOE is in the process
of evaluating the resulting report.66
M. Congressional Notification
As required by 5 U.S.C. 801, DOE will
report to Congress on the promulgation
of this rule prior to its effective date.
The report will state that it has been
determined that the rule is not a ‘‘major
rule’’ as defined by 5 U.S.C. 804(2).
VII. Approval of the Office of the
Secretary
The Secretary of Energy has approved
publication of this final rule.
List of Subjects in 10 CFR Part 430
Administrative practice and
procedure, Confidential business
information, Energy conservation,
Household appliances, Imports,
Intergovernmental relations, Reporting
and recordkeeping requirements, and
Small businesses.
65 The 2007 ‘‘Energy Conservation Standards
Rulemaking Peer Review Report’’ is available at
energy.gov/eere/buildings/downloads/energyconservation-standards-rulemaking-peer-reviewreport-0 (Last accessed January 23, 2023).
66 The report is available at
www.nationalacademies.org/our-work/review-ofmethods-for-setting-building-and-equipmentperformance-standards.
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39959
Signing Authority
This document of the Department of
Energy was signed on April 20, 2023, by
Francisco Alejandro Moreno, Acting
Assistant Secretary for Energy Efficiency
and Renewable Energy, pursuant to
delegated authority from the Secretary
of Energy. That document with the
original signature and date is
maintained by DOE. For administrative
purposes only, and in compliance with
requirements of the Office of the Federal
Register, the undersigned DOE Federal
Register Liaison Officer has been
authorized to sign and submit the
document in electronic format for
publication, as an official document of
the Department of Energy. This
administrative process in no way alters
the legal effect of this document upon
publication in the Federal Register.
Signed in Washington, DC, on June 13,
2023.
Treena V. Garrett,
Federal Register Liaison Officer, U.S.
Department of Energy.
For the reasons set forth in the
preamble, DOE amends part 430 of
chapter II, subchapter D, of title 10 of
the Code of Federal Regulations, as set
forth below:
PART 430—ENERGY CONSERVATION
PROGRAM FOR CONSUMER
PRODUCTS
1. The authority citation for part 430
continues to read as follows:
■
Authority: 42 U.S.C. 6291–6309; 28 U.S.C.
2461 note.
2. Section 430.32 is amended by
revising paragraph (j)(3) to read as
follows:
■
§ 430.32 Energy and water conservation
standards and their compliance dates.
*
*
*
*
*
(j) * * *
(3) Microwave ovens:
(i) Microwave-only ovens and
countertop convection microwave ovens
manufactured on or after June 17, 2016,
and before June 22, 2026, shall have an
average standby power not more than
1.0 watt. Built-in and over-the-range
convection microwave ovens
manufactured on or after June 17, 2016,
and before June 22, 2026, shall have an
average standby power not more than
2.2 watts.
(ii) Microwave-only ovens and
countertop convection microwave ovens
manufactured on or after June 22, 2026,
shall have an average standby power not
more than 0.6 watts. Built-in and overthe-range convection microwave ovens
manufactured on or after June 22, 2026,
E:\FR\FM\20JNR2.SGM
20JNR2
39960
Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules and Regulations
shall have an average standby power not
more than 1.0 watt.
*
*
*
*
*
Note: The following letter will not appear
in the Code of Federal Regulations.
lotter on DSK11XQN23PROD with RULES2
U.S. Department of Justice
Antitrust Division
Jonathan S. Kanter
Assistant Attorney General
Main Justice Building
950 Pennsylvania Avenue NW
Washington, DC 20530–0001
(202) 514–2401/(202) 616–2645 (Fax)
XXXX XX, 2023
Ami Grace-Tardy
Assistant General Counsel for
Legislation, Regulation and Energy
Efficiency
U.S. Department of Energy
Washington, DC 20585
Ami.Grace-Tardy@hq.doe.gov
Dear Assistant General Counsel GraceTardy:
I am responding to your August 25,
2022 letter seeking the views of the
Attorney General about the potential
impact on competition of proposed
energy conservation standards for
VerDate Sep<11>2014
17:13 Jun 16, 2023
Jkt 259001
microwave ovens. Your request was
submitted under Section
325(o)(2)(B)(i)(V) of the Energy Policy
and Conservation Act, as amended
(EPCA), 42 U.S.C. 6295(o)(2)(B)(i)(V)
and 42 U.S.C. 6316(a), 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 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). The Assistant Attorney
General for the Antitrust Division has
authorized me, as the Policy Director
the Antitrust Division, to provide the
Antitrust Division’s views regarding the
potential impact on competition of
proposed energy conservation standards
on his behalf.
In conducting its analysis, the
Antitrust Division examines whether a
proposed standard may lessen
competition, for example, by
PO 00000
Frm 00050
Fmt 4701
Sfmt 9990
substantially limiting consumer choice
or increasing industry concentration. A
lessening of competition could result in
higher prices to manufacturers and
consumers. We have reviewed the
proposed standards contained in the
Supplemental Notice of Proposed
Rulemaking (87 FR 52282 August 24,
2022), and the related technical support
documents. We also reviewed the
transcript from the public meeting held
on October 11, 2022, and reviewed
public comments submitted by industry
members in response to DOE’s Request
for Information in this matter.
Based on the information currently
available, we do not believe that the
proposed energy conservation standards
for microwave ovens are likely to have
a significant adverse impact on
competition.
Sincerely,
David G.B. Lawrence,
Policy Director.
[FR Doc. 2023–12958 Filed 6–16–23; 8:45 am]
BILLING CODE 6450–01–P
E:\FR\FM\20JNR2.SGM
20JNR2
Agencies
[Federal Register Volume 88, Number 117 (Tuesday, June 20, 2023)]
[Rules and Regulations]
[Pages 39912-39960]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2023-12958]
[[Page 39911]]
Vol. 88
Tuesday,
No. 117
June 20, 2023
Part II
Department of Energy
-----------------------------------------------------------------------
10 CFR Part 430
Energy Conservation Program: Energy Conservation Standards for
Microwave Ovens; Final Rule
Federal Register / Vol. 88, No. 117 / Tuesday, June 20, 2023 / Rules
and Regulations
[[Page 39912]]
-----------------------------------------------------------------------
DEPARTMENT OF ENERGY
10 CFR Part 430
[EERE-2017-BT-STD-0023]
RIN 1904-AE00
Energy Conservation Program: Energy Conservation Standards for
Microwave Ovens
AGENCY: Office of Energy Efficiency and Renewable Energy, Department of
Energy.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Energy Policy and Conservation Act, as amended (``EPCA''),
prescribes energy conservation standards for various consumer products
and certain commercial and industrial equipment, including microwave
ovens. EPCA also requires the U.S. Department of Energy (``DOE'') to
periodically determine whether more stringent standards would be
technologically feasible and economically justified, and whether they
would result in significant energy savings. In this final rule, DOE is
adopting amended energy conservation standards for microwave ovens. It
has determined that the amended energy conservation standards for these
products would result in significant conservation of energy and are
technologically feasible and economically justified.
DATES: The effective date of this rule is August 21, 2023. Compliance
with the amended standards established for microwave ovens in this
final rule is required on and after June 22, 2026.
ADDRESSES: The docket for this rulemaking, which includes Federal
Register notices, public meeting attendee lists and transcripts,
comments, and other supporting documents/materials, is available for
review at www.regulations.gov. All documents in the docket are listed
in the www.regulations.gov index. However, not all documents listed in
the index may be publicly available, such as information that is exempt
from public disclosure.
The docket web page can be found at www.regulations.gov/docket/EERE-2017-BT-STD-0023. The docket web page contains instructions on how
to access all documents, including public comments, in the docket.
For further information on how to review the docket, contact the
Appliance and Equipment Standards Program staff at (202) 287-1445 or by
email: [email protected].
FOR FURTHER INFORMATION CONTACT: Dr. Carl Shapiro, U.S. Department of
Energy, Office of Energy Efficiency and Renewable Energy, Building
Technologies Office, EE-2J, 1000 Independence Avenue SW, Washington, DC
20585-0121. Telephone: (202) 287-5649. Email:
[email protected].
Ms. Celia Sher, U.S. Department of Energy, Office of the General
Counsel, GC-33, 1000 Independence Avenue SW., Washington, DC, 20585-
0121. Telephone: (202) 287-6122. Email: [email protected].
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Synopsis of the Final Rule
A. Benefits and Costs to Consumers
B. Impact on Manufacturers
C. National Benefits and Costs
D. Conclusion
II. Introduction
A. Authority
B. Background
1. Current Standards
2. History of Standards Rulemaking for Microwave Ovens
III. General Discussion
A. Scope of Coverage
B. Test Procedure
C. Technological Feasibility
1. General
2. Maximum Technologically Feasible Levels
D. Energy Savings
1. Determination of Savings
2. Significance of Savings
E. Economic Justification
1. Specific Criteria
a. Economic Impact on Manufacturers and Consumers
b. Savings in Operating Costs Compared To Increase in Price (LCC
and PBP)
c. Energy Savings
d. Lessening of Utility or Performance of Products
e. Impact of Any Lessening of Competition
f. Need for National Energy Conservation
g. Other Factors
2. Rebuttable Presumption
IV. Methodology and Discussion of Related Comments
1. Market and Technology Assessment
2. Product Classes
3. Technology Options
B. Screening Analysis
1. Screened-Out Technologies
2. Remaining Technologies
C. Engineering Analysis
1. Efficiency Analysis
a. Baseline Efficiency/Energy Use
b. Higher Efficiency Levels
2. Cost Analysis
3. Cost-Efficiency Results
D. Markups Analysis
E. Energy Use Analysis
F. Life-Cycle Cost and Payback Period Analysis
1. Product Cost
2. Installation Cost
3. Annual Energy Consumption
4. Energy Prices
5. Maintenance and Repair Costs
6. Product Lifetime
7. Discount Rates
8. Energy Efficiency Distribution in the No-New-Standards Case
9. Payback Period Analysis
G. Shipments Analysis
H. National Impact Analysis
1. Product Efficiency Trends
2. National Energy Savings
3. Net Present Value Analysis
I. Consumer Subgroup Analysis
J. Manufacturer Impact Analysis
1. Overview
2. Government Regulatory Impact Model and Key Inputs
a. Manufacturer Production Costs
b. Shipments Projections
c. Product and Capital Conversion Costs
d. Markup Scenarios
3. Discussion of MIA Comments
K. Emissions Analysis
1. Air Quality Regulations Incorporated in DOE's Analysis
L. Monetizing Emissions Impacts
1. Monetization of Greenhouse Gas Emissions
a. Social Cost of Carbon
b. Social Cost of Methane and Nitrous Oxide
2. Monetization of Other Emissions Impacts
M. Utility Impact Analysis
N. Employment Impact Analysis
V. Analytical Results and Conclusions
A. Trial Standard Levels
B. Economic Justification and Energy Savings
1. Economic Impacts on Individual Consumers
a. Life-Cycle Cost and Payback Period
b. Consumer Subgroup Analysis
c. Rebuttable Presumption Payback
2. Economic Impacts on Manufacturers
a. Industry Cash Flow Analysis Results
b. Direct Impacts on Employment
c. Impacts on Manufacturing Capacity
d. Impacts on Subgroups of Manufacturers
e. Cumulative Regulatory Burden
3. National Impact Analysis
a. Significance of Energy Savings
b. Net Present Value of Consumer Costs and Benefits
c. Indirect Impacts on Employment
4. Impact on Utility or Performance of Products
5. Impact of Any Lessening of Competition
6. Need of the Nation To Conserve Energy
7. Other Factors
8. Summary of Economic Impacts
C. Conclusion
1. Benefits and Burdens of TSLs Considered for Microwave Ovens
Standards
2. Annualized Benefits and Costs of the Adopted Standards
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Orders 12866 and 13563
B. Review Under the Regulatory Flexibility Act
C. Review Under the Paperwork Reduction Act
D. Review Under the National Environmental Policy Act of 1969
[[Page 39913]]
E. Review Under Executive Order 13132
F. Review Under Executive Order 12988
G. Review Under the Unfunded Mandates Reform Act of 1995
H. Review Under the Treasury and General Government
Appropriations Act, 1999
I. Review Under Executive Order 12630
J. Review Under the Treasury and General Government
Appropriations Act, 2001
K. Review Under Executive Order 13211
L. Information Quality
M. Congressional Notification
VII. Approval of the Office of the Secretary
I. Synopsis of the Final Rule
The Energy Policy and Conservation Act, Public Law 94-163, as
amended (``EPCA''),\1\ authorizes DOE to regulate the energy efficiency
of a number of consumer products and certain industrial equipment. (42
U.S.C. 6291-6317) Title III, Part B of EPCA \2\ established the Energy
Conservation Program for Consumer Products Other Than Automobiles. (42
U.S.C. 6291-6309) These products include microwave ovens, the subject
of this rulemaking.
---------------------------------------------------------------------------
\1\ All references to EPCA in this document refer to the statute
as amended through the Energy Act of 2020, Public Law 116-260 (Dec.
27, 2020), which reflect the last statutory amendments that impact
Parts A and A-1 of EPCA.
\2\ For editorial reasons, upon codification in the U.S. Code,
Part B was redesignated Part A.
---------------------------------------------------------------------------
Pursuant to EPCA, any new or amended energy conservation standard
must be designed to achieve the maximum improvement in energy
efficiency that DOE determines is technologically feasible and
economically justified. (42 U.S.C. 6295(o)(2)(A)) Furthermore, the new
or amended standard must result in significant conservation of energy.
(42 U.S.C. 6295(o)(3)(B)) EPCA also provides that not later than 6
years after issuance of any final rule establishing or amending a
standard, DOE must publish either a notice of determination that
standards for the product do not need to be amended, or a notice of
proposed rulemaking including new proposed energy conservation
standards (proceeding to a final rule, as appropriate). (42 U.S.C.
6295(m))
In accordance with these and other statutory provisions discussed
in this document, DOE is adopting amended energy conservation standards
for microwave ovens. The adopted standards, which are expressed in
watts (``W''), are shown in Table I.1. These standards apply to all
products listed in Table I.1 and manufactured in, or imported into, the
United States starting on June 22, 2026.
Table I.1--Energy Conservation Standards for Microwave Ovens (Compliance
Starting June 22, 2026)
------------------------------------------------------------------------
Maximum allowable average
Product class standby power, (watts)
------------------------------------------------------------------------
PC 1: Microwave-Only Ovens and 0.6 W
Countertop Convection Microwave Ovens.
PC 2: Built-In and Over-the-Range 1.0 W
Convection Microwave Ovens.
------------------------------------------------------------------------
A. Benefits and Costs to Consumers
Table I.2 summarizes DOE's evaluation of the economic impacts of
the adopted standards on consumers of microwave ovens, as measured by
the average life-cycle cost (``LCC'') savings and the simple payback
period (``PBP'').\3\ The average LCC savings are positive for all
product classes, and the PBP is less than the average lifetime of
microwave ovens, which is estimated to be 10.78 years (see section IV.F
of this document).
---------------------------------------------------------------------------
\3\ The average LCC savings refer to consumers that are affected
by a standard and are measured relative to the efficiency
distribution in the no-new-standards case, which depicts the market
in the compliance year in the absence of new or amended standards
(see section [IV.F.9] of this document). The simple PBP, which is
designed to compare specific efficiency levels, is measured relative
to the baseline product (see section IV.C of this document).
Table I.2--Impacts of Adopted Energy Conservation Standards on Consumers
of Microwave Ovens
------------------------------------------------------------------------
Average LCC Simple
Product class savings payback
(2021$) period (years)
------------------------------------------------------------------------
PC 1: Microwave-Only Ovens and 0.99 1.3
Countertop Convection Microwave Ovens..
PC 2: Built-In and Over-the-Range 0.83 0.8
Convection Microwave Ovens.............
------------------------------------------------------------------------
DOE's analysis of the impacts of the adopted standards on consumers
is described in section IV.F of this document.
B. Impact on Manufacturers
The industry net present value (``INPV'') is the sum of the
discounted cash flows to the industry from the base year through the
end of the analysis period (2023-2055). Using a real discount rate of
8.5 percent, DOE estimates that the INPV for manufacturers of microwave
ovens in the case without amended standards is $1,426 million in 2021
dollars. Under the adopted standards, DOE estimates the change in INPV
to range from -$37.2 million, which represents a change of -2.6
percent, to no change in INPV. In order to bring products into
compliance with amended standards, it is estimated that industry will
incur total conversion costs of $46.1 million.
DOE's analysis of the impacts of the adopted standards on
manufacturers is described in sections IV.J and V.B.2 of this document.
C. National Benefits and Costs 4
---------------------------------------------------------------------------
\4\ All monetary values in this document are expressed in 2021
dollars. and, where appropriate, are discounted to 2023 unless
explicitly stated otherwise.
---------------------------------------------------------------------------
DOE's analyses indicate that the adopted energy conservation
standards for microwave ovens would save a significant amount of
energy. Relative to the case without amended standards, the lifetime
energy savings for microwave ovens purchased in the 30-year period that
begins in the anticipated year of compliance with the amended standards
(2026-2055), amount to 0.06 quadrillion British thermal units
(``Btu''), or quads.\5\ This represents a savings of 19 percent
relative to the energy use of these products in the case without
amended standards (referred to as the ``no-new-standards case'').
---------------------------------------------------------------------------
\5\ The quantity refers to full-fuel-cycle (FFC) energy savings.
FFC energy savings includes the energy consumed in extracting,
processing, and transporting primary fuels (i.e., coal, natural gas,
petroleum fuels), and, thus, presents a more complete picture of the
impacts of energy efficiency standards. For more information on the
FFC metric, see section IV.H.1 of this document.
---------------------------------------------------------------------------
[[Page 39914]]
The cumulative net present value (``NPV'') of total consumer
benefits of the standards for microwave ovens ranges from $0.16 (at a
7-percent discount rate) to $0.35 (at a 3-percent discount rate). This
NPV expresses the estimated total value of future operating-cost
savings minus the estimated increased product costs for microwave ovens
purchased in 2026-2055.
In addition, the adopted standards for microwave ovens are
projected to yield significant environmental benefits. DOE estimates
that the standards will result in cumulative emission reductions (over
the same period as for energy savings) of 1.87 million metric tons
(``Mt'') \6\ of carbon dioxide (``CO2''), 0.85 thousand tons
of sulfur dioxide (``SO2''), 2.88 thousand tons of nitrogen
oxides (``NOX''), 12.64 thousand tons of methane
(``CH4''), 0.02 thousand tons of nitrous oxide
(``N2O''), and 0.005 tons of mercury (``Hg'').\7\ The
estimated cumulative reduction in CO2 emissions through 2030
amounts to 0.10 Mt, which is equivalent to the emissions resulting from
the annual electricity use of more than 19 thousand homes.
---------------------------------------------------------------------------
\6\ A metric ton is equivalent to 1.1 short tons. Results for
emissions other than CO2 are presented in short tons.
\7\ DOE calculated emissions reductions relative to the no-new-
standards-case, which reflects key assumptions in the Annual Energy
Outlook 2022 (``AEO2022''). AEO2022 represents current Federal and
State legislation and final implementation of regulations as of the
time of its preparation. See section IV.K of this document for
further discussion of AEO2022 assumptions that effect air pollutant
emissions.
---------------------------------------------------------------------------
DOE estimates the value of climate benefits from a reduction in
greenhouse gases (GHG) using four different estimates of the social
cost of CO2 (``SC-CO2''), the social cost of
methane (``SC-CH4''), and the social cost of nitrous oxide
(``SC-N2O''). Together these represent the social cost of
GHG (SC-GHG). DOE used interim SC-GHG values developed by an
Interagency Working Group on the Social Cost of Greenhouse Gases
(IWG).\8\ The derivation of these values is discussed in section IV.L
of this document. For presentational purposes, the climate benefits
associated with the average SC-GHG at a 3-percent discount rate are
estimated to be $0.10 billion. DOE does not have a single central SC-
GHG point estimate and DOE emphasizes the importance and value of
considering the benefits calculated using all four sets of SC-GHG
estimates.\9\
---------------------------------------------------------------------------
\8\ See Interagency Working Group on Social Cost of Greenhouse
Gases, Technical Support Document: Social Cost of Carbon, Methane,
and Nitrous Oxide. Interim Estimates Under Executive Order 13990,
Washington, DC, February 2021 (``February 2021 SC-GHG TSD'').
www.whitehouse.gov/wp-content/uploads/2021/02/TechnicalSupportDocument_SocialCostofCarbonMethaneNitrousOxide.pdf.
\9\ On March 16, 2022, the Fifth Circuit Court of Appeals (No.
22-30087) granted the Federal government's emergency motion for stay
pending appeal of the February 11, 2022, preliminary injunction
issued in Louisiana v. Biden, No. 21-cv-1074-JDC-KK (W.D. La.). As a
result of the Fifth Circuit's order, the preliminary injunction is
no longer in effect, pending resolution of the Federal government's
appeal of that injunction or a further court order. Among other
things, the preliminary injunction enjoined the defendants in that
case from ``adopting, employing, treating as binding, or relying
upon'' the interim estimates of the social cost of greenhouse
gases--which were issued by the Interagency Working Group on the
Social Cost of Greenhouse Gases on February 26, 2021--to monetize
the benefits of reducing greenhouse gas emissions. As reflected in
this rule, DOE has reverted to its approach prior to the injunction
and presents monetized benefits where appropriate and permissible
under law.
---------------------------------------------------------------------------
DOE estimated the monetary health benefits of SO2 and
NOX emissions reductions, using benefit-per-ton estimates
from the scientific literature, as discussed in section IV.L of this
document. DOE estimated the present value of the health benefits would
be $0.07 billion using a 7-percent discount rate, and $0.17 billion
using a 3-percent discount rate.\10\ DOE is currently only monetizing
(for SO2 and NOX) PM2.5 precursor
health benefits and (for NOX) ozone precursor health
benefits, but will continue to assess the ability to monetize other
effects, such as health benefits, from reductions in direct
PM2.5 emissions.
---------------------------------------------------------------------------
\10\ DOE estimates the economic value of these emissions
reductions resulting from the considered TSLs for the purpose of
complying with the requirements of Executive Order 12866.
---------------------------------------------------------------------------
Table I.3 summarizes the monetized benefits and costs expected to
result from the amended standards for microwave ovens. There are other
important unquantified effects, including certain unquantified climate
benefits, unquantified public health benefits from the reduction of
toxic air pollutants and other emissions, unquantified energy security
benefits, and distributional effects, among others.
Table I.3--Summary of Monetized Benefits and Costs of Adopted Energy
Conservation Standards for Microwave Ovens
------------------------------------------------------------------------
Billion $2021
------------------------------------------------------------------------
3% discount rate
------------------------------------------------------------------------
Consumer Operating Cost Savings......................... 0.43
Climate Benefits *...................................... 0.10
Health Benefits **...................................... 0.17
---------------
Total Benefits [dagger]............................. 0.70
Consumer Incremental Product Costs [Dagger]............. 0.08
---------------
Net Benefits........................................ 0.62
------------------------------------------------------------------------
7% discount rate
------------------------------------------------------------------------
Consumer Operating Cost Savings......................... 0.21
Climate Benefits * (3% discount rate)................... 0.10
Health Benefits **...................................... 0.07
---------------
Total Benefits[dagger].............................. 0.38
Consumer Incremental Product Costs [Dagger]............. 0.05
---------------
Net Benefits........................................ 0.34
------------------------------------------------------------------------
Note: This table presents the costs and benefits associated with
microwave ovens shipped in 2026-2055. These results include benefits
to consumers which accrue after 2055 from the products shipped in 2026-
2055.
[[Page 39915]]
* Climate benefits are calculated using four different estimates of the
social cost of carbon (SC-CO2), methane (SC-CH4), and nitrous oxide
(SC-N2O) (model average at 2.5-percent, 3-percent, and 5-percent
discount rates; 95th percentile at 3-percent discount rate) (see
section IV.L of this document). Together these represent the global SC-
GHG. For presentational purposes of this table, the climate benefits
associated with the average SC-GHG at a 3-percent discount rate are
shown, but DOE does not have a single central SC-GHG point estimate.
On March 16, 2022, the Fifth Circuit Court of Appeals (No. 22-30087)
granted the Federal government's emergency motion for stay pending
appeal of the February 11, 2022, preliminary injunction issued in
Louisiana v. Biden, No. 21-cv-1074-JDC-KK (W.D. La.). As a result of
the Fifth Circuit's order, the preliminary injunction is no longer in
effect, pending resolution of the Federal government's appeal of that
injunction or a further court order. Among other things, the
preliminary injunction enjoined the defendants in that case from
``adopting, employing, treating as binding, or relying upon'' the
interim estimates of the social cost of greenhouse gases--which were
issued by the Interagency Working Group on the Social Cost of
Greenhouse Gases on February 26, 2021--to monetize the benefits of
reducing greenhouse gas emissions. As reflected in this rule, DOE has
reverted to its approach prior to the injunction and presents
monetized benefits where appropriate and permissible under law.
** Health benefits are calculated using benefit-per-ton values for NOX
and SO2. DOE is currently only monetizing (for SO2 and NOX) PM2.5
precursor health benefits and (for NOX) ozone precursor health
benefits, but will continue to assess the ability to monetize other
effects, such as health benefits, from reductions in direct PM2.5
emissions. See section IV.L of this document for more details.
[dagger] Total and net benefits include those consumer, climate, and
health benefits that can be quantified and monetized. For presentation
purposes, total and net benefits for both the 3-percent and 7-percent
cases are presented using the average SC-GHG with 3-percent discount
rate.
[Dagger] Costs include incremental equipment costs as well as
installation costs.
The benefits and costs of the proposed standards can also be
expressed in terms of annualized values. The monetary values for the
total annualized net benefits are (1) the reduced consumer operating
costs, minus (2) the increase in product purchase prices and
installation costs, plus (3) the value of climate and health benefits
of emission reductions, all annualized.\11\
---------------------------------------------------------------------------
\11\ To convert the time-series of costs and benefits into
annualized values, DOE calculated a present value in 2022, the year
used for discounting the NPV of total consumer costs and savings.
For the benefits, DOE calculated a present value associated with
each year's shipments in the year in which the shipments occur
(e.g., 2020 or 2030), and then discounted the present value from
each year to 2022. Using the present value, DOE then calculated the
fixed annual payment over a 30-year period, starting in the
compliance year, that yields the same present value.
---------------------------------------------------------------------------
The national operating cost savings are domestic private U.S.
consumer monetary savings that occur as a result of purchasing the
covered products and are measured for the lifetime of microwave ovens
shipped in 2026-2055. The benefits associated with reduced emissions
achieved as a result of the adopted standards are also calculated based
on the lifetime of microwave ovens shipped in 2026-2055. Total benefits
for both the 3-percent and 7-percent cases are presented using the
average GHG social costs with 3-percent discount rate. Estimates of SC-
GHG values are presented for all four discount rates in section V.B.8
of this document.
Table I.4 presents the total estimated monetized benefits and costs
associated with the standards adopted in this rule, expressed in terms
of annualized values. The results under the primary estimate are as
follows.
Using a 7-percent discount rate for consumer benefits and costs and
health benefits from reduced NOX and SO2
emissions, and the 3-percent discount rate case for climate benefits
from reduced GHG emissions, the estimated cost of the standards adopted
in this rule is $4.3 million per year in increased equipment costs,
while the estimated annual benefits are $19.5 million in reduced
equipment operating costs, $5.2 million in climate benefits, and $6.9
million in health benefits. In this case, the net benefit would amount
to $27.3 million per year.
Using a 3-percent discount rate for all benefits and costs, the
estimated cost of the amended standards is $4.3 million per year in
increased equipment costs, while the estimated annual benefits are
$23.5 million in reduced operating costs, $5.2 million in climate
benefits, and $9.2 million in health benefits. In this case, the net
benefit would amount to $33.5 million per year.
Table I.4--Annualized Benefits and Costs of Adopted Standards for Microwave Ovens
----------------------------------------------------------------------------------------------------------------
Million 2021 $/year
-----------------------------------------------
Low-net- High-net-
Primary benefits benefits
estimate estimate estimate
----------------------------------------------------------------------------------------------------------------
3% discount rate
----------------------------------------------------------------------------------------------------------------
Consumer Operating Cost Savings................................. 23.5 22.2 25.0
Climate Benefits *.............................................. 5.2 5.1 5.4
Health Benefits **.............................................. 9.2 9.0 9.4
-----------------------------------------------
Total Benefits [dagger]..................................... 37.9 36.3 39.8
Consumer Incremental Product Costs [Dagger]..................... 4.3 4.3 4.2
-----------------------------------------------
Net Benefits................................................ 33.5 31.9 35.6
----------------------------------------------------------------------------------------------------------------
7% discount rate
----------------------------------------------------------------------------------------------------------------
Consumer Operating Cost Savings................................. 19.5 18.6 20.5
Climate Benefits * (3% discount rate)........................... 5.2 5.1 5.4
Health Benefits **.............................................. 6.9 6.7 7.1
-----------------------------------------------
Total Benefits [dagger]..................................... 31.6 30.4 32.9
Consumer Incremental Product Costs [Dagger]..................... 4.3 4.3 4.2
-----------------------------------------------
[[Page 39916]]
Net Benefits................................................ 27.3 26.1 28.7
----------------------------------------------------------------------------------------------------------------
Note: This table presents the costs and benefits associated with microwave ovens shipped in 2026-2055. These
results include benefits to consumers which accrue after 2055 from the products shipped in 2026-2055. The
Primary, Low Net Benefits, and High Net Benefits Estimates utilize projections of energy prices from the
AEO2022 Reference case, Low Economic Growth case, and High Economic Growth case, respectively. In addition,
incremental equipment costs reflect a medium decline rate in the Primary Estimate, a low decline rate in the
Low Net Benefits Estimate, and a high decline rate in the High Net Benefits Estimate. The methods used to
derive projected price trends are explained in sections IV.F.1 and IV.H.1 of this document. Note that the
Benefits and Costs may not sum to the Net Benefits due to rounding.
* Climate benefits are calculated using four different estimates of the global SC-GHG (see section IV.L of this
document). For presentational purposes of this table, the climate benefits associated with the average SC-GHG
at a 3-percent discount rate are shown, but DOE does not have a single central SC-GHG point estimate, and it
emphasizes the importance and value of considering the benefits calculated using all four sets of SC-GHG
estimates. On March 16, 2022, the Fifth Circuit Court of Appeals (No. 22-30087) granted the Federal
government's emergency motion for stay pending appeal of the February 11, 2022, preliminary injunction issued
in Louisiana v. Biden, No. 21-cv-1074-JDC-KK (W.D. La.). As a result of the Fifth Circuit's order, the
preliminary injunction is no longer in effect, pending resolution of the Federal government's appeal of that
injunction or a further court order. Among other things, the preliminary injunction enjoined the defendants in
that case from ``adopting, employing, treating as binding, or relying upon'' the interim estimates of the
social cost of greenhouse gases--which were issued by the Interagency Working Group on the Social Cost of
Greenhouse Gases on February 26, 2021--to monetize the benefits of reducing greenhouse gas emissions. As
reflected in this rule, DOE has reverted to its approach prior to the injunction and presents monetized
benefits where appropriate and permissible under law.
** Health benefits are calculated using benefit-per-ton values for NOX and SO2. DOE is currently only monetizing
(for SO2 and NOX) PM2.5 precursor health benefits and (for NOX) ozone precursor health benefits, but will
continue to assess the ability to monetize other effects such as health benefits from reductions in direct
PM2.5 emissions. See section IV.L of this document for more details.
[dagger] Total benefits for both the 3-percent and 7-percent cases are presented using the average SC-GHG with 3-
percent discount rate.
[Dagger] Costs include incremental equipment costs as well as installation costs.
DOE's analysis of the national impacts of the adopted standards is
described in sections IV.H, IV.K, and IV.L of this document.
D. Conclusion
DOE concludes that the standards adopted in this final rule
represent the maximum improvement in energy efficiency that is
technologically feasible and economically justified, and would result
in the significant conservation of energy. Specifically, with regards
to technological feasibility, products achieving these standard levels
are already commercially available for all product classes covered by
this proposal. As for economic justification, DOE's analysis shows that
the benefits of the standards exceed, to a great extent, the burdens of
the standards.
Using a 7-percent discount rate for consumer benefits and costs and
NOX and SO2 reduction benefits, and a 3-percent
discount rate case for GHG social costs, the estimated cost of the
standards for microwave ovens is $4.3 million per year in increased
product costs, while the estimated annual benefits are $19.5 million in
reduced product operating costs, $5.2 million in climate benefits, and
$6.9 million in health benefits. The net benefit amounts to $27.3
million per year.
The significance of energy savings offered by a new or amended
energy conservation standard cannot be determined without knowledge of
the specific circumstances surrounding a given rulemaking.\12\ For
example, some covered products and equipment have most of their energy
consumption occur during periods of peak energy demand. The impacts of
these products on the energy infrastructure can be more pronounced than
products with relatively constant demand. Accordingly, DOE evaluates
the significance of energy savings on a case-by-case basis.
---------------------------------------------------------------------------
\12\ Procedures, Interpretations, and Policies for Consideration
in New or Revised Energy Conservation Standards and Test Procedures
for Consumer Products and Commercial/Industrial Equipment, 86 FR
70892, 70901 (Dec. 13, 2021).
---------------------------------------------------------------------------
As previously mentioned, the standards are projected to result in
estimated national energy savings of 0.06 quads in FFC energy use and
emissions, the equivalent of the primary annual energy use of 1.6
million homes. In addition, the standards are projected to reduce
CO2 emissions by 1.87 Mt. Based on these findings, DOE has
determined the energy savings from the standard levels adopted in this
final rule are ``significant'' within the meaning of 42 U.S.C.
6295(o)(3)(B). A more detailed discussion of the basis for these
conclusions is contained in the remainder of this document and the
accompanying final rule technical support document (``TSD'').
II. Introduction
The following section briefly discusses the statutory authority
underlying this final rule, as well as some of the relevant historical
background related to the establishment of standards for microwave
ovens.
A. Authority
EPCA authorizes DOE to regulate the energy efficiency of a number
of consumer products and certain industrial equipment. Title III, Part
B of EPCA established the Energy Conservation Program for Consumer
Products Other Than Automobiles. These products include microwave
ovens, the subject of this document. (42 U.S.C. 6292(a)(10)) EPCA
prescribed energy conservation standards for these products, and
directs DOE to conduct future rulemakings to determine whether to amend
these standards. (42 U.S.C. 6295(h)(2)(A)-(B)) EPCA further provides
that, not later than 6 years after the issuance of any final rule
establishing or amending a standard, DOE must publish either a notice
of determination that standards for the product do not need to be
amended, or a NOPR including new proposed energy conservation standards
(proceeding to a final rule, as appropriate). (42 U.S.C. 6295(m)(1))
The energy conservation program under EPCA consists essentially of
four parts: (1) testing, (2) labeling, (3) the establishment of Federal
energy conservation standards, and (4) certification and enforcement
procedures. Relevant provisions of EPCA specifically include
definitions (42 U.S.C. 6291), test procedures (42 U.S.C. 6293),
labeling provisions (42 U.S.C. 6294), energy conservation
[[Page 39917]]
standards (42 U.S.C. 6295), and the authority to require information
and reports from manufacturers (42 U.S.C. 6296).
Federal energy efficiency requirements for covered products
established under EPCA generally supersede State laws and regulations
concerning energy conservation testing, labeling, and standards. (42
U.S.C. 6297(a)-(c)) DOE may, however, grant waivers of Federal
preemption in limited instances for particular State laws or
regulations, in accordance with the procedures and other provisions set
forth under EPCA. (See 42 U.S.C. 6297(d))
Subject to certain criteria and conditions, DOE is required to
develop test procedures to measure the energy efficiency, energy use,
or estimated annual operating cost of each covered product. (42 U.S.C.
6295(o)(3)(A) and 42 U.S.C. 6295(r)) Manufacturers of covered products
must use the prescribed DOE test procedure as the basis for certifying
to DOE that their products comply with the applicable energy
conservation standards adopted under EPCA and when making
representations to the public regarding the energy use or efficiency of
those products. (42 U.S.C. 6293(c) and 6295(s)) Similarly, DOE must use
these test procedures to determine whether the products comply with
standards adopted pursuant to EPCA. (42 U.S.C. 6295(s)) The DOE test
procedures for microwave ovens appear at title 10 of the Code of
Federal Regulations (``CFR'') Sec. 430.23(i) and 10 CFR part 430,
subpart B, appendix I (``appendix I'').
DOE must follow specific statutory criteria for prescribing new or
amended standards for covered products, including microwave ovens. Any
new or amended standard for a covered product must be designed to
achieve the maximum improvement in energy efficiency that the Secretary
of Energy determines is technologically feasible and economically
justified. (42 U.S.C. 6295(o)(2)(A) and 42 U.S.C. 6295(o)(3)(B))
Furthermore, DOE may not adopt any standard that would not result in
the significant conservation of energy. (42 U.S.C. 6295(o)(3))
Moreover, DOE may not prescribe a standard (1) for certain products,
including microwave ovens, if no test procedure has been established
for the product, or (2) if DOE determines by rule that the standard is
not technologically feasible or economically justified. (42 U.S.C.
6295(o)(3)(A)-(B)) In deciding whether a proposed standard is
economically justified, DOE must determine whether the benefits of the
standard exceed its burdens. (42 U.S.C. 6295(o)(2)(B)(i)) DOE must make
this determination after receiving comments on the proposed standard,
and by considering, to the greatest extent practicable, the following
seven statutory factors:
(1) The economic impact of the standard on manufacturers and
consumers of the products subject to the standard;
(2) The savings in operating costs throughout the estimated average
life of the covered products in the type (or class) compared to any
increase in the price, initial charges, or maintenance expenses for the
covered products that are likely to result from the standard;
(3) The total projected amount of energy (or as applicable, water)
savings likely to result directly from the standard;
(4) Any lessening of the utility or the performance of the covered
products likely to result from the standard;
(5) The impact of any lessening of competition, as determined in
writing by the Attorney General, that is likely to result from the
standard;
(6) The need for national energy and water conservation; and
(7) Other factors the Secretary of Energy (``Secretary'') considers
relevant. (42 U.S.C. 6295(o)(2)(B)(i)(I)-(VII))
Further, EPCA, as codified, establishes a rebuttable presumption
that a standard is economically justified if the Secretary finds that
the additional cost to the consumer of purchasing a product complying
with an energy conservation standard level will be less than three
times the value of the energy savings during the first year that the
consumer will receive as a result of the standard, as calculated under
the applicable test procedure. (42 U.S.C. 6295(o)(2)(B)(iii))
EPCA, as codified, also contains what is known as an ``anti-
backsliding'' provision, which prevents the Secretary from prescribing
any amended standard that either increases the maximum allowable energy
use or decreases the minimum required energy efficiency of a covered
product. (42 U.S.C. 6295(o)(1)) Also, the Secretary may not prescribe
an amended or new standard if interested persons have established by a
preponderance of the evidence that the standard is likely to result in
the unavailability in the United States in any covered product type (or
class) of performance characteristics (including reliability),
features, sizes, capacities, and volumes that are substantially the
same as those generally available in the United States. (42 U.S.C.
6295(o)(4))
Additionally, EPCA specifies requirements when promulgating an
energy conservation standard for a covered product that has two or more
subcategories. DOE must specify a different standard level for a type
or class of products that has the same function or intended use if DOE
determines that products within such group (A) consume a different kind
of energy from that consumed by other covered products within such type
(or class); or (B) have a capacity or other performance-related feature
which other products within such type (or class) do not have and such
feature justifies a higher or lower standard. (42 U.S.C. 6295(q)(1)) In
determining whether a performance-related feature justifies a different
standard for a group of products, DOE must consider such factors as the
utility to the consumer of such a feature and other factors DOE deems
appropriate. Id. Any rule prescribing such a standard must include an
explanation of the basis on which such higher or lower level was
established. (42 U.S.C. 6295(q)(2))
Finally, pursuant to the amendments contained in the Energy
Independence and Security Act of 2007 (EISA 2007), Public Law 110-140,
any final rule for new or amended energy conservation standards
promulgated after July 1, 2010, is required to address standby mode and
off mode energy use. (42 U.S.C. 6295(gg)(3)) Specifically, when DOE
adopts a standard for a covered product after that date, it must, if
justified by the criteria for adoption of standards under EPCA (42
U.S.C. 6295(o)), incorporate standby mode and off mode energy use into
a single standard, or, if that is not feasible, adopt a separate
standard for such energy use for that product. (42 U.S.C.
6295(gg)(3)(A)-(B))
B. Background
1. Current Standards
In a final rule published on June 17, 2013 (``June 2013 Final
Rule''), DOE prescribed the current energy conservation standards for
microwave ovens manufactured on and after June 17, 2016. 78 FR 36316.
These standards are set forth in DOE's regulations at 10 CFR
430.32(j)(3) and are repeated in Table II.1.
[[Page 39918]]
Table II.1--Federal Energy Conservation Standards for Microwave Ovens
------------------------------------------------------------------------
Maximum allowable average
Product class standby power
------------------------------------------------------------------------
Microwave-Only Ovens and Countertop 1.0 W.
Convection Microwave Ovens.
Built-In and Over-the-Range Convection 2.2 W.
Microwave Ovens.
------------------------------------------------------------------------
2. History of Standards Rulemaking for Microwave Ovens
EPCA prescribed an energy conservation standard for kitchen ranges
and ovens, and directed DOE to conduct two cycles of rulemakings to
determine whether to amend standards for these products. (42 U.S.C.
6295(h)(2)(A)-(B)) DOE completed the first of these rulemaking cycles
by publishing a final rule on September 8, 1998, that codified the
prescriptive design standard for gas cooking products established in
EPCA, but found that no standards were justified for electric cooking
products, including microwave ovens, at that time. 63 FR 48038, 48053-
48054. DOE completed the second rulemaking cycle and published a final
rule on April 8, 2009, in which it determined, among other things, that
standards for microwave oven active mode energy use were not
economically justified. 74 FR 16040.
DOE published the June 2013 Final Rule, adopting energy
conservation standards for microwave ovens. 78 FR 36316. In the June
2013 Final Rule, DOE maintained its prior determination that active
mode standards are not warranted for microwave ovens and prescribed
energy conservation standards that address the standby and off mode
energy use of microwave ovens. 78 FR 36316, 36317.
In support of the present review of the microwave oven energy
conservation standards, DOE published an early assessment request for
information on August 13, 2019, which identified various issues on
which DOE sought comment to inform its determination of whether the
standards need to be amended. 84 FR 39980.
DOE subsequently published a notice of proposed determination
(``NOPD'') on August 12, 2021, in which DOE initially determined that
current standards for microwave ovens do not need to be amended. 86 FR
44298. (``August 2021 NOPD'') In the August 2021 NOPD, DOE tentatively
determined that there are technology options that would improve the
efficiency of microwave ovens. 86 FR 44298, 44310. Based on the
analysis conducted for the August 2021 NOPD, DOE estimated that amended
standards for microwave oven standby power at the maximum
technologically feasible (``max-tech'') level would result in 0.1 quads
of energy saved over a 30-year period (representing an estimated 8
percent reduction in site energy use of microwave ovens). 86 FR 44298,
44310.
In evaluating the significance of the estimated energy savings for
the August 2021 NOPD, DOE applied a two-part numeric threshold test
that was then applicable under section 6(b) of appendix A to 10 CFR
part 430 subpart C (Jan. 1, 2021 edition). Specifically, the threshold
required that an energy conservation standard result in a 0.30 quads
reduction in site energy use over a 30-year analysis period or a 10-
percent reduction in site energy use over that same period. See 85 FR
8626, 8670 (Feb. 14, 2020). In the August 2021 NOPD, DOE stated that
the estimated site energy savings at the max-tech level was under the
0.3-quads/10-percent threshold and tentatively determined that amended
energy conservation standards for microwave oven standby power would
not result in significant conservation of energy. 86 FR 44298, 44310.
DOE also noted that the two-part numeric threshold was under
reconsideration. 86 FR 44298, 44302.
On December 13, 2021, DOE published in the Federal Register a final
rule that amended appendix A to 10 CFR part 430 subpart C (``appendix
A''). 86 FR 70892 (``December 2021 Final Rule''). The December 20201
Final Rule, in part, removed the numeric threshold in section 6(b) of
appendix A for determining when the significant energy savings
criterion is met, reverting to DOE's prior practice of making such
determinations on a case-by-case basis. 86 FR 70892.
After the publication of the NOPD, DOE conducted investigative
testing and manufacturer discussions, and updated the engineering
analysis to be used in a subsequently published supplemental notice of
proposed rulemaking (``SNOPR'') on August 24, 2022. 87 FR 52282.
(``August 2022 SNOPR'') In the August 2022 SNOPR, DOE revised the
efficiency levels, manufacturer selling price (``MSP'')-efficiency
relationships, and LCC and PBP analyses to evaluate the economic
impacts of potential energy conservation standards for microwave ovens
on individual consumers. The amended energy conservation standards for
microwave ovens proposed in the August 2022 SNOPR are shown in Table
II.2. DOE requested comment on these proposed standards and associated
analyses and results.
Table II.2--August 2022 SNOPR Proposed Energy Conservation Standards for
Microwave Ovens
------------------------------------------------------------------------
Maximum allowable average
Product class standby power (watts)
------------------------------------------------------------------------
PC 1: Microwave-Only Ovens and 0.6 W.
Countertop Convection Microwave Ovens.
PC 2: Built-In and Over-the-Range 1.0 W.
Convection Microwave Ovens.
------------------------------------------------------------------------
DOE held a public meeting on October 11, 2022, to solicit feedback
from stakeholders concerning the August 2022 SNOPR, and received 5
comments in response to the August 2022 SNOPR from the interested
parties listed in Table II.3.
Table II.3--August 2022 SNOPR Written Comments
----------------------------------------------------------------------------------------------------------------
Comment number
Commenter(s) Abbreviation in the docket Commenter type
----------------------------------------------------------------------------------------------------------------
Appliance Standards Awareness Project, The Joint Commenters...... 31 Efficiency Organizations.
American Council for an Energy-
Efficient Economy, Consumer Federation
of America, National Consumer Law
Center, Natural Resources Defense
Council, Northwest Energy Efficiency
Alliance.
Association of Home Appliance AHAM...................... 28 Trade Association.
Manufacturers.
Center for Climate and Energy Solutions, C2ES...................... 29 Efficiency Organizations.
Institute for Policy Integrity at New
York University School of Law, Natural
Resources Defense Council, Sierra Club,
Union of Concerned Scientists,
Institute for Policy Integrity.
[[Page 39919]]
Whirlpool Corporation................... Whirlpool................. 30 Manufacturer.
----------------------------------------------------------------------------------------------------------------
A parenthetical reference at the end of a comment quotation or
paraphrase provides the location of the item in the public record.\13\
To the extent that interested parties have provided written comments
that are substantively consistent with any oral comments provided
during the October 11, 2022 webinar, DOE cites the written comments
throughout this final rule. Any oral comments provided during the
webinar that are not substantively addressed by written comments are
summarized and cited separately throughout this final rule.
---------------------------------------------------------------------------
\13\ The parenthetical reference provides a reference for
information located in the docket of DOE's rulemaking to develop
energy conservation standards for microwave ovens. (Docket No. EERE-
2017-BT-STD-0023, which is maintained at www.regulations.gov). The
references are arranged as follows: (commenter name, comment docket
ID number, page of that document).
---------------------------------------------------------------------------
III. General Discussion
DOE developed this final rule after considering oral and written
comments, data, and information from interested parties that represent
a variety of interests. The following discussion addresses issues
raised by these commenters.
A. Scope of Coverage
This final rule covers those consumer products that meet the
definition of ``microwave oven'' as codified at 10 CFR 430.2, which
defines ``microwave oven'' as a category of cooking products which is a
household cooking appliance consisting of a compartment designed to
cook or heat food by means of microwave energy, including microwave
ovens with or without thermal elements designed for surface browning of
food and convection microwave ovens. This includes any microwave
oven(s) component of a combined cooking product. Any product meeting
the definition of microwave oven is included in DOE's scope of
coverage.
For this final rule, DOE considered the two product classes of
microwave ovens prescribed in the current energy conservation
standards: (1) Microwave-Only Ovens and Countertop Convection Microwave
Ovens, and (2) Built-In and Over-the-Range Convection Microwave Ovens.
For these two classes of microwave ovens, DOE's current test
procedure measures the energy consumption in standby mode and off mode
only. Consequently, DOE's current energy conservation standards for
microwave ovens are also expressed in terms of standby mode and off
mode power. There are currently no active mode energy conservation
standards; nor is there a prescribed test procedure for measuring the
active mode energy use or efficiency (e.g., cooking efficiency) of
microwave ovens.
The Joint Commenters commented that adopting a standard for active
mode energy consumption could achieve ``significantly greater'' savings
than proposed standby power standards, and that DOE should develop a
test procedure and standards for active mode power consumption. (Joint
Commenters, No. 31 at p. 2) DOE previously rejected developing an
active mode test procedure in the microwave oven test procedure final
rule published on March 30, 2022, (``March 2022 TP Final Rule'') due to
undue burden on manufacturers and the lack of an available test
procedure that accounts for the efficiency improvements of inverter
microwave ovens. 87 FR 18261. As there is no test procedure for
measuring the active mode efficiency of a microwave oven, and since
development of such a test procedure is out of the scope of this
document, DOE is not currently proposing to adopt an active mode energy
usage standard.
See section IV.2 of this document for discussion of the product
classes analyzed in this final rule.
B. Test Procedure
EPCA sets forth generally applicable criteria and procedures for
DOE's adoption and amendment of test procedures. (42 U.S.C. 6293)
Manufacturers of covered products must use these test procedures to
certify to DOE that their product complies with energy conservation
standards and to quantify the efficiency of their product. DOE will
finalize a test procedure establishing methodologies used to evaluate
proposed energy conservation standards prior to publication of a NOPR
proposing new or amended energy conservation standards. Section 8(d)(1)
of appendix A. As discussed, DOE amended the test procedure for
microwave ovens, set forth in appendix I, in the March 2022 TP Final
Rule. DOE's current energy conservation standards for microwave ovens
are expressed in terms of watts of standby power. (See 10 CFR
430.23(j)(3).)
C. Technological Feasibility
1. General
In each energy conservation standards rulemaking, DOE conducts a
screening analysis based on information gathered on all current
technology options and prototype designs that could improve the
efficiency of the products or equipment that are the subject of the
rulemaking. As the first step in such an analysis, DOE develops a list
of technology options for consideration in consultation with
manufacturers, design engineers, and other interested parties. DOE then
determines which of those means for improving efficiency are
technologically feasible. DOE considers technologies incorporated in
commercially available products or in working prototypes to be
technologically feasible. Sections 6(b)(3)(i) and 7(b)(1) of appendix
A.
After DOE has determined that particular technology options are
technologically feasible, it further evaluates each technology option
in light of the following additional screening criteria: (1)
practicability to manufacture, install, and service; (2) adverse
impacts on product utility or availability; (3) adverse impacts on
health or safety and (4) unique-pathway proprietary technologies.
Sections 6(b)(3)(ii) through (v) and sections 7(b)(2) through (5) of
appendix A. Section IV.B of this document discusses the results of the
screening analysis for microwave ovens, particularly the designs DOE
considered, those it screened out, and those that are the basis for the
standards considered in this rulemaking. For further details on the
screening analysis for this rulemaking, see chapter 4 of the final rule
TSD.
2. Maximum Technologically Feasible Levels
When DOE proposes to adopt an amended standard for a type or class
of covered product, it must determine the maximum improvement in energy
[[Page 39920]]
efficiency or maximum reduction in energy use that is technologically
feasible for such product. (42 U.S.C. 6295(p)(1)) Accordingly, in the
engineering analysis, DOE determined the maximum technologically
feasible (``max-tech'') improvements in energy efficiency for microwave
ovens, using the design parameters for the most efficient products
available on the market or in working prototypes. The max-tech levels
that DOE determined for this rulemaking are described in section IV.C
of this document and in chapter 5 of the final rule TSD.
D. Energy Savings
1. Determination of Savings
For each trial standard level (``TSL''), DOE projected energy
savings from application of the TSL to microwave ovens purchased in the
30-year period that begins in the year of compliance with the amended
standards (2026-2055).\14\ The savings are measured over the entire
lifetime of products purchased in the 30-year analysis period. DOE
quantified the energy savings attributable to each TSL as the
difference in energy consumption between each standards case and the
no-new-standards case. The no-new-standards case represents a
projection of energy consumption that reflects how the market for a
product would likely evolve in the absence of amended energy
conservation standards.
---------------------------------------------------------------------------
\14\ Each TSL is composed of specific efficiency levels for each
product class. The TSLs considered for this rule are described in
section V.A of this document. DOE also presents a sensitivity
analysis that considers impacts for products shipped in a 9-year
period.
---------------------------------------------------------------------------
DOE used its national impact analysis (``NIA'') spreadsheet models
to estimate national energy savings (``NES'') from potential amended
standards for microwave ovens. The NIA spreadsheet model (described in
section IV.H of this document) calculates energy savings in terms of
site energy, which is the energy directly consumed by products at the
locations where they are used. For electricity, DOE reports national
energy savings in terms of primary energy savings, which is the savings
in the energy that is used to generate and transmit the site
electricity. For natural gas, the primary energy savings are considered
to be equal to the site energy savings. DOE also calculates NES in
terms of FFC energy savings. The FFC metric includes the energy
consumed in extracting, processing, and transporting primary fuels
(i.e., coal, natural gas, petroleum fuels), and thus presents a more
complete picture of the impacts of energy conservation standards.\15\
DOE's approach is based on the calculation of an FFC multiplier for
each of the energy types used by covered products or equipment. For
more information on FFC energy savings, see section IV.H.2 of this
document.
---------------------------------------------------------------------------
\15\ The FFC metric is discussed in DOE's statement of policy
and notice of policy amendment. 76 FR 51282 (Aug. 18, 2011), as
amended at 77 FR 49701 (Aug. 17, 2012).
---------------------------------------------------------------------------
2. Significance of Savings
To adopt any new or amended standards for a covered product, DOE
must determine that such action would result in significant energy
savings. (42 U.S.C. 6295(o)(3)(B))
The significance of energy savings offered by a new or amended
energy conservation standard cannot be determined without knowledge of
the specific circumstances surrounding a given rulemaking. For example,
some covered products and equipment have most of their energy
consumption occur during periods of peak energy demand. The impacts of
these products on the energy infrastructure can be more pronounced than
products with relatively constant demand. In evaluating the
significance of energy savings, DOE considers differences in primary
energy and FFC effects for different covered products and equipment
when determining whether energy savings are significant. Primary energy
and FFC effects include the energy consumed in electricity production
(depending on load shape), in distribution and transmission, and in
extracting, processing, and transporting primary fuels (i.e., coal,
natural gas, petroleum fuels), and thus present a more complete picture
of the impacts of energy conservation standards.
Accordingly, DOE evaluates the significance of energy savings on a
case-by-case basis. As stated, the standard levels adopted in this
final rule are projected to result in national FFC energy savings of
0.06 quads, the equivalent of the electricity use of 1.6 million homes
in one year. DOE has determined the energy savings from the standard
levels adopted in this final rule are ``significant'' within the
meaning of 42 U.S.C. 6295(o)(3)(B).
E. Economic Justification
1. Specific Criteria
As noted previously, EPCA provides seven factors to be evaluated in
determining whether a potential energy conservation standard is
economically justified. (42 U.S.C. 6295(o)(2)(B)(i)(I)-(VII)) The
following sections discuss how DOE has addressed each of those seven
factors in this rulemaking.
a. Economic Impact on Manufacturers and Consumers
In determining the impacts of potential amended standards on
manufacturers, DOE conducts a Manufacturer Impact Analysis (``MIA''),
as discussed in section IV.J of this document. DOE uses an annual cash-
flow approach to determine the quantitative impacts. This step includes
both a short-term assessment--based on the cost and capital
requirements during the period between when a regulation is issued and
when entities must comply with the regulation--and a long-term
assessment over a 30-year period. The industry-wide impacts analyzed
include (1) INPV, which values the industry on the basis of expected
future cash flows; (2) cash flows by year; (3) changes in revenue and
income; and (4) other measures of impact, as appropriate. Second, DOE
analyzes and reports the impacts on different types of manufacturers,
including impacts on small manufacturers. Third, DOE considers the
impact of standards on domestic manufacturer employment and
manufacturing capacity, as well as the potential for standards to
result in plant closures and loss of capital investment. Finally, DOE
takes into account cumulative impacts of various DOE regulations and
other regulatory requirements on manufacturers.
For individual consumers, measures of economic impact include the
changes in LCC and payback period (``PBP'') associated with new or
amended standards. These measures are discussed further in the
following section. For consumers in the aggregate, DOE also calculates
the national net present value of the consumer costs and benefits
expected to result from particular standards. DOE also evaluates the
impacts of potential standards on identifiable subgroups of consumers
that may be affected disproportionately by a standard.
b. Savings in Operating Costs Compared To Increase in Price (LCC and
PBP)
EPCA requires DOE to consider the savings in operating costs
throughout the estimated average life of the covered product in the
type (or class) compared to any increase in the price of, or in the
initial charges for, or maintenance expenses of, the covered product
that are likely to result from a standard. (42 U.S.C.
6295(o)(2)(B)(i)(II)) DOE conducts this comparison in its LCC and PBP
analysis.
The LCC is the sum of the purchase price of a product (including
its
[[Page 39921]]
installation) and the operating cost (including energy, maintenance,
and repair expenditures) discounted over the lifetime of the product.
The LCC analysis requires a variety of inputs, such as product prices,
product energy consumption, energy prices, maintenance and repair
costs, product lifetime, and discount rates appropriate for consumers.
To account for uncertainty and variability in specific inputs, such as
product lifetime and discount rate, DOE uses a distribution of values,
with probabilities attached to each value.
The PBP is the estimated amount of time (in years) it takes
consumers to recover the increased purchase cost (including
installation) of a more-efficient product through lower operating
costs. DOE calculates the PBP by dividing the change in purchase cost
due to a more-stringent standard by the change in annual operating cost
for the year that standards are assumed to take effect.
For its LCC and PBP analysis, DOE assumes that consumers will
purchase the covered products in the first year of compliance with new
or amended standards. The LCC savings for the considered efficiency
levels are calculated relative to the case that reflects projected
market trends in the absence of new or amended standards. DOE's LCC and
PBP analysis is discussed in further detail in section IV.F of this
document.
c. Energy Savings
Although significant conservation of energy is a separate statutory
requirement for adopting an energy conservation standard, EPCA requires
DOE, in determining the economic justification of a standard, to
consider the total projected energy savings that are expected to result
directly from the standard. (42 U.S.C. 6295(o)(2)(B)(i)(III)) As
discussed in section IV.E of this document, DOE uses the NIA
spreadsheet models to project national energy savings.
d. Lessening of Utility or Performance of Products
In establishing product classes, and in evaluating design options
and the impact of potential standard levels, DOE evaluates potential
standards that would not lessen the utility or performance of the
considered products. (42 U.S.C. 6295(o)(2)(B)(i)(IV)) Based on data
available to DOE, the standards adopted in this document would not
reduce the utility or performance of the products under consideration
in this rulemaking.
e. Impact of Any Lessening of Competition
EPCA directs DOE to consider the impact of any lessening of
competition, as determined in writing by the Attorney General, that is
likely to result from a standard. (42 U.S.C. 6295(o)(2)(B)(i)(V)) It
also directs the Attorney General to determine the impact, if any, of
any lessening of competition likely to result from a proposed standard
and to transmit such determination to the Secretary within 60 days of
the publication of a proposed rule, together with an analysis of the
nature and extent of the impact. (42 U.S.C. 6295(o)(2)(B)(ii)) To
assist the Department of Justice (``DOJ'') in making such a
determination, DOE transmitted copies of the August 2022 SNOPR and the
SNOPR TSD to the Attorney General for review, with a request that the
DOJ provide its determination on this issue. In its assessment letter
responding to DOE, DOJ concluded that the proposed energy conservation
standards for microwave ovens are unlikely to have a significant
adverse impact on competition. DOE is publishing the Attorney General's
assessment at the end of this final rule.
f. Need for National Energy Conservation
DOE also considers the need for national energy and water
conservation in determining whether a new or amended standard is
economically justified. (42 U.S.C. 6295(o)(2)(B)(i)(VI)) The energy
savings from the adopted standards are likely to provide improvements
to the security and reliability of the Nation's energy system.
Reductions in the demand for electricity also may result in reduced
costs for maintaining the reliability of the Nation's electricity
system. DOE conducts a utility impact analysis to estimate how
standards may affect the Nation's needed power generation capacity, as
discussed in section IV.M of this document.
DOE maintains that environmental and public health benefits
associated with the more efficient use of energy are important to take
into account when considering the need for national energy
conservation. The adopted standards are likely to result in
environmental benefits in the form of reduced emissions of air
pollutants and greenhouse gases (``GHGs'') associated with energy
production and use. DOE conducts an emissions analysis to estimate how
potential standards may affect these emissions, as discussed in section
IV.K of this document; the estimated emissions impacts are reported in
section V.B.6 of this document. DOE also estimates the economic value
of emissions reductions resulting from the considered TSLs, as
discussed in section IV.L of this document.
g. Other Factors
In determining whether an energy conservation standard is
economically justified, DOE may consider any other factors that the
Secretary deems to be relevant. (42 U.S.C. 6295(o)(2)(B)(i)(VII)) To
the extent DOE identifies any relevant information regarding economic
justification that does not fit into the other categories described
previously, DOE could consider such information under ``other
factors.''
2. Rebuttable Presumption
As set forth in 42 U.S.C. 6295(o)(2)(B)(iii), EPCA creates a
rebuttable presumption that an energy conservation standard is
economically justified if the additional cost to the consumer of a
product that meets the standard is less than three times the value of
the first year's energy savings resulting from the standard, as
calculated under the applicable DOE test procedure. DOE's LCC and PBP
analyses generate values used to calculate the effects that proposed
energy conservation standards would have on the payback period for
consumers. These analyses include, but are not limited to, the 3-year
payback period contemplated under the rebuttable-presumption test. In
addition, DOE routinely conducts an economic analysis that considers
the full range of impacts to consumers, manufacturers, the Nation, and
the environment, as required under 42 U.S.C. 6295(o)(2)(B)(i). The
results of this analysis serve as the basis for DOE's evaluation of the
economic justification for a potential standard level (thereby
supporting or rebutting the results of any preliminary determination of
economic justification). The rebuttable presumption payback calculation
is discussed in section IV.F of this document.
IV. Methodology and Discussion of Related Comments
This section addresses the analyses DOE has performed for this
rulemaking with regard to microwave ovens. Separate subsections address
each component of DOE's analyses.
DOE used several analytical tools to estimate the impact of the
standards considered in this document. The first tool is a spreadsheet
that calculates the LCC savings and PBP of potential amended or new
energy conservation
[[Page 39922]]
standards. The national impacts analysis uses a second spreadsheet set
that provides shipments projections and calculates national energy
savings and net present value of total consumer costs and savings
expected to result from potential energy conservation standards. DOE
uses the third spreadsheet tool, the Government Regulatory Impact Model
(``GRIM''), to assess manufacturer impacts of potential standards.
These three spreadsheet tools are available on the DOE website for this
rulemaking: www1.eere.energy.gov/buildings/appliance_standards/product.aspx/productid/48. Additionally, DOE used output from the
latest version of the Energy Information Administration's (``EIA's'')
Annual Energy Outlook (``AEO'') for the emissions and utility impact
analyses.
1. Market and Technology Assessment
DOE develops information in the market and technology assessment
that provides an overall picture of the market for the products
concerned, including the purpose of the products, the industry
structure, manufacturers, market characteristics, and technologies used
in the products. This activity includes both quantitative and
qualitative assessments, based primarily on publicly-available
information. The subjects addressed in the market and technology
assessment for this rulemaking include (1) a determination of the scope
of the rulemaking and product classes, (2) manufacturers and industry
structure, (3) existing efficiency programs, (4) shipments information,
(5) market and industry trends, and (6) technologies or design options
that could improve the energy efficiency of microwave ovens. The key
findings of DOE's market assessment are summarized in the following
sections. See chapter 3 of the final rule TSD for further discussion of
the market and technology assessment.
AHAM commented that it disagrees with DOE addressing European
efficiency programs as a part of its analysis for the August 2022
SNOPR. AHAM stated that DOE is improperly making direct comparisons to
the European market and should not look to Europe or any other
jurisdiction for guidance without first understanding the differences
between products in those markets and those in the United States.
(AHAM, No. 28 at p. 10) In response to AHAM's comment, DOE notes that
its analysis of foreign regulatory programs is only to reduce
additional manufacturer burden in complying with conflicting standards.
DOE did not find any conflicting foreign regulatory programs, nor did
it develop trial standards levels based on any foreign regulations. In
the case of this rulemaking, foreign regulations had no bearing on
DOE's analysis.
2. Product Classes
When evaluating and establishing energy conservation standards, DOE
may establish separate standards for a group of covered products (i.e.,
establish a separate product class) if DOE determines that separate
standards are justified based on the type of energy used, or if DOE
determines that a product's capacity or other performance-related
feature justifies a different standard. (42 U.S.C. 6295(q)) In making a
determination whether a performance-related feature justifies a
different standard, DOE must consider such factors as the utility of
the feature to the consumer and other factors DOE determines are
appropriate. (Id.)
Any product meeting the definition of a microwave oven, as codified
in 10 CFR 430.2, is included in DOE's scope of coverage. ``Microwave
oven'' is defined as a category of cooking products which is a
household cooking appliance consisting of a compartment designed to
cook or heat food by means of microwave energy, including microwave
ovens with or without thermal elements designed for surface browning of
food and convection microwave ovens. This includes any microwave
oven(s) component of a combined cooking product.
For this proposal, DOE considered the two product classes of
microwave ovens prescribed in the current energy conservation
standards: (1) Microwave-Only Ovens and Countertop Convection Microwave
Ovens, and (2) Built-In and Over-the-Range Convection Microwave Ovens.
For these two classes of microwave ovens, DOE's current test
procedure measures the energy consumption in standby mode and off mode
only. Consequently, DOE's current energy conservation standards for
microwave ovens are also expressed in terms of standby mode and off
mode power. There are currently no active mode energy conservation
standards nor a prescribed test procedure for measuring the active mode
energy use or efficiency (e.g., cooking efficiency) of microwave ovens.
In response to the August 2022 SNOPR, AHAM and Whirlpool requested
that DOE consider changing microwave oven product classes to align with
the three general chassis designs: countertop, built-in, and over-the-
range. AHAM commented that the feature sets, design requirements,
consumer use patterns, and standby powers are more correlated to
chassis type than the presence of convection functionality. (AHAM, No.
28 at p. 12) AHAM further stated that, on a shipment-weighted average
basis, countertop models consume 0.6 W of standby power, followed by
over-the-range models, and built-in models consuming 0.81 W and 1.65 W
of standby power, respectively. (AHAM, No. 28 at p. 13) Whirlpool added
that task lights, exhaust fans, and environmental sensors are some of
the unique features of many over-the-range microwave ovens. (Whirlpool,
No. 30 at p. 6).
In the June 2013 Final Rule, DOE discussed its rationale for
establishing the current product class structure. In that rulemaking,
DOE acknowledged that over-the-range microwave ovens contain additional
relays for components that are not found in countertop units, such as
exhaust or cooling fans and cooktop lighting. However, these components
were not found in DOE's analysis to require larger power supplies that
would affect standby power consumption, and thus would not warrant a
separate product class for over-the-range microwave-only ovens from
countertop microwave ovens. 78 FR 36328. For this rulemaking, DOE's
teardown and analyses of the Compliance Certification Database (``CCD
\16\'') showed that microwave ovens have a wide variety of features
independent of chassis type. DOE found various sensors, display types,
and connectivity features in over-the-range, built-in and countertop
microwave ovens. As such, DOE determines that performance-related
features are fully reflected by the current product class structure.
Additionally, AHAM claims via its shipment-weighted average standby
power consumption data that the only meaningful differentiation for
product classes is installation configuration. AHAM however did not
provide shipments data with sufficient granularity to contradict DOE's
previous data and conclusions (i.e., to justify eliminating product
class differentiation on the basis of convection features and instead
defining product classes solely by installation configuration). As a
result, DOE is unable to rely on AHAM's data to revise the product
classes. Further, DOE is not aware of, nor did AHAM provide, any data
demonstrating that consumer utility varies by chassis type and has
impacts on energy use that would justify establishing separate product
classes. As a result, DOE is
[[Page 39923]]
opting to maintain its current product class structure.
---------------------------------------------------------------------------
\16\ Available at www.regulations.doe.gov/certification-data.
---------------------------------------------------------------------------
3. Technology Options
In the preliminary market analysis and technology assessment for
the August 2022 SNOPR, DOE identified four technology options initially
determined to improve the efficiency of microwave ovens, as measured by
the DOE test procedure:
Table IV.1--Microwave Oven Technology Options
------------------------------------------------------------------------
Mode Technology option
------------------------------------------------------------------------
Standby................................ Lower-power display
technologies.
Standby................................ Cooking sensors with no standby
power requirement.
Standby................................ More efficient power supply and
control board options.
Standby................................ Automatic power-down of most
power-consuming components,
including the clock display.
------------------------------------------------------------------------
In support of the analysis for its August 2022 SNOPR, DOE purchased
and tested 33 microwave ovens representing the two proposed product
classes, and the results confirmed that microwave oven models currently
on the market can achieve standby power consumption values in-between
the very low levels enabled by automatic power-down microwave ovens and
the proposed levels (i.e., 0.6 W for Product Class 1 and 1.0 W for
Product Class 2). 87 FR 52283. Further, DOE's testing suggested that
microwave ovens are frequently rated conservatively, such that their
certified standby power level is higher than actual values obtained
when tested in accordance with appendix I. Therefore, DOE was unable to
accurately assess the relationship between specific standby power
levels and utilized technology options based on data from the CCD.
Instead, DOE used the measured standby power levels of microwave oven
models in its test sample as a proxy to determine the representative
distribution of standby power levels among microwave ovens on the
market, as shown in Table IV.2. Details of the methodology and results
from DOE's investigative testing are included in chapter 3 and chapter
5 of the SNOPR TSD as well as the final rule TSD.\17\
---------------------------------------------------------------------------
\17\ The final rule TSD as well as the SNOPR TSD are available
on the docket, www.regulations.gov/document/EERE-2017-BT-STD-0023-0022.
Table IV.2--Estimated Market Distribution of Microwave Ovens
------------------------------------------------------------------------
Market share
Standby power (W) (%)
------------------------------------------------------------------------
Microwave-Only Ovens and Countertop Convection Microwave Ovens
------------------------------------------------------------------------
1....................................................... 15
0.8..................................................... 45
0.6..................................................... 29
0.4..................................................... 11
------------------------------------------------------------------------
Built-in and Over-the-Range Convection Microwave Ovens
------------------------------------------------------------------------
2.2..................................................... 0
1.5..................................................... 36
1....................................................... 59
0.5..................................................... 5
------------------------------------------------------------------------
AHAM commented that it disagreed with DOE's use of tested values
rather than CCD reported values in the August 2022 SNOPR, a practice it
says undermines the practice of conservatively reporting standby power
to allow some ``buffer'' to ensure consumers are getting what they are
promised. (AHAM, No. 28 at p. 9) AHAM further commented that
conservative rating ensures compliance with applicable standards by
providing a safety factor to account for unavoidable variation in the
manufacturing process. DOE notes that its tested values were often much
lower than the reported values in the CCD, with differences as great as
1.43 W (approximately 65 percent) for Product Class 2 microwave ovens
and 0.6192 W (approximately 61 percent) for Product Class 1 microwave
ovens. DOE determines these current ratings to be significantly more
conservative than is necessary, considering electronics manufacturing
processes are sufficiently advanced. Furthermore, DOE did not see any
variation in standby power greater than 0.1 W in the duplicate test
units.
AHAM additionally commented that the products that use
significantly less power than rated undermine the need for new
standards, as there is little to gain. (AHAM, No. 28 at p. 9)
DOE reiterates that its analysis uses an efficiency distribution
based on tested values that shows the existing market to be more
efficient compared to that based on overly conservative rated values.
As discussed further in section V.C.1 of this document, DOE's analysis
demonstrates that despite the use of a more efficient distribution in
its analysis as a starting point, the benefits of the standard exceed,
to a great extent, the burdens at TSL 2 and an amended standard set at
this level for microwave ovens would be economically justified.
Additionally, AHAM's comment underscores the importance of testing
units rather than relying solely on data from the CCD.
As part of the analysis for the August 2022 SNOPR, DOE subsequently
tore down all 33 microwave ovens, but was unable to isolate a unique
set of technology options associated with each standby power level. As
such, DOE concluded that models demonstrating lower standby power
consumption than the current energy conservation standards are not
implementing specific technology options; rather, they are
incorporating a comprehensive, system-level control board redesign that
prioritizes standby power performance from the ground up. Examples of
possible redesign strategies include (1) the replacement of
microcontrollers with modern ones that demonstrate significantly lower
quiescent current consumption and (2) firmware that emphasizes the
shutting down of any subassemblies that are not in use while idle. DOE
estimated that while these improvements would not contribute to the
incremental manufacturer production cost (``MPC'') of a control board,
the redesign would result in significant conversion costs for
manufacturers as they attempt to bring their microwave oven models into
compliance with any proposed standards. See section IV.J.2.a of this
document.
In the August 2022 SNOPR, DOE requested feedback on its tentative
conclusion that reducing the standby power consumption of a microwave
oven would require a whole-board redesign, and that manufacturers would
incur a one-time conversion cost without any additional MPC. AHAM and
Whirlpool agreed with DOE's assessment that standby power reduction is
a system-level redesign challenge, and that standby power often cannot
be reduced with simple component changes. (AHAM, No. 28 at p. 5;
Whirlpool, No. 30 at p. 6) AHAM and Whirlpool disagreed with DOE's
conclusion that redesign would not impact overall MPC of a given
product. Whirlpool commented that the new classes of microprocessors,
display backlight circuits, display deep sleep technologies, and power
switches may be necessary to reach higher efficiencies, and that this
will add to the MPC for more efficient microwave ovens. (Whirlpool, No.
30 at p. 7) AHAM commented that changes to the control board may
require manufacturers to evaluate and replace or remove components
affected by the control board (e.g., displays, sensors,
[[Page 39924]]
and clock) to reach amended standard levels. (AHAM, No. 28 at p. 5)
In response to AHAM and Whirlpool's comments, DOE notes that the
analysis of the 33 microwave ovens noted above included product
teardowns and establishing costed bill of materials. DOE examined the
datasheets for components used in each design but was unable to
establish a strong relationship between the use of better components
and a microwave oven's overall standby performance. DOE found that
while standby performance could be improved by opting for a better
component, such as in the case of microcontrollers with deep sleep
states, the cost differentials were often zero or negative. In all
situations, DOE found that overall circuit design rather than component
selection itself had a greater impact on standby performance cost. In
the absence of additional cost data showing a clear MPC-efficiency
relationship, DOE maintains its conclusion that any system-level
redesign would not contribute to an incremental MPC increase.
B. Screening Analysis
DOE uses the following five screening criteria to determine which
technology options are suitable for further consideration in an energy
conservation standards rulemaking:
(1) Technological feasibility. Technologies that are not
incorporated in commercial products or in working prototypes will not
be considered further.
(2) Practicability to manufacture, install, and service. If it is
determined that mass production and reliable installation and servicing
of a technology in commercial products could not be achieved on the
scale necessary to serve the relevant market at the time of the
projected compliance date of the standard, then that technology will
not be considered further.
(3) Impacts on product utility or product availability. If it is
determined that a technology would have a significant adverse impact on
the utility of the product for significant subgroups of consumers or
would result in the unavailability of any covered product type with
performance characteristics (including reliability), features, sizes,
capacities, and volumes that are substantially the same as products
generally available in the United States at the time, it will not be
considered further.
(4) Adverse impacts on health or safety. If it is determined that a
technology would have significant adverse impacts on health or safety,
it will not be considered further.
(5) Unique-Pathway Proprietary Technologies. If a design option
utilizes proprietary technology that represents a unique pathway to
achieving a given efficiency level, that technology will not be
considered further due to the potential for monopolistic concerns.
Sections 6(b)(3) and 7(b) of appendix A.
In sum, if DOE determines that a technology, or a combination of
technologies, fails to meet one or more of the listed five criteria, it
will be excluded from further consideration in the engineering
analysis. The reasons for eliminating any technology are discussed in
the following sections.
The subsequent sections include DOE's evaluation of each technology
option against the screening analysis criteria, and whether DOE
determined that a technology option should be excluded (``screened
out'') based on the screening criteria.
1. Screened-Out Technologies
DOE considers whether a technology option will adversely impact
consumer utility and product availability. To that end, DOE has
previously stated it is uncertain the extent to which consumers value
the function of a continuous display clock, but that loss of such
function may result in significant loss of consumer utility. 78 FR
36316, 36362. Consistent with this prior concern, DOE has screened out
``automatic power-down'' as a technology option due to its impact on
consumer utility in this final rule.
2. Remaining Technologies
Through a review of each technology, DOE concludes that all of the
other identified technologies listed in section IV.B.2 of this document
meet all five screening criteria to be examined further as design
options in DOE's final rule analysis. In summary, DOE did not screen
out the following technology options:
(1) Lower-power display technologies;
(2) Cooking sensors with no standby power requirement; and
(3) More efficient power supply and control board options.
DOE determines that these technology options are technologically
feasible because they are being used or have previously been used in
commercially-available products or working prototypes. DOE also finds
that all of the remaining technology options meet the other screening
criteria (i.e., practicable to manufacture, install, and service and do
not result in adverse impacts on consumer utility, product
availability, health, or safety). For additional details, see chapter 4
of the final rule TSD.
AHAM and Whirlpool asserted that DOE's revised standards will cause
an unacceptable loss of product functionality, and that future features
will not be able to be added to microwave ovens due to feature power
draw and DOE's practice of undermining conservative ratings. (AHAM, No.
28 at pp. 3-4, 8; Whirlpool, No. 30 at p. 5) AHAM provided a
confidential list of various features that it states would be
impossible to implement at DOE's updated standards. (AHAM, No. 28 at p.
4) AHAM additionally commented that manufacturers will also be unable
to incorporate indoor air quality (``IAQ'') sensors, which may be
required by future state building codes and could be impossible to
implement due to EPCA's backsliding provision. (Id. at pp. 3, 13) AHAM
and Whirlpool commented that other sensors may also need to be removed
as well, driving consumers to use less efficient methods of cooking,
and Whirlpool added that it was not aware of any humidity sensors that
do not impact standby power. (AHAM, No. 28 at p. 4; Whirlpool, No. 30
at pp. 4, 7) Finally, AHAM stated that updated microwave oven standby
power standards could lead to a loss of connectivity features in
microwave ovens. (AHAM, No 28 at p. 3)
The Joint Commenters commented that they were able to find many
Product Class 1 \18\ units from various manufacturers with reported
powers below 0.6 W that incorporated sensor technologies. (Joint
Commenters, No. 31 at p. 3)
---------------------------------------------------------------------------
\18\ Product Class 1 comprises microwave-only ovens and
countertop convection microwave ovens.
---------------------------------------------------------------------------
In response to these comments, DOE concludes that IAQ monitoring
sensors (smoke and carbon monoxide(``CO'')) are technologically mature
enough to be implemented without any significant impact to microwave
oven standby power budgets due to the prevalence and maturity of low-
power smoke and carbon monoxide detectors required by most state
building codes.\19\ DOE researched additional sensors that might be
applicable for use in microwave ovens, and found low-power options for
IAQ, such as the Bosch BME688, with an average current consumption of
0.1 milliamps (``mA'') at 3.6 volts (``V'') in low power mode, and the
Renesas ZMOD4410 with an average power consumption of 0.16 milliwatts
in ultra-low power mode. Similarly, DOE found
[[Page 39925]]
flame detection sensors, such as the Kemet QFS series, with an average
current draw of 3.5 microamps (``[micro]A'') at 3.6 V and PM sensors,
such as the Sensirion SPS30, with an idle current draw of 330 [micro]A
and a sleep current draw of 50 [micro]A.
---------------------------------------------------------------------------
\19\ DOE found that the First Alert BRK PRC710 and Kidde P3010CU
combination smoke and CO detectors include sealed batteries meant to
last 10 years.
---------------------------------------------------------------------------
Regarding AHAM's comment that updated standards impact connectivity
features, DOE notes that section 2.1.1 of appendix I instructs that if
a microwave oven can communicate through a network (e.g.,
Bluetooth[supreg] or internet connection), the network function is
disabled for the duration of standby mode and off mode testing, if it
is possible to disable it by means provided in the manufacturer's user
manual. Furthermore, DOE's testing did not find any correlation between
presence of connected features and standby power consumption.
Similarly, DOE did not find any standby power impact from humidity
sensors in the microwave ovens tested and torn down. An additional
review of available humidity sensors showed multiple models without a
listed electrical warm-up time, as well as sensors with power
requirements less than 0.005 W (e.g. review of datasheets for humidity
sensors from component manufacturers such as Reneas, Amphenol, and
Texas Instrument shows typical supply currents in the range of 1 to 200
[micro]A).
With regards to loss of features and functionality, DOE notes that
many of the features discussed confidentially by AHAM were already
present in the microwave ovens torn down by DOE and therefore were
captured by DOE in its analysis. DOE also determines that those
features discussed by AHAM that were not seen in DOE's teardown
analysis would not impact standby power, as the microwave oven would
not be in standby mode while those features are activated. Instead, the
features would be disconnected, turned off, or put into a quiescent
state \20\ in order to place the microwave oven in standby mode for
testing. As such, DOE determines that amending standards would neither
impact the types of sensors that can be used in microwave oven designs
nor adversely impact consumer utility.
---------------------------------------------------------------------------
\20\ In electronics design, Quiescent state or Quiescent mode is
defined as a state of inactivity or dormancy, with attributes of
very low current draw.
---------------------------------------------------------------------------
C. Engineering Analysis
The purpose of the engineering analysis is to establish the
relationship between the efficiency and cost of microwave ovens. There
are two elements to consider in the engineering analysis; the selection
of efficiency levels to analyze (i.e., the ``efficiency analysis'') and
the determination of product cost at each efficiency level (i.e., the
``cost analysis''). In determining the performance of higher-efficiency
microwave ovens, DOE considers technologies and design option
combinations not eliminated by the screening analysis. For each product
class, DOE estimates the baseline cost, as well as the incremental cost
for the product/equipment at efficiency levels above the baseline. The
output of the engineering analysis is a set of cost-efficiency
``curves'' that are used in downstream analyses (i.e., the LCC and PBP
analyses and the NIA).
1. Efficiency Analysis
DOE typically uses one of two approaches to develop energy
efficiency levels for the engineering analysis: (1) relying on observed
efficiency levels in the market (i.e., the efficiency-level approach),
or (2) determining the incremental efficiency improvements associated
with incorporating specific design options to a baseline model (i.e.,
the design-option approach). Using the efficiency-level approach, the
efficiency levels established for the analysis are determined based on
the market distribution of existing products (in other words, based on
the range of efficiencies and efficiency level ``clusters'' that
already exist on the market). Using the design option approach, the
efficiency levels established for the analysis are determined through
detailed engineering calculations and/or computer simulations of the
efficiency improvements from implementing specific design options that
have been identified in the technology assessment. DOE may also rely on
a combination of these two approaches. For example, the efficiency-
level approach (based on actual products on the market) may be extended
using the design option approach to ``gap fill'' levels (to bridge
large gaps between other identified efficiency levels) and/or to
extrapolate to the ``max-tech'' level (particularly in cases where the
``max-tech'' level exceeds the maximum efficiency level currently
available on the market).
In this rulemaking, DOE applied the efficiency-level approach. As
discussed, DOE was unable to use the design-option approach because it
did not identify specific design options associated with each standby
power level.
a. Baseline Efficiency/Energy Use
For each product class, DOE generally selects a baseline model as a
reference point against which to measure changes resulting from energy
conservation standards. The baseline model in each product class
represents the characteristics of a product typical of that class
(e.g., capacity, physical size). Generally, a baseline model is one
that just meets current energy conservation standards, or, if no
standards are in place, the baseline is typically the most common or
least efficient unit on the market.
For microwave-only ovens and countertop convection microwave ovens
(``Product Class 1''), the baseline standby power level is equal to the
current standard of 1.0 W. For the built-in and over-the-range
convection microwave ovens product class (``Product Class 2''), the
baseline standby power consumption used for the analysis is equal to
the current standard of 2.2 W. This maximum allowable average standby
power consumption for Product Class 2 is higher than that allowed for
Product Class 1 microwave ovens because, in the June 2013 Final Rule,
DOE concluded that built-in and over-the-range convection microwave
ovens require a larger power supply to support additional features,
such as an exhaust fan, additional relays, and additional lights, and
that the larger power supply contributes to a higher standby power
consumption. 78 FR 36316, 36328. Nonetheless, DOE expects that certain
available design options for reducing standby power consumption for
Product Class 2 microwave ovens would be similar to those for Product
Class 1 microwave ovens.
b. Higher Efficiency Levels
Using the efficiency-level approach, the higher efficiency levels
established for the analysis are determined based on the market
distribution of existing products (in other words, based on the range
of efficiencies and efficiency level ``clusters'' that already exist on
the market). As noted in section IV.A.2 of this document, DOE's testing
suggests that microwave ovens are frequently rated conservatively, such
that their certified standby power level is higher than actual values
obtained when tested in accordance with appendix I. DOE therefore used
the measured standby power levels of microwave oven models in its test
sample as a proxy to determine the representative distribution of
standby power levels among microwave ovens currently on the market, as
shown in Table IV.2.
According to this efficiency distribution, 85 percent of Product
Class 1 microwave ovens achieve a standby power consumption lower than
the
[[Page 39926]]
current standard of 1.0 W, with 45 percent of the market estimated to
be achieving 0.8 W, 29 percent achieving 0.6 W, and 11 percent
achieving 0.4 W, all without the use of automatic power-down. For
Product Class 1, therefore, DOE analyzed three efficiency levels
(``ELs'') above the baseline, which correspond to these three standby
power levels, as shown in Table IV.3.
The test results also showed that all of the Product Class 2 test
units achieved a standby power consumption in the range of 0.5 W to 1.5
W, lower than the current standard of 2.2 W. As such, DOE analyzed
higher efficiency levels for this product class at standby power values
evenly distributed within that range: EL 1 at 1.5 W, EL 2 at 1.0 W, and
EL 3 (max-tech) at 0.5 W. DOE estimates that there are currently no
built-in and over-the-range convection microwave ovens in the market at
the baseline standby power consumption of 2.2 W.
In summary, DOE analyzed the following efficiency levels for this
rule:
Table IV.3--Analyzed Efficiency Levels for Microwave-Only Ovens and
Countertop Convection Microwave Ovens
------------------------------------------------------------------------
Standby power
Efficiency level (W)
------------------------------------------------------------------------
Baseline................................................ 1.00
1....................................................... 0.8
2....................................................... 0.6
3 (Max-Tech)............................................ 0.4
------------------------------------------------------------------------
Table IV.4--Analyzed Efficiency Levels for Built-In and Over-the-Range
Convection Microwave Ovens
------------------------------------------------------------------------
Standby power
Efficiency level (W)
------------------------------------------------------------------------
Baseline................................................ 2.2
1....................................................... 1.5
2....................................................... 1.0
3 (Max-Tech)............................................ 0.5
------------------------------------------------------------------------
The Joint Commenters requested that DOE analyze an additional
efficiency level above max-tech, citing a number of microwave ovens in
the CCD with reported standby powers of less than 0.3 W. The Joint
Commenters further stated that many of these microwave ovens do not
utilize the screened-out automatic power-down technology option, making
this a viable efficiency level for manufacturers.
With regard to the Joint Commenters request, DOE's review of the
market has shown that the majority of the microwave ovens at or below
0.3 W utilize other screened-out technology options (no clock, no
display, and automatic power-down) to achieve a low standby power, and
that an EL above max-tech would require designing microwave ovens with
a significant impact to consumer utility. Also, as discussed further in
section V.C of this document, DOE has determined that there is
uncertainty as to whether or not a standard at max-tech would stifle
innovation and risk impacting customer utility. Accordingly, DOE has
elected not to analyze an efficiency level above the max-tech discussed
in the August 2022 SNOPR.
AHAM and Whirlpool commented that electromagnetic interference
(``EMI'') filtration boards draw a significant amount of power that
DOE's analysis did not take into account. (AHAM, No. 28 at p. 6;
Whirlpool, No. 30, at pp. 2-3) Furthermore, AHAM stated that EMI
filters that draw less power than those currently in use may not be as
effective at filtering out conducted electromagnetic fields (``EMF'').
Whirlpool stated that effective filter designs can account for up to
0.3 W of standby power in a microwave oven. (Whirlpool, No. 30 at p. 4)
AHAM commented that a survey of the current market found filter board
power contributions of 0.17 W for countertop microwave ovens, 0.22 W
for over-the-range microwave ovens, and 0.08 W for built-in microwave
ovens (AHAM, No. 28 at p. 6).
As detailed in chapter 5 of the final rule TSD, DOE conducted a
number of additional standby power tests on a sample of nine microwave
ovens from both product classes after removing their input power
filtration boards. Tested units included inverter microwave ovens,
which tend to have more expensive and complex filtration boards, and
units with different sensors and WiFi functionality.
DOE found that the sampled power filtration boards, on average,
account for only 0.012 W of power during standby testing, calculated as
the difference between the standby power with the filter installed and
the standby power without the filter installed. This average measured
value of 0.012 W is approximately 25 times less than Whirlpool's
estimate (0.3 W) and about 10 times less than the shipment-weighted
average of AHAM's reported values (0.173 W) using shipment weights
provided by Whirlpool in its comments. (Whirlpool, No. 30 at p. 6) DOE
conducted a single-tailed T-test to determine whether AHAM's reported
mean differs in a statistically significant way from the measured mean.
The resulting p-value rejected the null hypothesis (i.e., the
difference is indeed statistically significant and not due to sampling
artifices). Whirlpool commented that DOE's tested models may not
utilize the highest levels of filtering. (Whirlpool, No. 30 at p. 4)
Since neither AHAM nor Whirlpool provided any further information
identifying brands and models used to arrive at these values, DOE
cannot verify the comments that EMI filtration boards take up a
significant amount of a microwave's standby power budget, nor that
DOE's tests were not representative of the market.
DOE performed additional teardown analysis of power filter boards
from tested microwave ovens. All boards were passive filtration boards
that utilize (1) a selection of capacitors and a common mode choke for
mains power filtration; (2) a safety capacitor bleed resistor used to
discharge capacitors that might otherwise shock a user when unplugging
the unit from the wall; and (3) In some cases, a metal oxide varistor
likely for voltage transient suppression. The primary standby power
draw of this circuit is the always-connected bleeder resistor, which
can be further eliminated with minimal impact to EMI filtration quality
by using any number of automatic safety capacitor discharge circuits.
However, this approach to reducing standby power with an automatic
safety capacitor discharge circuit would only be relevant and
meaningful if the power consumption of EMI filters with regular bleed
resistors were significant. As discussed previously, DOE's testing
showed power consumption of EMI filters to be a fraction of what AHAM
and Whirlpool commented. The use of automatic capacitor discharge
circuits would therefore not be meaningful and/or necessary.
Additionally, AHAM commented that microwave ovens account for 40.51
percent of consumer-reported nuisance trips when connected to a mains
line with an arc-fault circuit interrupter (``AFCI'') circuit breaker.
(AHAM, No. 28 at p. 8) AHAM stated that manufacturers traditionally
outfit microwave ovens with EMI filters designed to only meet emissions
limits established by the Federal Communications Commission (``FCC'')
in 47 CFR part 15 and 47 CFR part 18 (referred to as ``Part 15'' and
``Part 18''), and that actual limits for avoiding accidental
``nuisance'' tripping are much more stringent and require EMI filters
that consume more power. (AHAM, No. 28 at pp. 6-8) With increasing use
of AFCIs in homes, Whirlpool commented that DOE must account for the
additional power draw
[[Page 39927]]
of AFCI-compliant EMI filters when amending standards or risk losing
other features that provide consumer utility. (Whirlpool, No. 30 at p.
4)
DOE researched guidance for appliance manufacturers on ensuring
compatibility with AFCI outlets. As part of its efforts to promote the
use of AFCIs, the National Electrical Manufacturer's Association
(``NEMA'') has published guidelines \21\ for appliance manufacturers
that wish to design appliances that are compatible with AFCI outlets.
These guidelines were developed by the Molded Case Circuit Breaker
Product Group of the Low Voltage Distribution Equipment Section of
NEMA. At the time of publication, this group included ABB Control,
Inc.; Eaton Corporation; General Electric; Siemens Industry, Inc.; and
Schneider Electric USA, all manufacturers of AFCIs. Although it is
unclear how many of these members participated in the development of
NEMA's guidance, DOE has not found contradicting guidance from any AFCI
manufacturers.
---------------------------------------------------------------------------
\21\ National Electrical Manufacturer's Association.
Recommendations on AFCI/Home Electrical Product Compatibility. 2011.
Rosslyn, VA.
---------------------------------------------------------------------------
NEMA's white paper describes the emission limits recommendations
for appliance manufacturers. Specifically, NEMA recommends that
manufacturers meet Part 15 requirements for Class B devices, even if
appliances are not subject to these regulations. DOE notes that the
Part 15 requirements for conducted emissions of Class B devices are the
same as the Part 18 requirements for consumer devices other than
induction cooking ranges and ultrasonic equipment. Thus, if
manufacturers are designing microwave ovens to meet Part 18
requirements as AHAM states, they are following the leading industry
guidance for avoiding AFCI nuisance tripping.
Although AHAM commented that AFCIs are being improperly tripped by
normal microwave use, DOE recognizes that there are many potential
sources of arcing in a microwave oven that may be difficult for
consumers to recognize, potentially leading to an over-reporting of
nuisance tripping. Unwanted arcing can occur during cooking if there
are materials that reflect microwaves; the microwave is improperly
loaded (ran empty or nearly empty); or there is a stalled stirrer blade
or non-rotating antenna, which may not be visible to the consumer,
resulting in reflected microwaves. In all three of these cases, the
AFCI is performing its function correctly by detecting arcs and
preventing further power draw, though consumers may not be aware that
these arcs are occurring. Microwave ovens also rely on a number of
relays to control various functionality. Relays, if not properly
implemented, can also be prone to producing excessive arcing that may
trip AFCIs. Thus, AFCIs can correctly trip from detected arcs that may
be invisible to consumers.
In sum, DOE does not find that future EMI filter board designs
would substantively alter the standby power levels that microwave ovens
can achieve and concludes, therefore, that EMI filtration board power
draw will not prohibit future innovation in microwave ovens. Further,
DOE determined that microwave ovens are already meeting the leading
guidance for avoiding nuisance tripping and will continue to do so as
long as manufacturers design according to mandatory FCC standards.
2. Cost Analysis
The cost analysis portion of the engineering analysis is conducted
using one or a combination of cost approaches. The selection of cost
approach depends on a suite of factors, including the availability and
reliability of public information, characteristics of the regulated
product, and the availability and timeliness of purchasing the
microwave oven on the market. The cost approaches are summarized as
follows:
Physical teardowns: Under this approach, DOE physically
dismantles a commercially available product, component-by-component, to
develop a detailed bill of materials for the product.
Catalog teardowns: In lieu of physically deconstructing a
product, DOE identifies each component using parts diagrams (available
from manufacturer websites or appliance repair websites, for example)
to develop the bill of materials for the product.
Price surveys: If neither a physical nor catalog teardown
is feasible (for example, for tightly integrated products such as
fluorescent lamps, which are infeasible to disassemble and for which
parts diagrams are unavailable) or cost-prohibitive and otherwise
impractical (e.g., large commercial boilers), DOE conducts price
surveys using publicly available pricing data published on major online
retailer websites and/or by soliciting prices from distributors and
other commercial channels.
For microwave ovens, DOE attempted to estimate the MPC of attaining
each efficiency level using the physical teardowns approach described
previously. As stated in section IV.A.2 of this document, DOE tore down
all 33 microwave ovens in its test sample but was unable to isolate a
unique set of technology options associated with each standby power
level. As such, DOE concludes that models demonstrating lower standby
power consumption than the current energy conservation standards are
not implementing specific technology options, but rather incorporate a
comprehensive system-level control board design that prioritizes
standby power performance from the ground up. Examples of possible
design strategies include the replacement of microcontrollers and
switch mode controllers with modern ones that demonstrate significantly
lower quiescent current consumption at no additional cost compared to
those found in inefficient systems and firmware that emphasizes the
shutting down of all subassemblies that are not in use while idle. DOE
estimates that, while these improvements would not contribute to an
increase in the MPC of a control board (i.e., incremental MPC of $0),
the redesign would result in conversion costs for manufacturers as they
bring their microwave oven models into compliance with any proposed
standards. See section IV.J.2.a of this document. To account for
manufacturers' non-production costs and profit margin, DOE applies a
multiplier (the manufacturer markup) to the MPC. The resulting MSP is
the price at which the manufacturer distributes a unit into commerce.
DOE developed an average manufacturer markup by examining the annual
Securities and Exchange Commission (``SEC'') 10-K reports filed by
publicly-traded manufacturers primarily engaged in household cooking
appliance manufacturing and whose combined product range includes
microwave ovens.
3. Cost-Efficiency Results
The results of the engineering analysis are reported as cost-
efficiency data (or ``curves'') in the form of MPC (in dollars) versus
standby power consumption (in W). For the reasons discussed in sections
IV.A.2 and IV.C.2 of this document, DOE estimated an incremental MPC of
$0 at all higher efficiency levels, compared to the baseline MPC, for
both of the product classes, as shown in Table IV.5 and Table IV.6 of
this document. See chapter 5 of the final rule TSD for additional
detail on the engineering analysis.
[[Page 39928]]
Table IV.5--Analyzed Efficiency Levels and Incremental Manufacturer
Production Costs for Microwave-Only Ovens and Countertop Convection
Microwave Ovens
------------------------------------------------------------------------
Standby power Incremental
Efficiency level (W) MPC (2021$)
------------------------------------------------------------------------
Baseline................................ 1.00 ..............
1....................................... 0.8 0.0
2....................................... 0.6 0.0
3....................................... 0.4 0.0
------------------------------------------------------------------------
Table IV.6--Analyzed Efficiency Levels and Incremental Manufacturer
Production Costs for Built-In and Over-the-Range Convection Microwave
Ovens
------------------------------------------------------------------------
Standby power Incremental
Efficiency level (W) MPC (2021$)
------------------------------------------------------------------------
Baseline................................ 2.20 ..............
1....................................... 1.5 $0.0
2....................................... 1.00 $0.0
3....................................... 0.5 $0.0
------------------------------------------------------------------------
D. Markups Analysis
The markups analysis develops appropriate markups (e.g., retailer
markups, distributor markups, contractor markups) in the distribution
chain and sales taxes to convert the MSP estimates derived in the
engineering analysis to consumer prices, which are then used in the LCC
and PBP analysis. At each step in the distribution channel, companies
mark up the price of the product to cover business costs and profit
margin.
For microwave ovens, DOE further developed baseline and incremental
markups for each link in the distribution chain (after the product
leaves the manufacturer). Baseline markups are applied to the price of
products with baseline efficiency, while incremental markups are
applied to the difference in price between baseline and higher-
efficiency models (the incremental cost increase). The incremental
markup is typically less than the baseline markup and is designed to
maintain similar per-unit operating profit before and after new or
amended standards.\22\
---------------------------------------------------------------------------
\22\ Because the projected price of standards-compliant products
is typically higher than the price of baseline products, using the
same markup for the incremental cost and the baseline cost would
result in higher per-unit operating profit. While such an outcome is
possible, DOE maintains that in markets that are reasonably
competitive, it is unlikely that standards would lead to a
sustainable increase in profitability in the long run.
---------------------------------------------------------------------------
DOE relied on economic data from the U.S. Census Bureau to estimate
average baseline and incremental markups. Specifically, DOE used the
2017 Annual Retail Trade Survey for the ``electronics and appliance
stores'' sector to develop retailer markups.\23\
---------------------------------------------------------------------------
\23\ US Census Bureau, Annual Retail Trade Survey. 2017.
www.census.gov/programs-surveys/arts.html.
---------------------------------------------------------------------------
Chapter 6 of the final rule TSD provides details on DOE's
development of markups for microwave ovens.
E. Energy Use Analysis
The purpose of the energy use analysis is to determine the annual
energy consumption of microwave ovens at different efficiencies in
representative U.S. single-family homes, multi-family residences, and
mobile homes, and to assess the energy savings potential of increased
microwave ovens efficiency. The energy use analysis estimates the range
of energy use of microwave ovens in the field (i.e., as they are
actually used by consumers). The energy use analysis provides the basis
for other analyses DOE performed, particularly assessments of the
energy savings and the savings in consumer operating costs that could
result from adoption of amended or new standards.
For this final rule, DOE used the same methodology as that
described in section IV.D of the August 2022 SNOPR. In the June 2013
Final Rule, DOE determined the average hours of operation for microwave
ovens to be 44.9 hours per year.24 25 To calibrate the
average annual operating hours, DOE primarily used data from the EIA's
2020 Residential Energy Consumption Survey (``RECS'').\26\ RECS 2020
provides information on the frequency of microwave oven usage per week
for each household. DOE calculated the RECS microwave oven usage factor
for each household in the sample by dividing the weighted-average usage
based on the entire RECS samples. DOE then multiplied the usage factor
by the annual operating hours (i.e., 44.9 hours) for each household in
the RECS. DOE subtracted field microwave ovens operating hours from the
total number of hours in a year and multiplied that difference by the
standby mode power usage at each efficiency level to determine annual
standby mode and off mode energy consumption.
---------------------------------------------------------------------------
\24\ Uniform Test Method for Measuring the Energy Consumption of
Cooking Products. 10 CFR part 430, subpart B, appendix I,
www.law.cornell.edu/cfr/text/10/appendix-I_to_subpart_B_of_part_430.
\25\ Williams, et al. 2012. Surveys of Microwave Ovens in U.S.
Homes. LBNL-5947E www.osti.gov/biblio/1172657.
\26\ U.S. Department of Energy-Energy Information
Administration, Residential Energy Consumption Survey, 2020 Public
Use Microdata Files, 2015. Washington, DC. Available online at:
www.eia.doe.gov/emeu/recs/recspubuse20/pubuse20.html.
---------------------------------------------------------------------------
Chapter 7 of the final rule TSD provides details on DOE's energy
use analysis for microwave ovens.
F. Life-Cycle Cost and Payback Period Analysis
DOE conducted LCC and PBP analyses to evaluate the economic impacts
on individual consumers of potential energy conservation standards for
microwave ovens. The effect of new or amended energy conservation
standards on individual consumers usually involves a reduction in
operating cost and an increase in purchase cost. DOE used the following
two metrics to measure consumer impacts:
The LCC is the total consumer expense of an appliance or
product over the life of that product, consisting of
[[Page 39929]]
total installed cost (manufacturer selling price, distribution chain
markups, sales tax, and installation costs) plus operating costs
(expenses for energy use, maintenance, and repair). To compute the
operating costs, DOE discounts future operating costs to the time of
purchase and sums them over the lifetime of the product.
The PBP is the estimated amount of time (in years) it
takes consumers to recover the increased purchase cost (including
installation) of a more-efficient product through lower operating
costs. DOE calculates the PBP by dividing the change in purchase cost
at higher efficiency levels by the change in annual operating cost for
the year that amended or new standards are assumed to take effect.
For any given efficiency level, DOE measures the change in LCC
relative to the LCC in the no-new-standards case, which reflects the
estimated efficiency distribution of microwave ovens in the absence of
new or amended energy conservation standards. In contrast, the PBP for
a given efficiency level is measured relative to the baseline product.
For each considered efficiency level in each product class, DOE
calculated the LCC and PBP for a nationally representative set of
housing units. As stated previously, DOE developed household samples
from the RECS 2020. For each sample household, DOE determined the
energy consumption for the microwave ovens and the appropriate energy
price. By developing a representative sample of households, the
analysis captured the variability in energy consumption and energy
prices associated with the use of microwave ovens.
Inputs to the calculation of total installed cost include the cost
of the product--which includes MPCs, manufacturer markups, retailer and
distributor markups, and sales taxes--and installation costs. Inputs to
the calculation of operating expenses include annual energy
consumption, energy prices and price projections, repair and
maintenance costs, product lifetimes, and discount rates. DOE created
distributions of values for product lifetime, discount rates, and sales
taxes, with probabilities attached to each value, to account for their
uncertainty and variability.
The computer model DOE uses to calculate the LCC relies on a Monte
Carlo simulation to incorporate uncertainty and variability into the
analysis. The Monte Carlo simulations randomly sample input values from
the probability distributions and microwave ovens user samples. For
this rulemaking, the Monte Carlo approach is implemented in MS Excel
together with the Crystal BallTM add-on.\27\ The model
calculated the LCC for products at each efficiency level for 10,000
housing units per simulation run. The analytical results include a
distribution of 10,000 data points showing the range of LCC savings for
a given efficiency level relative to the no-new-standards case
efficiency distribution. In performing an iteration of the Monte Carlo
simulation for a given consumer, product efficiency is chosen based on
its probability. If the chosen product efficiency is greater than or
equal to the efficiency of the standard level under consideration, the
LCC calculation reveals that a consumer is not impacted by the standard
level. By accounting for consumers who already purchase more-efficient
products, DOE avoids overstating the potential benefits from increasing
product efficiency. DOE calculated the LCC and PBP for consumers of
microwave ovens as if each were to purchase a new product in the first
year of required compliance with new or amended standards. Amended
standards apply to microwave ovens manufactured 3 years after the date
on which any new or amended standard is published. (42 U.S.C.
6295(g)(10)(B)) Therefore, DOE used 2026 as the first year of
compliance with any amended standards for microwave ovens.
---------------------------------------------------------------------------
\27\ Crystal BallTM is a commercially-available
software tool to facilitate the creation of these types of models by
generating probability distributions and summarizing results within
Excel, available at www.oracle.com/technetwork/middleware/crystalball/overview/ (last accessed December 13, 2022).
---------------------------------------------------------------------------
Table IV.5 summarizes the approach and data DOE used to derive
inputs to the LCC and PBP calculations. The subsections that follow
provide further discussion. Details of the spreadsheet model, and of
all the inputs to the LCC and PBP analyses, are contained in chapter 8
of the final rule TSD and its appendices.
Table IV.5--Summary of Inputs and Methods for the LCC and PBP Analysis *
------------------------------------------------------------------------
Inputs Source/method
------------------------------------------------------------------------
Product Cost........................... Derived by multiplying MPCs by
manufacturer and retailer
markups and sales tax, as
appropriate. Used historical
data to derive a price scaling
index to project product
costs.
Installation Costs..................... Assumed no change with
efficiency level.
Annual Energy Use...................... The total annual energy use
multiplied by the hours per
year. Average number of hours
based on field data.
Variability: Based on the RECS
2020.
Energy Prices.......................... Electricity: Based on EEI 2021.
Variability: Regional energy
prices determined for nine
regions.
Energy Price Trends.................... Based on AEO2022 price
projections.
Repair and Maintenance Costs........... Assumed no change with
efficiency level.
Product Lifetime....................... Average: 10.78 years.
Discount Rates......................... Approach involves identifying
all possible debt or asset
classes that might be used to
purchase the considered
appliances, or might be
affected indirectly. Primary
data source was the Federal
Reserve Board's Survey of
Consumer Finances.
Compliance Date........................ 2026.
------------------------------------------------------------------------
* Not used for PBP calculation. References for the data sources
mentioned in this table are provided in the sections following the
table or in chapter 8 of the final rule TSD.
1. Product Cost
To calculate consumer product costs, DOE multiplied the MPCs
developed in the engineering analysis by the markups described
previously (along with sales taxes). DOE used different markups for
baseline products and higher-efficiency products, because DOE applies
an incremental markup to the increase in MSP associated with higher-
efficiency products.
Economic literature and historical data suggest that the real costs
of many products may trend downward over time according to ``learning''
or ``experience'' curves. An experience curve analysis implicitly
includes factors such as efficiencies in labor, capital investment,
automation, materials prices, distribution, and economies of scale at
an industry-wide level. To derive the learning rate parameter for
microwave ovens, DOE obtained historical Producer Price Index (``PPI'')
data for microwave ovens from the Bureau of Labor Statistics (``BLS'').
A PPI for ``Household Cooking Appliance Manufacturing: Electric
(Including Microwave) Household Ranges, Ovens, Surface Cooking Units,
[[Page 39930]]
and Equipment'' was available for the time period between 1972 and
2020.\28\ Inflation-adjusted price indices were calculated by dividing
the PPI series by the gross domestic product index from the Bureau of
Economic Analysis for the same years. Using data from 1972-2020, the
estimated learning rate (defined as the fractional reduction in price
expected from each doubling of cumulative production) is 10.7 percent.
---------------------------------------------------------------------------
\28\ U.S. Bureau of Labor Statistics, PPI Industry Data, Major
household appliance manufacturers, Product series ID: PCU
33522033522011. Data series available at: www.bls.gov/ppi/.
---------------------------------------------------------------------------
2. Installation Cost
Installation cost includes labor, overhead, and any miscellaneous
materials and parts needed to install the product. DOE used data from
2022 to estimate the baseline installation cost for microwave ovens.
DOE found no evidence that installation costs would be impacted with
increased efficiency levels.
3. Annual Energy Consumption
For each sampled household, DOE determined the energy consumption
for a microwave oven at different efficiency levels using the approach
described previously in section IV.E of this document.
4. Energy Prices
Because marginal electricity price more accurately captures the
incremental savings associated with a change in energy use from higher
efficiency, it provides a better representation of incremental change
in consumer costs than average electricity prices. Therefore, DOE
applied average electricity prices for the energy use of the product
purchased in the no-new-standards case, and marginal electricity prices
for the incremental change in energy use associated with the other
efficiency levels considered.
DOE derived electricity prices in 2022 using data from Edison
Electric Institute (``EEI'') Typical Bills and Average Rates
reports.\29\ Based upon comprehensive, industry-wide surveys, this
semi-annual report presents typical monthly electric bills and average
kilowatt-hour costs to the customer as charged by investor-owned
utilities. For the residential sector, DOE calculated electricity
prices using the methodology described in Coughlin and Beraki
(2018).\30\ For the commercial sector, DOE calculated electricity
prices using the methodology described in Coughlin and Beraki
(2019).\31\
---------------------------------------------------------------------------
\29\ Edison Electric Institute. Typical Bills and Average Rates
Report. 2020. Winter 2020, Summer 2020: Washington, DC
\30\ Coughlin, K. and B. Beraki.2018. Residential Electricity
Prices: A Review of Data Sources and Estimation Methods. Lawrence
Berkeley National Lab. Berkeley, CA. Report No. LBNL-2001169.
ees.lbl.gov/publications/residential-electricity-prices-review.
\31\ Coughlin, K. and B. Beraki. 2019. Non-residential
Electricity Prices: A Review of Data Sources and Estimation Methods.
Lawrence Berkeley National Lab. Berkeley, CA. Report No. LBNL-
2001203. ees.lbl.gov/publications/non-residential-electricity-prices.
---------------------------------------------------------------------------
DOE's methodology allows electricity prices to vary by sector,
region, and season. In the analysis, variability in electricity prices
is chosen to be consistent with the way the consumer economic and
energy use characteristics are defined in the LCC analysis. For
microwave ovens, DOE derived electricity prices in 2022 using data from
EEI. DOE used the EEI data to define a marginal price as the ratio of
the change in the bill to the change in energy consumption. See chapter
8 of the final rule TSD for details.
To estimate energy prices in future years, DOE multiplied the 2020
energy prices by the projection of annual average price changes for
each of the nine census divisions from the Reference case in AEO2022,
which has an end year of 2050.\32\ To estimate price trends after 2050,
the 2046-2050 average was used for all subsequent years.
---------------------------------------------------------------------------
\32\ U.S. Department of Energy--Energy Information
Administration. Annual Energy Outlook 2018 with Projections to 2050.
Washington, DC. Available at www.eia.gov/forecasts/aeo/ (last
accessed December 13, 2022).
---------------------------------------------------------------------------
5. Maintenance and Repair Costs
Repair costs are associated with repairing or replacing product
components that have failed in an appliance; maintenance costs are
associated with maintaining the operation of the product. Typically,
small incremental increases in product efficiency entail no, or only
minor, changes in repair and maintenance costs compared to baseline
efficiency products. In this final rule analysis, DOE included no
changes in maintenance or repair costs for microwave ovens that exceed
baseline efficiency.
6. Product Lifetime
For microwave ovens, DOE developed a distribution of lifetimes from
which specific values are assigned to the appliances in the samples.
DOE conducted an analysis of actual lifetime in the field using a
combination of historical shipments data, the stock of the considered
appliances in the American Housing Survey, and responses in RECS on the
age of the appliances in the homes. The data allowed DOE to estimate a
survival function, which provides an average appliance lifetime. This
analysis yielded a lifetime probability distribution with an average
lifetime for microwave ovens of approximately 10.78 years. See chapter
8 of the final rule TSD for further details.
7. Discount Rates
In the calculation of LCC, DOE applies discount rates appropriate
to households to estimate the present value of future operating cost
savings. DOE estimated a distribution of discount rates for microwave
ovens based on the opportunity cost of consumer funds.
DOE applies weighted average discount rates calculated from
consumer debt and asset data, rather than marginal or implicit discount
rates.\33\ The LCC analysis estimates net present value over the
lifetime of the product, so the appropriate discount rate will reflect
the general opportunity cost of household funds, taking this time scale
into account. Given the long time horizon modeled in the LCC, the
application of a marginal interest rate associated with an initial
source of funds is inaccurate. Regardless of the method of purchase,
consumers are expected to continue to rebalance their debt and asset
holdings over the LCC analysis period, based on the restrictions
consumers face in their debt payment requirements and the relative size
of the interest rates available on debts and assets. DOE estimates the
aggregate impact of this rebalancing using the historical distribution
of debts and assets.
---------------------------------------------------------------------------
\33\ The implicit discount rate is inferred from a consumer
purchase decision between two otherwise identical goods with
different first cost and operating cost. It is the interest rate
that equates the increment of first cost to the difference in net
present value of lifetime operating cost, incorporating the
influence of several factors: transaction costs; risk premiums and
response to uncertainty; time preferences; and interest rates at
which a consumer is able to borrow or lend. The implicit discount
rate is not appropriate for the LCC analysis because it reflects a
range of factors that influence consumer purchase decisions, rather
than the opportunity cost of the funds that are used in purchases.
---------------------------------------------------------------------------
To establish residential discount rates for the LCC analysis, DOE
identified all relevant household debt or asset classes in order to
approximate a consumer's opportunity cost of funds related to appliance
energy cost savings. It estimated the average percentage shares of the
various types of debt and equity by household income group using data
from the Federal Reserve Board's triennial Survey of Consumer
[[Page 39931]]
Finances \34\ (``SCF'') starting in 1995 and ending in 2019. Using the
SCF and other sources, DOE developed a distribution of rates for each
type of debt and asset by income group to represent the rates that may
apply in the year in which amended standards would take effect. DOE
assigned each sample household a specific discount rate drawn from one
of the distributions. The average rate across all types of household
debt and equity and income groups, weighted by the shares of each type,
is 4.3 percent. See chapter 8 of the final rule TSD for further details
on the development of consumer discount rates.
---------------------------------------------------------------------------
\34\ U.S. Board of Governors of the Federal Reserve System.
Survey of Consumer Finances. 1995, 1998, 2001, 2004, 2007, 2010,
2013, 2016, and 2019. Available at www.Federalreserve.gov/econresdata/scf/scfindex.htm (last accessed December 13, 2022).
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8. Energy Efficiency Distribution in the No-New-Standards Case
To accurately estimate the share of consumers that would be
affected by a potential energy conservation standard at a particular
efficiency level, DOE's LCC analysis considered the projected
distribution (market shares) of product efficiencies under the no-new-
standards case (i.e., the case without amended or new energy
conservation standards).
To estimate the energy efficiency distribution of microwave ovens
for 2026, DOE used data from the engineering analysis. The estimated
market shares for the no-new-standards case for microwave ovens are
shown in Table IV.6. See chapter 8 of the final rule TSD for further
information on the derivation of the efficiency distributions.
Table IV.6--No-New-Standards Case Efficiency Distribution for Microwave Ovens in 2026
----------------------------------------------------------------------------------------------------------------
Product class 1: microwave- Product class 2: built-in and
only and countertop convection over-the- range convection
microwave ovens microwave ovens
TSL ---------------------------------------------------------------
Standby power Market share Standby power Market share
(W) (%) (W) (%)
----------------------------------------------------------------------------------------------------------------
Baseline........................................ 1.00 15 2.20 0
1............................................... 0.8 45 1.5 36
2............................................... 0.6 29 1.0 59
3............................................... 0.4 11 0.5 5
----------------------------------------------------------------------------------------------------------------
In response to the August 2023 SNOPR, AHAM stated that the CCD is
not an accurate determination of efficiency distributions. (AHAM, No.
28 at p. 10) DOE agrees that shipment-weighted efficiency distributions
would be preferable to shares based on model counts, but such data were
not available for microwave ovens, and there is no firm basis to make
an adjustment to the model count market shares. DOE's approach may well
overstate the market share of higher-efficiency products in the absence
of new standards, but this would mean that the energy and economic
benefits estimated by DOE for new standards are minimum amounts. The
justification for the adopted standards would be even stronger if DOE
were able to use actual shipment data for the model counts.
The LCC Monte Carlo simulations draw from the efficiency
distributions and randomly assign an efficiency to the microwave oven
purchased by each sample household in the no-new-standards case. The
resulting percent shares within the sample match the market shares in
the efficiency distributions.
9. Payback Period Analysis
The payback period is the amount of time (expressed in years) it
takes the consumer to recover the additional installed cost of more-
efficient products, compared to baseline products, through energy cost
savings. Payback periods that exceed the life of the product mean that
the increased total installed cost is not recovered in reduced
operating expenses.
The inputs to the PBP calculation for each efficiency level are the
change in total installed cost of the product and the change in the
first-year annual operating expenditures relative to the baseline. DOE
refers to this as a ``simple PBP'' because it does not consider changes
over time in operating cost savings. The PBP calculation uses the same
inputs as the LCC analysis when deriving first-year operating costs.
As noted previously, EPCA establishes a rebuttable presumption that
a standard is economically justified if the Secretary finds that the
additional cost to the consumer of purchasing a product complying with
an energy conservation standard level will be less than three times the
value of the first year's energy savings resulting from the standard,
as calculated under the applicable test procedure. (42 U.S.C.
6295(o)(2)(B)(iii)) For each considered efficiency level, DOE
determined the value of the first year's energy savings by calculating
the energy savings in accordance with the applicable DOE test
procedure, and multiplying those savings by the average energy price
projection for the year in which compliance with the amended standards
would be required.
G. Shipments Analysis
DOE uses projections of annual product shipments to calculate the
national impacts of potential amended or new energy conservation
standards on energy use, NPV, and future manufacturer cash flows.\35\
The shipments model takes an accounting approach, tracking market
shares of each product class and the vintage of units in the stock.
Stock accounting uses product shipments as inputs to estimate the age
distribution of in-service product stocks for all years. The age
distribution of in-service product stocks is a key input to
calculations of both the NES and NPV, because operating costs for any
year depend on the age distribution of the stock.
---------------------------------------------------------------------------
\35\ DOE uses data on manufacturer shipments as a proxy for
national sales, as aggregate data on sales are lacking. In general,
one would expect a close correspondence between shipments and sales.
---------------------------------------------------------------------------
Total shipments for microwave ovens are developed by considering
the demand from replacements for units in stock that fail and the
demand from new installations in newly constructed homes. DOE
calculated shipments due to replacements using the retirement function
developed for the LCC analysis and historical data from AHAM. DOE
calculated shipments due to new installations using estimates from the
microwave oven saturation rate in new homes in RECS 2020 and
projections of new housing starts from AEO2022. See
[[Page 39932]]
chapter 9 of the final rule TSD for details.
For this final rule analysis, DOE used data from a market research
report and estimated the market share for built-in and over-the-range
convection microwave ovens at 4 percent.\36\
---------------------------------------------------------------------------
\36\ Euromonitor International. 2021. Air treatment products in
the U.S. December.
---------------------------------------------------------------------------
DOE considers the impacts on shipments from changes in product
purchase price and operating cost associated with higher energy
efficiency levels using a price elasticity and an efficiency
elasticity. DOE employs a 0.2-percent efficiency elasticity rate and a
price elasticity of -0.45 in its shipments model.\37\ The market impact
is defined as the difference between the product of price elasticity of
demand and the change in price due to a standard level, and the product
of the efficiency elasticity and the change in operating costs due to a
standard level.
---------------------------------------------------------------------------
\37\ Fujita, K. (2015) Estimating Price Elasticity using Market-
Level Appliance Data. Lawrence Berkeley National Laboratory, LBNL-
188289.
---------------------------------------------------------------------------
H. National Impact Analysis
The NIA assesses the NES and the NPV from a national perspective of
total consumer costs and savings that would be expected to result from
new or amended standards at specific efficiency levels.\38\
(``Consumer'' in this context refers to consumers of the product being
regulated.) DOE calculates the NES and NPV for the potential standard
levels considered based on projections of annual product shipments,
along with the annual energy consumption and total installed cost data
from the energy use and LCC analyses. For the present analysis, DOE
projected the energy savings, operating cost savings, product costs,
and NPV of consumer benefits over the lifetime of microwave ovens sold
from 2026 through 2055.
---------------------------------------------------------------------------
\38\ The NIA accounts for impacts in the 50 states.
---------------------------------------------------------------------------
DOE evaluates the impacts of new or amended standards by comparing
a case without such standards with standards-case projections. The no-
new-standards case characterizes energy use and consumer costs for each
product class in the absence of new or amended energy conservation
standards. For this projection, DOE considers historical trends in
efficiency and various forces that are likely to affect the mix of
efficiencies over time. DOE compares the no-new-standards case with
projections characterizing the market for each product class if DOE
adopted new or amended standards at specific energy efficiency levels
(i.e., the TSLs or standards cases) for that class. For the standards
cases, DOE considers how a given standard would likely affect the
market shares of products with efficiencies greater than the standard.
DOE uses a spreadsheet model to calculate the energy savings and
the national consumer costs and savings from each TSL. Interested
parties can review DOE's analyses by changing various input quantities
within the spreadsheet. The NIA spreadsheet model uses typical values
(as opposed to probability distributions) as inputs.
Table IV.7 summarizes the inputs and methods DOE used for the NIA
analysis for the final rule. Discussion of these inputs and methods
follows the table. See chapter 10 of the final rule TSD for further
details.
Table IV.7--Summary of Inputs and Methods for the National Impact
Analysis
------------------------------------------------------------------------
Inputs Method
------------------------------------------------------------------------
Shipments.................... Annual shipments from shipments model.
Compliance Date of Standard.. 2026.
Efficiency Trends............ Standards cases: ``Roll up'' equipment to
meet potential efficiency level.
Annual Energy Consumption per Annual weighted-average values are a
Unit. function of energy use at each TSL.
Total Installed Cost per Unit Annual weighted-average values are a
function of cost at each TSL.
Annual Energy Cost per Unit.. Annual weighted-average values as a
function of the annual energy
consumption per unit and energy prices.
Repair and Maintenance Cost Annual values do not change with
per Unit. efficiency level.
Energy Price Trends.......... AEO2022 projections (to 2050) and
extrapolation thereafter.
Energy Site-to-Primary and A time-series conversion factor based on
FFC Conversion. AEO2022.
Discount Rate................ Three and seven percent.
Present Year................. 2023.
------------------------------------------------------------------------
1. Product Efficiency Trends
A key component of the NIA is the trend in energy efficiency
projected for the no-new-standards case and each of the standards
cases. Section IV.F.8 of this document describes how DOE developed an
energy efficiency distribution for the no-new-standards case (which
yields a shipment-weighted average efficiency) for each of the
considered product classes for the year of anticipated compliance with
an amended or new standard. To project the trend in efficiency absent
amended standards for microwave ovens over the entire shipments
projection period, DOE used the shipments-weighted standby power
(``SWSP'') as a starting point. DOE assumed that the shipment-weighted
efficiency would not increase annually for the microwave oven product
classes. The approach is further described in chapter 10 of the final
rule TSD.
For the standards cases, DOE used a ``roll-up'' scenario to
establish the shipment-weighted efficiency for the year that standards
are assumed to become effective (2026). In this scenario, the market
shares of products in the no-new-standards case that do not meet the
standard under consideration would ``roll up'' to meet the new standard
level, and the market share of products above the standard would remain
unchanged.
2. National Energy Savings
The national energy savings analysis involves a comparison of
national energy consumption of the considered products between each TSL
and the case with no new or amended energy conservation standards. DOE
calculated the national energy consumption by multiplying the number of
units (stock) of each product (by vintage or age) by the unit energy
consumption (also by vintage). DOE calculated annual NES based on the
difference in national energy consumption for the no-new-standards case
and for each higher efficiency standard case. DOE estimated energy
consumption and savings based on site energy and converted the
electricity consumption and savings to primary energy (i.e., the energy
consumed by power plants to generate site electricity) using annual
conversion factors derived from AEO2022.
[[Page 39933]]
Cumulative energy savings are the sum of the NES for each year over the
timeframe of the analysis.
Use of higher-efficiency products is sometimes associated with a
direct rebound effect, which refers to an increase in utilization of
the product due to the increase in efficiency. DOE did not find any
data on the rebound effect specific to microwave ovens; therefore, no
rebound was applied.
In 2011, in response to the recommendations of a committee on
``Point-of-Use and Full-Fuel-Cycle Measurement Approaches to Energy
Efficiency Standards'' appointed by the National Academy of Sciences,
DOE announced its intention to use FFC measures of energy use and
greenhouse gas and other emissions in the national impact analyses and
emissions analyses included in future energy conservation standards
rulemakings. 76 FR 51281 (Aug. 18, 2011). After evaluating the
approaches discussed in the August 18, 2011 notice, DOE published a
statement of amended policy in which DOE explained its determination
that EIA's National Energy Modeling System (``NEMS'') is the most
appropriate tool for its FFC analysis and its intention to use NEMS for
that purpose. 77 FR 49701 (Aug. 17, 2012). NEMS is a public domain,
multi-sector, partial equilibrium model of the U.S. energy sector \39\
that EIA uses to prepare its Annual Energy Outlook. The FFC factors
incorporate losses in production and delivery in the case of natural
gas (including fugitive emissions) and additional energy used to
produce and deliver the various fuels used by power plants. The
approach used for deriving FFC measures of energy use and emissions is
described in appendix 10B of the final rule TSD.
---------------------------------------------------------------------------
\39\ For more information on NEMS, refer to The National Energy
Modeling System: An Overview 2009, DOE/EIA-0581(2009), October 2009.
Available at www.eia.gov/forecasts/aeo/index.cfm (last accessed
December 13, 2022).
---------------------------------------------------------------------------
3. Net Present Value Analysis
The inputs for determining the NPV of the total costs and benefits
experienced by consumers are (1) total annual installed cost, (2) total
annual operating costs (energy costs and repair and maintenance costs),
and (3) a discount factor to calculate the present value of costs and
savings. DOE calculates net savings each year as the difference between
the no-new-standards case and each standards case in terms of total
savings in operating costs versus total increases in installed costs.
DOE calculates operating cost savings over the lifetime of each product
shipped during the projection period.
As discussed in section IV.F.1 of this document, DOE developed
microwave oven price trends based on historical PPI data. DOE applied
the same trends to project prices for each product class at each
considered efficiency level. By 2055, which is the end date of the
projection period, the average microwave oven price is projected to
drop 11 percent relative to 2021. DOE's projection of product prices is
described in appendix 10C of the final rule TSD.
To evaluate the effect of uncertainty regarding the price trend
estimates, DOE investigated the impact of different product price
projections on the consumer NPV for the considered TSLs for microwave
ovens. In addition to the default price trend, DOE considered two
product price sensitivity cases: (1) a high price decline case based on
``electric household cooking products'' PPI series from 1993 to 2021
and (2) a low price decline case based on the same PPI series from 1972
to 1992. The derivation of these price trends and the results of these
sensitivity cases are described in appendix 10C of the final rule TSD.
The energy cost savings are calculated using the estimated energy
savings in each year and the projected price of the appropriate form of
energy. To estimate energy prices in future years, DOE multiplied the
average regional energy prices by the projection of annual national-
average residential energy price changes in the Reference case from
AEO2022, which has an end year of 2050. To estimate price trends after
2050, the 2046-2050 average was used for all years. As part of the NIA,
DOE also analyzed scenarios that used inputs from variants of the
AEO2022 Reference case that have lower and higher economic growth.
Those cases have lower and higher energy price trends compared to the
Reference case. NIA results based on these cases are presented in
appendix 10C of the final rule TSD.
In considering the consumer welfare gained due to the direct
rebound effect, DOE accounted for change in consumer surplus attributed
to additional cooling from the purchase of a more efficient unit.
Overall consumer welfare is generally understood to be enhanced from
rebound. The net consumer impact of the rebound effect is included in
the calculation of operating cost savings in the consumer NPV results.
See appendix 10F of the final rule TSD for details on DOE's treatment
of the monetary valuation of the rebound effect.
In calculating the NPV, DOE multiplies the net savings in future
years by a discount factor to determine their present value. For this
final rule, DOE estimated the NPV of consumer benefits using both a 3-
percent and a 7-percent real discount rate. DOE uses these discount
rates in accordance with guidance provided by the Office of Management
and Budget (``OMB'') to Federal agencies on the development of
regulatory analysis.\40\ The discount rates for the determination of
NPV are in contrast to the discount rates used in the LCC analysis,
which are designed to reflect a consumer's perspective. The 7-percent
real value is an estimate of the average before-tax rate of return to
private capital in the U.S. economy. The 3-percent real value
represents the ``social rate of time preference,'' which is the rate at
which society discounts future consumption flows to their present
value.
---------------------------------------------------------------------------
\40\ United States Office of Management and Budget. Circular A-
4: Regulatory Analysis. September 17, 2003. Section E. Available at
obamawhitehouse.archives.gov/omb/circulars_a004_a-4/ (last accessed
December 13, 2022).
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I. Consumer Subgroup Analysis
In analyzing the potential impact of new or amended energy
conservation standards on consumers, DOE evaluates the impact on
identifiable subgroups of consumers that may be disproportionately
affected by a new or amended national standard. The purpose of a
subgroup analysis is to determine the extent of any such
disproportional impacts. DOE evaluates impacts on particular subgroups
of consumers by analyzing the LCC impacts and PBP for those particular
consumers from alternative standard levels. For this final rule, DOE
analyzed the impacts of the considered standard levels on two
subgroups: (1) low-income households and (2) senior-only households.
The analysis used subsets of the RECS 2020 sample composed of
households that meet the criteria for the considered subgroups. DOE
used the LCC and PBP spreadsheet model to estimate the impacts of the
considered efficiency levels on these subgroups. Chapter 11 of the
final rule TSD describes the consumer subgroup analysis.
J. Manufacturer Impact Analysis
1. Overview
DOE performed an MIA to estimate the financial impacts of amended
energy conservation standards on manufacturers of microwave ovens and
to estimate the potential impacts of such standards on employment and
manufacturing capacity. The MIA has both quantitative and qualitative
aspects and includes analyses of projected
[[Page 39934]]
industry cash flows, the INPV, investments in research and development
(``R&D'') and manufacturing capital, and domestic manufacturing
employment. Additionally, the MIA seeks to determine how amended energy
conservation standards might affect manufacturing employment, capacity,
and competition, as well as how standards contribute to overall
regulatory burden. Finally, the MIA serves to identify any
disproportionate impacts on manufacturer subgroups, including small
business manufacturers.
The quantitative part of the MIA primarily relies on the Government
Regulatory Impact Model (``GRIM''), an industry cash flow model with
inputs specific to this rulemaking. The key GRIM inputs include data on
the industry cost structure, unit production costs, product shipments,
manufacturer markups, and investments in R&D and manufacturing capital
required to produce compliant products. The key GRIM outputs are the
INPV, which is the sum of industry annual cash flows over the analysis
period, discounted using the industry-weighted average cost of capital,
and the impact to domestic manufacturing employment. The model uses
standard accounting principles to estimate the impacts of more-
stringent energy conservation standards on a given industry by
comparing changes in INPV and domestic manufacturing employment between
a no-new-standards case and the various standards cases (TSLs). To
capture the uncertainty relating to manufacturer pricing strategies
following amended standards, the GRIM estimates a range of possible
impacts under different markup scenarios.
The qualitative part of the MIA addresses manufacturer
characteristics and market trends. Specifically, the MIA considers such
factors as a potential standard's impact on manufacturing capacity,
competition within the industry, the cumulative impact of other DOE and
non-DOE regulations, and impacts on manufacturer subgroups. The
complete MIA is outlined in chapter 12 of the final rule TSD.
DOE prepared a profile of the microwave oven manufacturing industry
based on the market and technology assessment, current information from
DOE's CCD, and information from the June 2013 Final Rule. (78 FR 36316)
This included a top-down analysis of microwave oven manufacturers that
DOE used to derive preliminary financial inputs for the GRIM (e.g.,
revenues; materials, labor, overhead, and depreciation expenses; SG&A
expenses; and R&D expenses).
Additionally, DOE prepared a framework industry cash-flow analysis
to quantify the potential impacts of amended energy conservation
standards. The GRIM uses several factors to determine a series of
annual cash flows starting with the announcement of the standard and
extending over a 30-year period following the compliance date of the
standard. These factors include annual expected revenues, costs of
sales, SG&A and R&D expenses, taxes, and capital expenditures. In
general, energy conservation standards can affect manufacturer cash
flow in three distinct ways: (1) creating a need for increased
investment, (2) raising production costs per unit, and (3) altering
revenue due to higher per-unit prices and changes in sales volumes.
DOE also evaluated subgroups of manufacturers that may be
disproportionately impacted by amended standards or that may not be
accurately represented by the average cost assumptions used to develop
the industry cash flow analysis. Such manufacturer subgroups may
include small business manufacturers, low-volume manufacturers, niche
players, and/or manufacturers exhibiting a cost structure that largely
differs from the industry average. DOE identified one subgroup for a
separate impact analysis: small business manufacturers. The small
business subgroup is discussed in section VI.B of this document,
``Review under the Regulatory Flexibility Act'' and in chapter 12 of
the final rule TSD.
2. Government Regulatory Impact Model and Key Inputs
DOE uses the GRIM to quantify the changes in cash flow due to
amended standards that result in a higher or lower industry value. The
GRIM uses a standard, annual discounted cash-flow analysis that
incorporates manufacturer costs, markups, shipments, and industry
financial information as inputs. The GRIM models changes in costs,
distribution of shipments, investments, and manufacturer margins that
could result from amended energy conservation standards. The GRIM
spreadsheet uses the inputs to arrive at a series of annual cash flows,
beginning in 2023 (the base year of the analysis) and continuing to
2055. DOE calculated INPVs by summing the stream of annual discounted
cash flows during this period. For manufacturers of microwave ovens,
DOE used a real discount rate of 8.5 percent, which was the same real
discount rate used in the June 2013 Final Rule and that was verified
during manufacturer interviews for that rulemakings analysis.
The GRIM calculates cash flows using standard accounting principles
and compares changes in INPV between the no-new-standards case and each
standards case. The difference in INPV between the no-new-standards
case and a standards case represents the financial impact of the
amended energy conservation standards on manufacturers. As discussed
previously, DOE developed critical GRIM inputs using a number of
sources, including publicly available data, results of the engineering
analysis, and information used in the June 2013 Final Rule. The GRIM
results are presented in section V.B.2 of this document. Additional
details about the GRIM, the discount rate, and other financial
parameters can be found in chapter 12 of the final rule TSD.
a. Manufacturer Production Costs
Manufacturing more efficient products is typically more expensive
than manufacturing baseline products due to the use of more complex
components, which are typically more costly than baseline components.
The changes in the MPCs of covered products can affect the revenues,
gross margins, and cash flow of the industry. As previously stated in
the engineering analysis in section IV.C.3 of this document, DOE
estimated an incremental MPC of $0 at all efficiency levels, compared
to the baseline MPC. DOE did not make any changes to the MPCs from the
August 2022 SNOPR.
b. Shipments Projections
The GRIM estimates manufacturer revenues based on total unit
shipment projections and the distribution of those shipments by
efficiency level. Changes in sales volumes and efficiency mix over time
can significantly affect manufacturer finances. For this analysis, the
GRIM uses the NIA's annual shipment projections derived from the
shipments analysis from 2023 (the base year) to 2055 (the end year of
the analysis period). See chapter 9 of the final rule TSD for
additional details. DOE slightly updated the shipments analysis from
the August 2022 SNOPR.
c. Product and Capital Conversion Costs
Amended energy conservation standards could cause manufacturers to
incur conversion costs to bring their production facilities and product
designs into compliance. DOE evaluated the level of conversion-related
expenditures that would be needed to comply with each considered
efficiency level in each product class. For the MIA, DOE classified
these conversion costs into two major groups: (1) product
[[Page 39935]]
conversion costs and (2) capital conversion costs. Product conversion
costs are investments in research, development, testing, marketing, and
other non-capitalized costs necessary to make product designs comply
with amended energy conservation standards. Capital conversion costs
are investments in property, plant, and equipment necessary to adapt or
change existing production facilities such that new compliant product
designs can be fabricated and assembled.
DOE used a bottom-up cost estimate to arrive at a total industry
conversion cost at each efficiency level for both product classes.
First, DOE estimated the investments manufacturers are likely to incur
in redesigning a single microwave oven control board to be able to meet
the analyzed energy conservation standards. These per-board conversion
costs were based on manufacturer interviews and include both per-board
capital conversion costs (e.g., investments in machinery and tooling)
as well as product conversion costs (e.g., investments in R&D and
testing). Based on manufacturer feedback, DOE assigned a smaller level
of investment necessary to achieve lower efficiency levels and a larger
level of investment to achieve higher efficiency levels.
Next, based on engineering teardowns and market research, DOE
estimated the total number of unique control boards used across all
covered microwave ovens. DOE used the percentage of unique microwave
oven models for each product class that were certified in DOE's
publicly available CCD to estimate the number of unique control boards
for each product class. Then DOE used the efficiency distribution from
the shipments analysis to estimate the number, for each product class,
of unique control boards specific to each efficiency level. Once DOE
estimated the number of unique control boards, DOE used the per-board
redesign costs specific to achieve each analyzed efficiency level in
order to arrive at the total industry conversion costs.
DOE did not make any changes to the capital and product conversion
costs estimates used in the August 2022 SNOPR. In general, DOE assumes
all conversion-related investments occur between the year of
publication of the final rule and the year by which manufacturers must
comply with the amended standards. The conversion cost figures used in
the GRIM can be found in section V.B.2 of this document. See chapter 12
of the final rule TSD for additional information on the estimated
capital and product conversion costs.
d. Markup Scenarios
MSPs include direct manufacturing production costs (i.e., labor,
materials, and overhead estimated in DOE's MPCs) and all non-production
costs (i.e., SG&A, R&D, and interest), along with profit. To calculate
the MSPs in the GRIM, DOE applied non-production cost markups to the
MPCs estimated in the engineering analysis for each product class and
efficiency level. Modifying these markups in the standards case yields
different sets of impacts on manufacturers. As in the August 2022
SNOPR, DOE used a manufacturer markup of 1.298 for both product classes
in the no-new-standards case. (87 FR 52282, 52296)
For the MIA, DOE modeled two standards-case markup scenarios to
represent uncertainty regarding the potential impacts on prices and
profitability for manufacturers following the implementation of amended
energy conservation standards: (1) a conversion cost recovery scenario;
and (2) a constant price scenario. These scenarios lead to different
manufacturer markup values at each TSL that, when applied to the MPCs,
result in varying revenue and cash flow impacts.
Under the conversion cost recovery scenario, DOE modeled a scenario
in which manufacturers increase their manufacturer markups in response
to amended energy conservation standards. Because DOE's engineering
analysis assumed there were no increases in the MPCs at higher
efficiency levels compared to the baseline MPCs, and that microwave
oven manufacturers would incur conversion costs to redesign non-
compliant models, DOE modeled a manufacturer markup scenario in which
microwave oven manufacturers attempt to recover these investments
through an increase in their manufacturer markup. Therefore, in the
standards cases, the manufacturer markup of models that would need to
be re-designed is a value larger than the 1.298 manufacturer markup
used in the no-new-standards case. DOE calibrated these manufacturer
markups for each product class at each efficiency level to cause
manufacturer INPV in the standards cases to be equal to the INPV in the
no-new-standards case. Because manufacturer markups used in this
scenario are calculated using the shipments analysis as inputs and the
shipments analysis was updated from the August 2022 SNOPR to this final
rule analysis, the calibrated manufacturer markups used in the
conversion cost recovery scenario for this final rule analysis are
slightly different than those values that were calculated in the August
2022 SNOPR. However, the methodology used to calculate these
manufacturer markup values are the same as those used in the August
2022 SNOPR.
The conversion cost recovery scenario represents the upper-bound of
manufacturer profitability, as microwave oven manufacturers are no
worse off, as measured by INPV, with energy conservation standards than
in the no-new-standards case (i.e., if DOE did not amend energy
conservation standards).
Under the constant price scenario, DOE applied the same
manufacturer markup, 1.298, for all efficiency levels in the no-new-
standards case and the standards cases. Because DOE's engineering
analysis assumed there were no increases in the MPCs at higher
efficiency levels and that microwave oven manufacturers would incur
conversion costs to redesign non-compliant models, microwave oven
manufacturers do not earn any additional revenue in the standards cases
than in the no-new-standards case, despite incurring conversion costs
to redesign non-compliant microwave oven models. The constant price
scenario represents the lower-bound of manufacturer profitability, as
microwave oven manufacturers incur conversion costs but do not receive
any additional revenue from these redesign efforts. The manufacturer
markups in the constant price scenario are the same as those used in
the August 2022 SNOPR.
A comparison of industry financial impacts under the two markup
scenarios is presented in section V.B.2.a of this document.
3. Discussion of MIA Comments
AHAM commented on the August 2022 SNOPR that DOE correctly decided
to incorporate conversion costs into the LCC analysis as part of the
August 2022 SNOPR. However, AHAM stated that DOE should amortize these
conversion costs over a 6-year period instead of amortizing these
conversion costs over a 30-year period, which is what was done in the
August 2022 SNOPR. (AHAM, No. 28 at p. 11)
In the SNOPR analysis, DOE used the GRIM to calculate a higher
manufacturer markup in the standards cases that results in an
equivalent manufacturer INPV in the standards cases compared to the no-
new-standards case. The conversion cost recovery scenario is the
manufacturer markup scenario incorporated into all downstream analyses,
including the LCC analysis, in the standards cases. In this scenario,
manufacturers make investments, both
[[Page 39936]]
in machinery and tooling (capital conversion costs) and in redesign and
testing (product conversion costs), prior to the compliance date of
energy conservation standards. After compliance with energy
conservation standards manufacturers increase their manufacturer
markup, thereby increasing revenue and free cash flow for the remainder
of the 30-year analysis period. Amortizing these conversion costs over
a 6-year period would create a scenario where manufacturer INPV
increases in all analyzed TSLs in the standards cases compared to the
no-new-standards case. DOE maintains that amortizing these conversion
costs over the 30-year analysis period reflects an accurate upper-bound
to industry profitability in the standards cases as manufacturers do
not lose INPV in the conversion cost recovery scenario in the standards
cases compared to the no-new-standards case.
K. Emissions Analysis
The emissions analysis consists of two components. The first
component estimates the effect of potential energy conservation
standards on power sector and site (where applicable) combustion
emissions of CO2, NOX, SO2, and Hg.
The second component estimates the impacts of potential standards on
emissions of two additional greenhouse gases, CH4 and
N2O, as well as the reductions in emissions of other gases
due to ``upstream'' activities in the fuel production chain. These
upstream activities comprise extraction, processing, and transporting
fuels to the site of combustion.
The analysis of electric power sector emissions of CO2,
NOX, SO2, and Hg uses emissions intended to
represent the marginal impacts of the change in electricity consumption
associated with amended or new standards. The methodology is based on
results published for the AEO, including a set of side cases that
implement a variety of efficiency-related policies. The methodology is
described in appendix 13A in the final rule TSD. The analysis presented
in this final rule uses projections from AEO2022. Power sector
emissions of CH4 and N2O from fuel combustion are
estimated using Emission Factors for Greenhouse Gas Inventories
published by the Environmental Protection Agency (EPA).\41\
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\41\ Available at www.epa.gov/sites/production/files/2021-04/documents/emission-factors_apr2021.pdf (last accessed December 13,
2022).
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FFC upstream emissions, which include emissions from fuel
combustion during extraction, processing, and transportation of fuels,
and ``fugitive'' emissions (direct leakage to the atmosphere) of
CH4 and CO2, are estimated based on the
methodology described in chapter 15 of the final rule TSD.
The emissions intensity factors are expressed in terms of physical
units per MWh or MMBtu of site energy savings. For power sector
emissions, specific emissions intensity factors are calculated by
sector and end use. Total emissions reductions are estimated using the
energy savings calculated in the national impact analysis.
1. Air Quality Regulations Incorporated in DOE's Analysis
DOE's no-new-standards case for the electric power sector reflects
the AEO, which incorporates the projected impacts of existing air
quality regulations on emissions. AEO2022 generally represents current
legislation and environmental regulations, including recent government
actions, that were in place at the time of preparation of AEO2022,
including the emissions control programs discussed in the following
paragraphs.\42\
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\42\ For further information, see the Assumptions to AEO2022
report that sets forth the major assumptions used to generate the
projections in the Annual Energy Outlook. Available at www.eia.gov/outlooks/aeo/assumptions/ (last accessed December 13, 2022).
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SO2 emissions from affected electric generating units
(``EGUs'') are subject to nationwide and regional emissions cap-and-
trade programs. Title IV of the Clean Air Act sets an annual emissions
cap on SO2 for affected EGUs in the 48 contiguous States and
the District of Columbia (``DC''). (42 U.S.C. 7651 et seq.)
SO2 emissions from numerous States in the eastern half of
the United States are also limited under the Cross-State Air Pollution
Rule (``CSAPR''). 76 FR 48208 (Aug. 8, 2011). CSAPR requires these
States to reduce certain emissions, including annual SO2
emissions, and went into effect as of January 1, 2015 and has been
subsequently updated.\43\ AEO2022 incorporates implementation of CSAPR,
including the Revised CSAPR Update issued in April 2021. 86 FR 23054.
Compliance with CSAPR is flexible among EGUs and is enforced through
the use of tradable emissions allowances. Under existing EPA
regulations, for States subject to SO2 emissions limits
under CSAPR, any excess SO2 emissions allowances resulting
from the lower electricity demand caused by the adoption of an
efficiency standard could be used to permit offsetting increases in
SO2 emissions by another regulated EGU.
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\43\ CSAPR requires States to address annual emissions of
SO2 and NOX, precursors to the formation of
fine particulate matter (``PM2.5'') pollution, in order
to address the interstate transport of pollution with respect to the
1997 and 2006 PM2.5 National Ambient Air Quality
Standards (``NAAQS''). CSAPR also requires certain States to address
the ozone season (May-September) emissions of NOX, a
precursor to the formation of ozone pollution, in order to address
the interstate transport of ozone pollution with respect to the 1997
ozone NAAQS. 76 FR 48208 (Aug. 8, 2011). EPA subsequently issued a
supplemental rule that included an additional five States in the
CSAPR ozone season program; 76 FR 80760 (Dec. 27, 2011)
(Supplemental Rule). In 2021, EPA issued the Revised CSAPR Update
for the 2008 Ozone NAAQs (Revised CSAPR Update) promulgating EGU
NOX ozone season emission budgets for 12 states. 86 FR
23054, 23059 (Apr. 30, 2021).
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Beginning in 2016, SO2 emissions began to fall as a
result of the Mercury and Air Toxics Standards (``MATS'') for power
plants. 77 FR 9304 (Feb. 16, 2012). In the MATS final rule, EPA
established a standard for hydrogen chloride as a surrogate for acid
gas hazardous air pollutants (``HAP''), and also established a standard
for SO2 (a non-HAP acid gas) as an alternative equivalent
surrogate standard for acid gas HAP. The same controls are used to
reduce HAP and non-HAP acid gas; thus, SO2 emissions are
being reduced as a result of the control technologies installed on
coal-fired power plants to comply with the MATS requirements for acid
gas. Because of the emissions reductions under the MATS, it is unlikely
that excess SO2 emissions allowances resulting from the
lower electricity demand would be needed or used to permit offsetting
increases in SO2 emissions by another regulated EGU.
Therefore, energy conservation standards that decrease electricity
generation will generally reduce SO2 emissions. DOE
estimated SO2 emissions reduction using emissions factors
based on AEO2022.
CSAPR also established limits on NOX emissions for
numerous States in the eastern half of the United States. Energy
conservation standards would have little effect on NOX
emissions in those States covered by CSAPR emissions limits if excess
NOX emissions allowances resulting from the lower
electricity demand could be used to permit offsetting increases in
NOX emissions from other EGUs. In such cases, NOX
emissions would remain near the limit even if electricity generation
goes down. A different case could possibly result, depending on the
configuration of the power sector in the different regions and the need
for allowances, such that NOX emissions might not remain at
the limit in the case of lower electricity demand. In this case, energy
conservation standards might
[[Page 39937]]
reduce NOX emissions in covered States. Despite this
possibility, DOE has chosen to be conservative in its analysis and has
maintained the assumption that standards will not reduce NOX
emissions in States covered by CSAPR. Standards would be expected to
reduce NOX emissions in the States not covered by CSAPR. DOE
used AEO2022 data to derive NOX emissions factors for the
group of States not covered by CSAPR.
The MATS limit mercury emissions from power plants, but they do not
include emissions caps and, as such, DOE's energy conservation
standards would be expected to slightly reduce Hg emissions. DOE
estimated mercury emissions reduction using emissions factors based on
AEO2022, which incorporates the MATS.
L. Monetizing Emissions Impacts
As part of the development of this final rule, for the purpose of
complying with the requirements of Executive Order 12866, DOE
considered the estimated monetary benefits from the reduced emissions
of CO2, CH4, N2O, NOX, and
SO2 that are expected to result from each of the TSLs
considered. In order to make this calculation analogous to the
calculation of the NPV of consumer benefit, DOE considered the reduced
emissions expected to result over the lifetime of products shipped in
the projection period for each TSL. This section summarizes the basis
for the values used for monetizing the emissions benefits and presents
the values considered in this final rule.
On March 16, 2022, the Fifth Circuit Court of Appeals (No. 22-
30087) granted the Federal government's emergency motion for stay
pending appeal of the February 11, 2022, preliminary injunction issued
in Louisiana v. Biden, No. 21-cv-1074-JDC-KK (W.D. La.). As a result of
the Fifth Circuit's order, the preliminary injunction is no longer in
effect, pending resolution of the Federal government's appeal of that
injunction or a further court order. Among other things, the
preliminary injunction enjoined the defendants in that case from
``adopting, employing, treating as binding, or relying upon'' the
interim estimates of the social cost of greenhouse gases--which were
issued by the Interagency Working Group on the Social Cost of
Greenhouse Gases on February 26, 2021--to monetize the benefits of
reducing greenhouse gas emissions. As reflected in this rule, DOE has
reverted to its approach prior to the injunction and presents monetized
benefits where appropriate and permissible under law. DOE requests
comment on how to address the climate benefits and other non-monetized
effects of the proposal.
AHAM commented that DOE should not use the social cost of carbon
and other monetization of emissions reductions benefits in its analysis
of the factors EPCA requires DOE to balance to determine the
appropriate standard. AHAM commented that while it may be acceptable
for DOE to continue its current practice of examining the social cost
of carbon and monetization of other emissions reductions benefits as
informational so long as the underlying interagency analysis is
transparent and vigorous, the monetization analysis should not impact
the TSLs DOE selects as a new or amended standard. (AHAM, No. 28 at p.
13)
As stated in section III.F.1.f of this document, DOE maintains that
environmental and public health benefits associated with the more
efficient use of energy, including those connected to global climate
change, are important to take into account when considering the need
for national energy conservation, which is one of the factors that EPCA
requires DOE to evaluate in determining whether a potential energy
conservation standard is economically justified. See 42 U.S.C.
6295(o)(2)(B)(i)(VI). In addition, Executive Order 13563, which was re-
affirmed on January 21, 2021, stated that each agency must, among other
things: ``select, in choosing among alternative regulatory approaches,
those approaches that maximize net benefits (including potential
economic, environmental, public health and safety, and other
advantages; distributive impacts; and equity).'' For these reasons, DOE
includes monetized emissions reductions in its evaluation of potential
standard levels. As previously stated, however, DOE would reach the
same conclusion presented in this final rulemaking in the absence of
the social cost of greenhouse gases.
1. Monetization of Greenhouse Gas Emissions
DOE estimates the monetized benefits of the reductions in emissions
of CO2, CH4, and N2O by using a
measure of the social cost of each pollutant (e.g., SC-CO2).
These estimates represent the monetary value of the net harm to society
associated with a marginal increase in emissions of these pollutants in
a given year, or the benefit of avoiding that increase. These estimates
are intended to include (but are not limited to) climate-change-related
changes in net agricultural productivity, human health, property
damages from increased flood risk, disruption of energy systems, risk
of conflict, environmental migration, and the value of ecosystem
services.
DOE exercises its own judgment in presenting monetized climate
benefits as recommended by applicable Executive orders, and DOE would
reach the same conclusion presented in this final rulemaking in the
absence of the social cost of greenhouse gases. That is, the social
costs of greenhouse gases, whether measured using the February 2021
interim estimates presented by the Interagency Working Group on the
Social Cost of Greenhouse Gases (IWG) or by another means, did not
affect the rule ultimately proposed by DOE.
DOE estimated the global social benefits of CO2,
CH4, and N2O reductions (i.e., SC-GHGs) using the
estimates presented in the Technical Support Document: Social Cost of
Carbon, Methane, and Nitrous Oxide Interim Estimates under Executive
Order 13990, published in February 2021 by the IWG. The SC-GHGs is the
monetary value of the net harm to society associated with a marginal
increase in emissions in a given year, or the benefit of avoiding that
increase. In principle, SC-GHGs includes the value of all climate
change impacts, including (but not limited to) changes in net
agricultural productivity, human health effects, property damage from
increased flood risk and natural disasters, disruption of energy
systems, risk of conflict, environmental migration, and the value of
ecosystem services. The SC-GHGs therefore reflects the societal value
of reducing emissions of the gas in question by one metric ton. The SC-
GHGs is the theoretically appropriate value to use in conducting
benefit-cost analyses of policies that affect CO2,
N2O, and CH4 emissions. As a member of the IWG
involved in the development of the February 2021 SC-GHG TSD, DOE agrees
that the interim SC-GHG estimates represent the most appropriate
estimate of the SC-GHG until revised estimates have been developed
reflecting the latest, peer-reviewed science.
The SC-GHGs estimates presented here were developed over many years
using a transparent process, peer-reviewed methodologies, the best
science available at the time of that process, and with input from the
public. Specifically, in 2009, the IWG, which included DOE and other
executive branch agencies and offices, was established to ensure that
agencies were using the best available science and to promote
consistency in the social cost of carbon (SC-CO2) values
used across agencies. The IWG published SC-CO2 estimates in
2010 that were developed from an ensemble of three widely cited
[[Page 39938]]
integrated assessment models (IAMs) that estimate global climate
damages using highly aggregated representations of climate processes
and the global economy combined into a single modeling framework. The
three IAMs were run using a common set of input assumptions in each
model for future population, economic, and CO2 emissions
growth, as well as equilibrium climate sensitivity--a measure of the
globally averaged temperature response to increased atmospheric
CO2 concentrations. These estimates were updated in 2013
based on new versions of each IAM. In August 2016, the IWG published
estimates of the social cost of methane (SC-CH4) and nitrous
oxide (SC-N2O) using methodologies that are consistent with
the methodology underlying the SC-CO2 estimates. The
modeling approach that extends the IWG SC-CO2 methodology to
non-CO2 GHGs has undergone multiple stages of peer review.
The SC-CH4 and SC-N2O estimates were developed by
Marten et al.\44\ and underwent a standard double-blind peer review
process prior to journal publication. In 2015, as part of the response
to public comments received to a 2013 solicitation for comments on the
SC-CO2 estimates, the IWG announced a National Academies of
Sciences, Engineering, and Medicine review of the SC-CO2
estimates to offer advice on how to approach future updates to ensure
that the estimates continue to reflect the best available science and
methodologies. In January 2017, the National Academies released their
final report, Valuing Climate Damages: Updating Estimation of the
Social Cost of Carbon Dioxide, and recommended specific criteria for
future updates to the SC-CO2 estimates, a modeling framework
to satisfy the specified criteria, and both near-term updates and
longer-term research needs pertaining to various components of the
estimation process.\45\ Shortly thereafter, in March 2017, President
Trump issued Executive Order 13783, which disbanded the IWG, withdrew
the previous TSDs, and directed agencies to ensure SC-CO2
estimates used in regulatory analyses are consistent with the guidance
contained in OMB's Circular A-4, ``including with respect to the
consideration of domestic versus international impacts and the
consideration of appropriate discount rates'' (E.O. 13783, Section
5(c)). Benefit-cost analyses following E.O. 13783 used SC-GHG estimates
that attempted to focus on the U.S.-specific share of climate change
damages as estimated by the models and were calculated using two
discount rates recommended by Circular A-4, 3 percent and 7 percent.
All other methodological decisions and model versions used in SC-GHG
calculations remained the same as those used by the IWG in 2010 and
2013, respectively.
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\44\ Marten, A. L., E. A. Kopits, C. W. Griffiths, S. C.
Newbold, and A. Wolverton. Incremental CH4 and
N2O mitigation benefits consistent with the US
Government's SC-CO2 estimates. Climate Policy. 2015.
15(2): pp. 272-298.
\45\ National Academies of Sciences, Engineering, and Medicine.
Valuing Climate Damages: Updating Estimation of the Social Cost of
Carbon Dioxide. 2017. The National Academies Press: Washington, DC.
---------------------------------------------------------------------------
On January 20, 2021, President Biden issued Executive Order 13990,
which re-established the IWG and directed it to ensure that the U.S.
Government's estimates of the social cost of carbon and other
greenhouse gases reflect the best available science and the
recommendations of the National Academies (2017). The IWG was tasked
with first reviewing the SC-GHG estimates currently used in Federal
analyses and publishing interim estimates within 30 days of the E.O.
that reflect the full impact of GHG emissions, including by taking
global damages into account. The interim SC-GHG estimates published in
February 2021 are used here to estimate the climate benefits for this
proposed rulemaking. The E.O. instructs the IWG to undertake a fuller
update of the SC-GHG estimates by January 2022 that takes into
consideration the advice of the National Academies (2017) and other
recent scientific literature. The February 2021 SC-GHG TSD provides a
complete discussion of the IWG's initial review conducted under
E.O.13990. In particular, the IWG found that the SC-GHG estimates used
under E.O. 13783 fail to reflect the full impact of GHG emissions in
multiple ways.
First, the IWG found that the SC-GHG estimates used under E.O.
13783 fail to fully capture many climate impacts that affect the
welfare of U.S. citizens and residents, and those impacts are better
reflected by global measures of the SC-GHG. Examples of omitted effects
from the E.O. 13783 estimates include: (1) direct effects on U.S.
citizens, assets, and investments located abroad; (2) supply chains;(3)
U.S. military assets and interests abroad; (4) tourism; and (5)
spillover pathways, such as economic and political destabilization and
global migration, that can lead to adverse impacts on U.S. national
security, public health, and humanitarian concerns. In addition,
assessing the benefits of U.S. GHG mitigation activities requires
consideration of how those actions may affect mitigation activities by
other countries, as those international mitigation actions will provide
a benefit to U.S. citizens and residents by mitigating climate impacts
that affect U.S. citizens and residents. A wide range of scientific and
economic experts have emphasized the issue of reciprocity as support
for considering global damages of GHG emissions. If the United States
does not consider impacts on other countries, it is difficult to
convince other countries to consider the impacts of their emissions on
the United States The only way to achieve an efficient allocation of
resources for emissions reduction on a global basis--and so benefit the
U.S. and its citizens--is for all countries to base their policies on
global estimates of damages. As a member of the IWG involved in the
development of the February 2021 SC-GHG TSD, DOE agrees with this
assessment and, therefore, in this proposed rule, DOE centers attention
on a global measure of SC-GHG. This approach is the same as that taken
in DOE regulatory analyses from 2012 through 2016. A robust estimate of
climate damages that accrue only to U.S. citizens and residents does
not currently exist in the literature. As explained in the February
2021 SC-GHG TSD, existing estimates are both incomplete and
underestimate total damages that accrue to the citizens and residents
of the U.S. because they do not fully capture the regional interactions
and spillovers discussed above, nor do they include all of the
important physical, ecological, and economic impacts of climate change
recognized in the literature. As noted in the February 2021 SC-GHG TSD,
the IWG will continue to review developments in the literature,
including more robust methodologies for estimating a U.S.-specific SC-
GHG value and exploring ways to better inform the public of the full
range of carbon impacts. As a member of the IWG, DOE will continue to
follow developments in the literature pertaining to this issue.
Second, the IWG found that the use of the social rate of return on
capital (7 percent under current OMB Circular A-4 guidance) to discount
the future benefits of reducing GHG emissions inappropriately
underestimates the impacts of climate change for the purposes of
estimating the SC-GHG. Consistent with the findings of the National
Academies (2017) and the economic literature, the IWG continued to
conclude that the consumption rate of interest is the theoretically
appropriate discount rate in an intergenerational
[[Page 39939]]
context \46\ and recommended that discount rate uncertainty and
relevant aspects of intergenerational ethical considerations be
accounted for in selecting future discount rates.
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\46\ Interagency Working Group on Social Cost of Carbon. Social
Cost of Carbon for Regulatory Impact Analysis under Executive Order
12866. 2010. United States Government. Available at www.epa.gov/sites/default/files/2016-12/documents/scc_tsd_2010.pdf (last
accessed April 15, 2022). Interagency Working Group on Social Cost
of Carbon. Technical Update of the Social Cost of Carbon for
Regulatory Impact Analysis Under Executive Order 12866. 2013
Available at www.federalregister.gov/documents/2013/11/26/2013-28242/technical-support-document-technical-update-of-the-social-cost-of-carbon-for-regulatory-impact (last accessed April 15, 2022).
Interagency Working Group on Social Cost of Greenhouse Gases, United
States Government. Technical Support Document: Technical Update on
the Social Cost of Carbon for Regulatory Impact Analysis-Under
Executive Order 12866. August 2016. Available at www.epa.gov/sites/default/files/2016-12/documents/sc_co2_tsd_august_2016.pdf (last
accessed January 18, 2022). Interagency Working Group on Social Cost
of Greenhouse Gases, United States Government. Addendum to Technical
Support Document on Social Cost of Carbon for Regulatory Impact
Analysis under Executive Order 12866: Application of the Methodology
to Estimate the Social Cost of Methane and the Social Cost of
Nitrous Oxide. August 2016. Available at www.epa.gov/sites/default/files/2016-12/documents/addendum_to_sc-ghg_tsd_august_2016.pdf (last
accessed January 18, 2022).
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Furthermore, the damage estimates developed for use in the SC-GHG
are estimated in consumption-equivalent terms, and so an application of
OMB Circular A-4's guidance for regulatory analysis would then use the
consumption discount rate to calculate the SC-GHG. DOE agrees with this
assessment and will continue to follow developments in the literature
pertaining to this issue. DOE also notes that while OMB Circular A-4,
as published in 2003, recommends using 3 percent and 7 percent discount
rates as ``default'' values, Circular A-4 also reminds agencies that
``different regulations may call for different emphases in the
analysis, depending on the nature and complexity of the regulatory
issues and the sensitivity of the benefit and cost estimates to the key
assumptions.'' On discounting, Circular A-4 recognizes that ``special
ethical considerations arise when comparing benefits and costs across
generations,'' and Circular A-4 acknowledges that analyses may
appropriately ``discount future costs and consumption benefits. . .at a
lower rate than for intragenerational analysis.'' In the 2015 Response
to Comments on the Social Cost of Carbon for Regulatory Impact
Analysis, OMB, DOE, and the other IWG members recognized that
``Circular A-4 is a living document'' and ``the use of 7 percent is not
considered appropriate for intergenerational discounting. There is wide
support for this view in the academic literature, and it is recognized
in Circular A-4 itself.'' Thus, DOE concludes that a 7-percent discount
rate is not appropriate to apply to value the social cost of greenhouse
gases presented in this analysis.
To calculate the present and annualized values of climate benefits,
DOE uses the same discount rate as the rate used to discount the value
of damages from future GHG emissions, for internal consistency. That
approach to discounting follows the same approach that the February
2021 SC-GHG TSD recommends ``to ensure internal consistency--i.e.,
future damages from climate change using the SC-GHG at 2.5 percent
should be discounted to the base year of the analysis using the same
2.5 percent rate.'' DOE has also consulted the National Academies' 2017
recommendations on how SC-GHG estimates can ``be combined in RIAs with
other cost and benefits estimates that may use different discount
rates.'' The National Academies reviewed several options, including
``presenting all discount rate combinations of other costs and benefits
with [SC-GHG] estimates.''
As a member of the IWG involved in the development of the February
2021 SC-GHG TSD, DOE agrees with the above assessment and will continue
to follow developments in the literature pertaining to this issue.
While the IWG is working to assess how best to incorporate the latest
peer-reviewed science to develop an updated set of SC-GHG estimates, it
set the interim estimates to be the most recent estimates developed by
the IWG prior to the group being disbanded in 2017. The estimates rely
on the same models and harmonized inputs and are calculated using a
range of discount rates. As explained in the February 2021 SC-GHG TSD,
the IWG has recommended that agencies revert to the same set of four
values drawn from the SC-GHG distributions based on three discount
rates as were used in regulatory analyses between 2010 and 2016 and
were subject to public comment. For each discount rate, the IWG
combined the distributions across models and socioeconomic emissions
scenarios (applying equal weight to each) and then selected a set of
four values recommended for use in benefit-cost analyses: an average
value resulting from the model runs for each of three discount rates
(2.5 percent, 3 percent, and 5 percent), plus a fourth value, selected
as the 95th percentile of estimates based on a 3-percent discount rate.
The fourth value was included to provide information on potentially
higher-than-expected economic impacts from climate change. DOE agrees
with the update explained in the February 2021 SC-GHG TSD, which
reflects the immediate need to have an operational SC-GHG--for use in
regulatory benefit-cost analyses and other applications--that was
developed using a transparent process, peer-reviewed methodologies, and
the science available at the time of that process. Those estimates were
subject to public comment in the context of dozens of proposed
rulemakings as well as in a dedicated public comment period in 2013.
A number of limitations and uncertainties are associated with the
SC-GHG estimates. First, the current scientific and economic
understanding of discounting approaches suggests discount rates
appropriate for intergenerational analysis in the context of climate
change are likely to be less than 3 percent, near 2 percent or
lower.\47\ Second, the IAMs used to produce these interim estimates do
not include all of the important physical, ecological, and economic
impacts of climate change recognized in the climate change literature;
furthermore, the science underlying their ``damage functions''--i.e.,
the core parts of the IAMs that map global mean temperature changes and
other physical impacts of climate change into economic (both market and
nonmarket) damages--lags behind the most recent research. For example,
limitations include the incomplete treatment of catastrophic and non-
catastrophic impacts in the integrated assessment models, their
incomplete treatment of adaptation and technological change, the
incomplete way in which inter-regional and intersectoral linkages are
modeled, uncertainty in the extrapolation of damages due to high
temperatures, and the inadequate representation of the relationship
between the discount rate and uncertainty in economic growth over long
time horizons. Likewise, the socioeconomic and emissions scenarios used
as inputs to the models do not reflect new information from the last
decade of scenario generation or the full range of projections. The
modeling limitations do not all work in the same direction in terms of
their influence on the SC-CO2 estimates. However, as
discussed in the February 2021 SC-GHG
[[Page 39940]]
TSD, the IWG has recommended that, taken together, the limitations
suggest that the interim SC-GHG estimates used in this final rule
likely underestimate the damages from GHG emissions. DOE concurs with
this assessment.
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\47\ Interagency Working Group on Social Cost of Greenhouse
Gases (IWG). 2021. Technical Support Document: Social Cost of
Carbon, Methane, and Nitrous Oxide Interim Estimates under Executive
Order 13990. February. United States Government. Available at
www.whitehouse.gov/briefing-room/blog/2021/02/26/a-return-to-science-evidence-based-estimates-of-the-benefits-of-reducing-climate-pollution/.
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DOE's derivations of the SC-CO2, SC-N2O, and
SC-CH4 values used for this rule are discussed in the
following sections, and the results of DOE's analyses estimating the
benefits of the reductions in emissions of these GHGs are presented in
section V.B.6 of this document.
The C2ES commented that DOE appropriately applies the social cost
estimates developed by the IWG to its analysis of emissions reduction
benefits generated by the proposed rule. The C2ES commented that DOE
should expand upon its rationale for adopting a global damages
valuation and for the range of discount rates it applies to climate
effects, as there are additional legal, economic, and policy reasons
for such methodological decisions that can further bolster DOE's
support for these choices. C2ES added that DOE should consider
conducting a sensitivity analysis using a sound domestic-only social
cost estimate as a backstop, and should explicitly conclude that the
rule is cost-benefit justified even using a domestic-only valuation
that may still undercount climate benefits. The C2ES urged DOE to
consider providing an additional sensitivity analysis using discount
rates lower than 2.5 percent for climate impacts. (C2ES, No. 29 at p.
2)
DOE maintains that the reasons for using global measures of the SC-
GHG previously discussed are sufficient for the purposes of this
rulemaking. DOE notes that further discussion of this topic is
contained in the February 2021 SC-GHG TSD, and DOE agrees with the
assessment therein. Regarding conducting sensitivity analysis using a
domestic-only social cost estimate, DOE agrees with the assessment in
the February 2021 SC-GHG TSD that the only currently available
quantitative characterization of domestic damages from GHG emissions is
both incomplete and an underestimate of the share of total damages that
accrue to the citizens and residents of the United States. Therefore,
it would be of questionable value to conduct the suggested sensitivity
analysis at this time. DOE considered performing sensitivity analysis
using discount rates lower than 2.5 percent for climate impacts, as
suggested by the IWG, but it concluded that such analysis would not add
meaningful information in the context of this rulemaking.
a. Social Cost of Carbon
The SC-CO2 values used for this final rule were based on
the values developed for the IWG's February 2021 TSD. Table IV.8 shows
the updated sets of SC-CO2 estimates from the IWG's TSD in
5-year increments from 2020 to 2050. The full set of annual values that
DOE used is presented in appendix 14-A of the final rule TSD. For
purposes of capturing the uncertainties involved in regulatory impact
analysis, DOE has determined it is appropriate to include all four sets
of SC-CO2 values, as recommended by the IWG.\48\
Table IV.8.--Annual SC-CO2 Values From 2021 Interagency Update, 2020-2050
[2020$ per Metric Ton CO2]
----------------------------------------------------------------------------------------------------------------
Discount rate and statistic
---------------------------------------------------------------
Year 3% 95th
5% Average 3% Average 2.5% Average percentile
----------------------------------------------------------------------------------------------------------------
2020............................................ 14 51 76 152
2025............................................ 17 56 83 169
2030............................................ 19 62 89 187
2035............................................ 22 67 96 206
2040............................................ 25 73 103 225
2045............................................ 28 79 110 242
2050............................................ 32 85 116 260
----------------------------------------------------------------------------------------------------------------
For 2051 to 2070, DOE used SC-CO2 estimates published by
EPA, adjusted to 2020$.\49\ These estimates are based on methods,
assumptions, and parameters identical to the 2020-2050 estimates
published by the IWG (which were based on EPA modeling). DOE expects
additional climate benefits to accrue for any longer-life furnaces
after 2070, but a lack of available SC-CO2 estimates for
emissions years beyond 2070 prevents DOE from monetizing these
potential benefits in this analysis.
---------------------------------------------------------------------------
\48\ For example, the February 2021 SC-GHG TSD discusses how the
understanding of discounting approaches suggests that discount rates
appropriate for intergenerational analysis in the context of climate
change may be lower than 3 percent.
\49\ See EPA, Revised 2023 and Later Model Year Light-Duty
Vehicle GHG Emissions Standards: Regulatory Impact Analysis,
Washington, DC, December 2021. Available at nepis.epa.gov/Exe/ZyPDF.cgi?Dockey=P1013ORN.pdf (last accessed January 13, 2023).
(last accessed January 20, 2023).
---------------------------------------------------------------------------
DOE multiplied the CO2 emissions reduction estimated for
each year by the SC-CO2 value for that year in each of the
four cases. DOE adjusted the values to 2021$ using the implicit price
deflator for gross domestic product (``GDP'') from the Bureau of
Economic Analysis. To calculate a present value of the stream of
monetary values, DOE discounted the values in each of the four cases
using the specific discount rate that had been used to obtain the SC-
CO2 values in each case.
b. Social Cost of Methane and Nitrous Oxide
The SC-CH4 and SC-N2O values used for this
final rule were based on the values developed for the February 2021 SC-
GHG TSD. Table IV.9 shows the updated sets of SC-CH4 and SC-
N2O estimates from the latest interagency update in 5-year
increments from 2020 to 2050. The full set of annual values used is
presented in appendix 14A of the final rule TSD. To capture the
uncertainties involved in regulatory impact analysis, DOE has
determined it is appropriate to include all four sets of SC-
CH4 and SC- N2O values, as recommended by the
IWG. DOE derived values after 2050 using the approach described above
for the SC-CO2.
[[Page 39941]]
Table IV.9.--Annual SC-CH4 and SC-N2O Values From 2021 Interagency Update, 2020-2050
[2020$ per metric ton]
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
SC-CH4 SC-N2O
-------------------------------------------------------------------------------------------------------------------------------------------------
Discount rate and statistic Discount rate and statistic
Year -------------------------------------------------------------------------------------------------------------------------------------------------
3% 95th 3% 95th
5% Average 3% Average 2.5% Average percentile 5% Average 3% Average 2.5% Average percentile
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
2020.......................................... 670............................. 1,500 2,000 3,900 5,800 18,000 27,000 48,000
2025.......................................... 800............................. 1,700 2,200 4,500 6,800 21,000 30,000 54,000
2030.......................................... 940............................. 2,000 2,500 5,200 7,800 23,000 33,000 60,000
2035.......................................... 1,100........................... 2,200 2,800 6,000 9,000 25,000 36,000 67,000
2040.......................................... 1,300........................... 2,500 3,100 6,700 10,000 28,000 39,000 74,000
2045.......................................... 1,500........................... 2,800 3,500 7,500 12,000 30,000 42,000 81,000
2050.......................................... 1,700........................... 3,100 3,800 8,200 13,000 33,000 45,000 88,000
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
2. Monetization of Other Emissions Impacts
For the final rule, DOE estimated the monetized value of
NOX and SO2 emissions reductions from electricity
generation using benefit-per-ton estimates for that sector from the
EPA's Benefits Mapping and Analysis Program.\50\ DOE used EPA's values
for PM2.5-related benefits associated with NOX
and SO2 and for ozone-related benefits associated with
NOX for 2025 and 2030, and 2040, calculated with discount
rates of 3 percent and 7 percent. DOE used linear interpolation to
define values for the years not given in the 2025 to 2040 range; for
years beyond 2040 the values are held constant. DOE combined the EPA
benefit per ton estimates with regional information on electricity
consumption and emissions to define weighted-average national values
for NOX and SO2 as a function of sector (see.
appendix 14B of the final rule TSD).
---------------------------------------------------------------------------
\50\ Estimating the Benefit per Ton of Reducing PM2.5
Precursors from 21 Sectors. Available at www.epa.gov/benmap/estimating-benefit-ton-reducing-pm25-precursors-21-sectors.
---------------------------------------------------------------------------
DOE multiplied the site emissions reduction (in tons) in each year
by the associated $/ton values, and then discounted each series using
discount rates of 3 percent and 7 percent as appropriate.
M. Utility Impact Analysis
The utility impact analysis estimates the changes in installed
electrical capacity and generation projected to result for each
considered TSL. The analysis is based on published output from the NEMS
associated with AEO2022. NEMS produces the AEO Reference case, as well
as a number of side cases that estimate the economy-wide impacts of
changes to energy supply and demand. For the current analysis, impacts
are quantified by comparing the levels of electricity sector
generation, installed capacity, fuel consumption and emissions in the
AEO2022 Reference case and various side cases. Details of the
methodology are provided in the appendices to chapters 13 and 15 of the
final rule TSD.
The output of this analysis is a set of time-dependent coefficients
that capture the change in electricity generation, primary fuel
consumption, installed capacity, and power sector emissions due to a
unit reduction in demand for a given end use. These coefficients are
multiplied by the stream of electricity savings calculated in the NIA
to provide estimates of selected utility impacts of potential new or
amended energy conservation standards.
N. Employment Impact Analysis
DOE considers employment impacts in the domestic economy as one
factor in selecting a standard. Employment impacts from new or amended
energy conservation standards include both direct and indirect impacts.
Direct employment impacts are any changes in the number of employees of
manufacturers of the products subject to standards, their suppliers,
and related service firms. The MIA addresses those impacts. Indirect
employment impacts are changes in national employment that occur due to
the shift in expenditures and capital investment caused by the purchase
and operation of more-efficient appliances. Indirect employment impacts
from standards consist of the net jobs created or eliminated in the
national economy, other than in the manufacturing sector being
regulated, caused by (1) reduced spending by consumers on energy, (2)
reduced spending on new energy supply by the utility industry, (3)
increased consumer spending on the products to which the new standards
apply and other goods and services, and (4) the effects of those three
factors throughout the economy.
One method for assessing the possible effects on the demand for
labor of such shifts in economic activity is to compare sector
employment statistics developed by the BLS. BLS regularly publishes its
estimates of the number of jobs per million dollars of economic
activity in different sectors of the economy, as well as the jobs
created elsewhere in the economy by this same economic activity. Data
from BLS indicate that expenditures in the utility sector generally
create fewer jobs (both directly and indirectly) than expenditures in
other sectors of the economy.\51\ There are many reasons for these
differences, including wage differences and the fact that the utility
sector is more capital-intensive and less labor-intensive than other
sectors. Energy conservation standards have the effect of reducing
consumer utility bills. Because reduced consumer expenditures for
energy likely lead to increased expenditures in other sectors of the
economy, the general effect of efficiency standards is to shift
economic activity from a less labor-intensive sector (i.e., the utility
sector) to more labor-intensive sectors (e.g., the retail and service
sectors). Thus, the BLS data suggest that net national employment may
increase due to shifts in economic activity resulting from energy
conservation standards.
---------------------------------------------------------------------------
\51\ See U.S. Department of Commerce-Bureau of Economic
Analysis. Regional Multipliers: A User Handbook for the Regional
Input-Output Modeling System (``RIMS II''). 1997. U.S. Government
Printing Office: Washington, DC. Available at https://www.bea.gov/sites/default/files/methodologies/RIMSII_User_Guide.pdf (last
accessed January 20, 2023).
---------------------------------------------------------------------------
DOE estimated indirect national employment impacts for the standard
levels considered in this final rule using an input/output model of the
U.S. economy called Impact of Sector Energy
[[Page 39942]]
Technologies version 4 (``ImSET'').\52\ ImSET is a special-purpose
version of the ``U.S. Benchmark National Input-Output'' (``I-O'')
model, which was designed to estimate the national employment and
income effects of energy-saving technologies. The ImSET software
includes a computer-based I-O model having structural coefficients that
characterize economic flows among 187 sectors most relevant to
industrial, commercial, and residential building energy use.
---------------------------------------------------------------------------
\52\ Livingston, O. V., S. R. Bender, M. J. Scott, and R. W.
Schultz. ImSET 4.0: Impact of Sector Energy Technologies Model
Description and User's Guide. 2015. Pacific Northwest National
Laboratory: Richland, WA. PNNL-24563.
---------------------------------------------------------------------------
DOE notes that ImSET is not a general equilibrium forecasting
model, and that the uncertainties involved in projecting employment
impacts especially change in the later years of the analysis. Because
ImSET does not incorporate price changes, the employment effects
predicted by ImSET may over-estimate actual job impacts over the long
run for this rule. Therefore, DOE used ImSET only to generate results
for near-term timeframes, where these uncertainties are reduced. For
more details on the employment impact analysis, see chapter 16 of the
final rule TSD.
V. Analytical Results and Conclusions
The following section addresses the results from DOE's analyses
with respect to the considered energy conservation standards for
microwave ovens. It addresses the TSLs examined by DOE, the projected
impacts of each of these levels if adopted as energy conservation
standards for microwave ovens, and the standards levels that DOE is
adopting in this final rule. Additional details regarding DOE's
analyses are contained in the final rule TSD supporting this document.
A. Trial Standard Levels
In general, DOE typically evaluates potential amended standards for
products and equipment by grouping individual efficiency levels for
each class into TSLs. Use of TSLs allows DOE to identify and consider
manufacturer cost interactions between the product classes, to the
extent that there are such interactions, and market cross elasticity
from consumer purchasing decisions that may change when different
standard levels are set.
In the analysis conducted for this final rule, DOE analyzed the
benefits and burdens of three TSLs for microwave ovens. DOE developed
TSLs that combine efficiency levels for each analyzed product class.
DOE presents the results for the TSLs in this document, while the
results for all efficiency levels that DOE analyzed are in the final
rule TSD.
Table V.1 presents the TSLs and the corresponding efficiency levels
that DOE has identified for potential amended energy conservation
standards for microwave ovens. TSL 3 represents the maximum
technologically feasible (``max-tech'') energy efficiency for all
product classes. TSL 2 and TSL 1 represent interim energy efficiency
levels between the current standard level and the max-tech energy
efficiency level.
Table V.1--Trial Standard Levels for Microwave Ovens
----------------------------------------------------------------------------------------------------------------
Product class TSL 1 TSL 2 TSL 3
----------------------------------------------------------------------------------------------------------------
Maximum allowable average standby power (W)
-----------------------------------------------
PC 1: Microwave-Only and Countertop Convection.................. 0.8 0.6 0.4
PC 2: Built-In and Over-the-Range Convection.................... 1.5 1.0 0.5
----------------------------------------------------------------------------------------------------------------
DOE constructed the TSLs for this final rule to include efficiency
levels representative of efficiency levels with similar characteristics
(i.e., using similar technologies and/or efficiencies, and having
roughly comparable equipment availability). The use of representative
efficiency levels provided for greater distinction between the TSLs.
While representative efficiency levels were included in the TSLs, DOE
considered all efficiency levels as part of its analysis.\53\
---------------------------------------------------------------------------
\53\ Efficiency levels that were analyzed for this NOPR are
discussed in section IV.C.4 of this document. Results by efficiency
level are presented in final rule TSD chapters 8, 10, and 12.
---------------------------------------------------------------------------
The Joint Commenters requested DOE to consider an additional TSL
that evaluates Product Class 1 at a level more stringent than what DOE
proposed in the August 2022 SNOPR. Specifically, the Joint Commenters
requested that DOE evaluate a modified TSL with Product Class 1 at 0.4W
and Product Class 2 at 1.0W, noting that this approach would alleviate
DOE's concerns of net cost to consumers while roughly doubling the
national energy savings relative to the proposed levels. (Joint
Commenters, No. 31 at p. 2)
As discussed in section V.B.2.c of this document, DOE assumes
manufacturers will meet amended energy conservation standards for
microwave ovens by re-designing the control boards of non-compliant
models. DOE estimates that approximately 89 percent of Product Class 1
shipments will need to be redesigned to meet the efficiency levels of
the modified TSL suggested by the Joint Commenters. This represents a
need to redesign models accounting for approximately 10.5 million units
with manufacturers expressing concern that a redesign effort of this
extent may not be possible in a three-year time period. Manufacturers
would most likely stop offering lower-volume non-compliant models to
consumers, choosing instead to focus their resources on remodeling the
highest-volume selling models first. Due to the potential impact on
consumer choice, DOE did not evaluate the additional TSL suggested by
the Joint Commenters in this rulemaking.
B. Economic Justification and Energy Savings
1. Economic Impacts on Individual Consumers
DOE analyzed the economic impacts on microwave oven consumers by
looking at the effects that potential amended standards at each TSL
would have on the LCC and PBP. DOE also examined the impacts of
potential standards on selected consumer subgroups. These analyses are
discussed in the following sections.
a. Life-Cycle Cost and Payback Period
In general, higher-efficiency products affect consumers in two
ways: (1) purchase price increases and (2) annual operating costs
decrease. Inputs used for calculating the LCC and PBP include total
installed costs (i.e., product price plus installation costs) and
operating costs (i.e., annual energy use, energy prices, energy price
trends, repair costs, and maintenance costs). The LCC calculation also
uses product lifetime
[[Page 39943]]
and a discount rate. Chapter 8 of the final rule TSD provides detailed
information on the LCC and PBP analyses.
Table V.2 through Table V.5 show the LCC and PBP results for the
TSLs considered for each product class. In the first of each pair of
tables, the simple payback is measured relative to the baseline
product. In the second table, the impacts are measured relative to the
efficiency distribution in the in the no-new-standards case in the
compliance year (see section IV.F.8 of this document). Because some
consumers purchase products with higher efficiency in the no-new-
standards case, the average savings are less than the difference
between the average LCC of the baseline product and the average LCC at
each TSL. The savings refer only to consumers who are affected by a
standard at a given TSL. Those who already purchase a product with
efficiency at or above a given TSL are not affected. Consumers for whom
the LCC increases at a given TSL experience a net cost.
Table V.2--Average LCC and PBP Results for PC 1: Microwave-Only Ovens and Countertop Convection Microwave Ovens
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
Average costs (2021$)
Standby power ---------------------------------------------------------------- Simple payback Average
TSL EL (W) First year's Lifetime (years) lifetime
Installed cost operating cost operating cost LCC (years)
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
0 .............. $254.16 $1.26 $11.38 $265.54 .............. 10.78
1............................................................... 1 0.8 254.24 1.02 9.20 263.44 0.3 10.78
2............................................................... 2 0.6 254.80 0.78 7.02 261.81 1.3 10.78
3............................................................... 3 0.4 255.57 0.54 4.83 260.40 2.0 10.78
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
Note: The results for each TSL are calculated assuming that all consumers use products at that efficiency level. The PBP is measured relative to the baseline product.
Table V.3--Average LCC Savings Relative to the No-New-Standards Case for PC 1: Microwave-Only Ovens and
Countertop Convection Microwave Ovens
----------------------------------------------------------------------------------------------------------------
Life-cycle cost savings
----------------------------------
Efficiency Percent of
TSL level Average LCC consumers that
savings * experience net
(2021$) cost
----------------------------------------------------------------------------------------------------------------
1............................................................ 1 $0.25 0
2............................................................ 2 0.99 5
3............................................................ 3 2.16 12
----------------------------------------------------------------------------------------------------------------
* The savings represent the average LCC for affected consumers.
Table V.4--Average LCC and PBP Results for PC 2: Built-In and Over-the-Range Convection Microwave Ovens
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
Average costs (2021$)
Standby power ---------------------------------------------------------------- Simple payback Average
TSL EL (W) First year's Lifetime (years) lifetime
Installed cost operating cost operating cost LCC (years)
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
0 .............. $546.11 $2.74 $24.75 $570.86 .............. 10.78
1............................................................... 1 1.5 546.11 1.89 17.11 563.22 0.0 10.78
2............................................................... 2 1.0 547.28 1.29 11.65 558.93 0.8 10.78
3............................................................... 3 0.5 551.36 0.69 6.19 557.55 2.6 10.78
------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------
Note: The results for each TSL are calculated assuming that all consumers use products at that efficiency level. The simple PBP is measured relative to the baseline product.
Table V.5--Average LCC Savings Relative to the No-New-Standards Case for PC 2: Built-In and Over-the-Range
Convection Microwave Ovens
----------------------------------------------------------------------------------------------------------------
Life-cycle cost savings
----------------------------------
Percent of
TSL EL Average LCC consumers that
savings * experience net
(2021$) cost
----------------------------------------------------------------------------------------------------------------
1............................................................ 1 $0.00 0
2............................................................ 2 0.83 7
[[Page 39944]]
3............................................................ 3 1.95 42
----------------------------------------------------------------------------------------------------------------
* The savings represent the average LCC for affected consumers.
b. Consumer Subgroup Analysis
In the consumer subgroup analysis, DOE estimated the impact of the
considered TSLs on low-income households and senior-only households.
Table V.6 and Table V.7 compare the average LCC savings and PBP at each
efficiency level for the consumer subgroups with similar metrics for
the entire consumer sample for both product classes. In most cases, the
average LCC savings and PBP for low-income households and senior-only
households at the considered efficiency levels are not substantially
different from the average for all households. Chapter 11 of the final
rule TSD presents the complete LCC and PBP results for the subgroups.
Table V.6--Comparison of LCC Savings and PBP for Consumer Subgroups and All Households; PC 1: Microwave-Only Ovens and Countertop Convection Microwave
Ovens
--------------------------------------------------------------------------------------------------------------------------------------------------------
Average life-cycle cost Simple payback period Net cost (%)
savings * (2021$) (years) -----------------------------
--------------------------------------------------------------
TSL EL Low- Senior- Low- Senior-
income only Nation Low- Senior- Nation income only Nation
[Dagger] Sec. income only
--------------------------------------------------------------------------------------------------------------------------------------------------------
1.................................................. 1 $0.25 $0.25 $0.25 0.3 0.3 0.3 0 0 0
2.................................................. 2 0.99 0.97 0.99 1.3 1.3 1.3 6 5 5
3.................................................. 3 2.13 2.12 2.16 2.0 2.0 2.0 13 12 12
--------------------------------------------------------------------------------------------------------------------------------------------------------
* The savings represent the average LCC for affected consumers.
[Dagger] Low-income households represent 12.5 percent of all households for this product class.
Sec. Senior-only households represent 24.7 percent of all households for this product class.
Table V.7--Comparison of LCC Savings and PBP for Consumer Subgroups and All Households; PC 2: Built-In and Over-the-Range Convection Microwave Ovens
--------------------------------------------------------------------------------------------------------------------------------------------------------
Average life-cycle cost Simple payback period Net cost (%)
savings * (2021$) (years) -----------------------------
--------------------------------------------------------------
TSL EL Low- Senior- Low- Senior-
income only Nation Low- Senior- Nation income only Nation
[Dagger] Sec. income only
--------------------------------------------------------------------------------------------------------------------------------------------------------
1.................................................. 1 $0.00 $0.00 $0.00 0.0 0.0 0.0 0 0 0
2.................................................. 2 0.76 0.76 0.83 0.8 0.8 0.8 8 8 7
3.................................................. 3 1.79 1.79 1.95 2.6 2.6 2.6 43 43 42
--------------------------------------------------------------------------------------------------------------------------------------------------------
* The savings represent the average LCC for affected consumers.
[Dagger] Low-income households represent 12.5 percent of all households for this product class.
Sec. Senior-only households represent 24.7 percent of all households for this product class.
c. Rebuttable Presumption Payback
As discussed in section III.E.2 of this document, EPCA establishes
a rebuttable presumption that an energy conservation standard is
economically justified if the increased purchase cost for a product
that meets the standard is less than three times the value of the
first-year energy savings resulting from the standard. In calculating a
rebuttable presumption payback period for each of the considered TSLs,
DOE used discrete values, and, as required by EPCA, based the energy
use calculation on the DOE test procedures for microwave ovens. In
contrast, the PBPs presented in section V.B.1.a of this document were
calculated using distributions that reflect the range of energy use in
the field.
Table V.8 presents the rebuttable-presumption payback periods for
the considered TSLs for microwave ovens. While DOE examined the
rebuttable-presumption criterion, it considered whether the standard
levels considered for this rule are economically justified through a
more detailed analysis of the economic impacts of those levels,
pursuant to 42 U.S.C. 6295(o)(2)(B)(i), that considers the full range
of impacts to the consumer, manufacturer, Nation, and environment. The
results of that analysis serve as the basis for DOE to definitively
evaluate the economic justification for a potential standard level,
thereby supporting or rebutting the results of any preliminary
determination of economic justification.
[[Page 39945]]
Table V.8--Rebuttable-Presumption Payback Periods
----------------------------------------------------------------------------------------------------------------
Product class 1 2 3
----------------------------------------------------------------------------------------------------------------
(years)
----------------------------------------------------------------------------------------------------------------
PC 1: Microwave-Only and Countertop Convection.................. 2.1 2.2 2.2
PC 2: Built-In and Over-the-Range Convection.................... 0.0 2.2 2.7
----------------------------------------------------------------------------------------------------------------
2. Economic Impacts on Manufacturers
DOE performed an MIA to estimate the impact of amended energy
conservation standards on manufacturers of microwave ovens. The next
section describes the expected impacts on manufacturers at each
considered TSL. Chapter 12 of the final rule TSD explains the analysis
in further detail.
a. Industry Cash Flow Analysis Results
In this section, DOE provides GRIM results from the analysis, which
examines changes in the industry that would result from a standard. The
following tables summarize the estimated financial impacts (represented
by changes in INPV) of potential amended energy conservation standards
on manufacturers of microwave ovens, as well as the conversion costs
that DOE estimates manufacturers of microwave ovens would incur at each
TSL. To evaluate the range of cash-flow impacts on the microwave oven
industry, DOE modeled two manufacturer markup scenarios using different
assumptions that correspond to the range of anticipated market
responses to amended energy conservation standards: (1) the conversion
cost recovery scenario and (2) the constant price scenario.
To assess the lowest magnitude of the range of potential impacts,
DOE modeled a conversion cost recovery scenario in which manufacturers
are able to increase their manufacturer markups in response to amended
energy conservation standards. To assess the largest magnitude of the
range of potential impacts, DOE modeled a constant price scenario in
which manufacturers incur conversion costs but do not receive any
additional revenue from these redesign efforts.
As noted in the MIA methodology discussion (see section IV.J of
this document), in addition to manufacturer markup scenarios, the MPCs,
shipments, and conversion cost assumptions also affect INPV results.
The results in Table V.9 and Table V.10 present potential INPV
impacts for microwave oven manufacturers. Table V.9 reflects the lowest
magnitude of potential impacts (conversion cost recovery scenario), and
Table V.10 represents the largest magnitude of potential impacts
(constant price scenario). In the following discussion, the INPV
results refer to the difference in industry value between the no-new-
standards case and each standards case that results from the sum of
discounted cash flows from 2023 (the reference year) through 2055 (the
end of the analysis period).
Table V.9--Manufacturer Impact Analysis Results--Conversion Cost Recovery Scenario
----------------------------------------------------------------------------------------------------------------
Trial standard level *
Units No-new- -----------------------------------------------
standards case 1 2 3
----------------------------------------------------------------------------------------------------------------
INPV.......................... 2021$ millions.. 1,426 1,426 1,426 1,426
Change in INPV................ 2021$ millions.. .............. 0.0 0.0 0.0
%............... .............. 0.0 0.0 0.0
Product Conversion Costs...... 2021$ millions.. .............. 2.8 23.6 55.0
Capital Conversion Costs...... 2021$ millions.. .............. 2.5 22.5 53.3
Total Conversion Costs........ 2021$ millions.. .............. 5.3 46.1 108.3
----------------------------------------------------------------------------------------------------------------
* Parentheses indicate negative values. Numbers may not sum exactly due to rounding.
Table V.10--Manufacturer Impact Analysis Results--Constant Price Scenario
----------------------------------------------------------------------------------------------------------------
Trial standard level *
Units No-new- -----------------------------------------------
standards case 1 2 3
----------------------------------------------------------------------------------------------------------------
INPV.......................... 2021$ millions.. 1,426 1,422 1,389 1,339
Change in INPV................ 2021$ millions.. .............. (4.2) (37.2) (87.5)
%............... .............. (0.3) (2.6) (6.1)
Product Conversion Costs...... 2021$ millions.. .............. 2.8 23.6 55.0
Capital Conversion Costs...... 2021$ millions.. .............. 2.5 22.5 53.3
Total Conversion Costs........ 2021$ millions.. .............. 5.3 46.1 108.3
----------------------------------------------------------------------------------------------------------------
* Parentheses indicate negative values. Numbers may not sum exactly due to rounding.
At TSL 1, DOE estimates impacts on INPV will range from -$4.2
million, which represents a change of -0.3 percent, to no change in
INPV. At TSL 1, industry free cash flow decreases to $98 million, which
represents a decrease of approximately 2.1 percent, compared to the no-
new-standards case value of $100 million in 2025, the year leading up
to the compliance date.
TSL 1 would set the energy conservation standard for both product
classes at EL 1. DOE estimates that 85 percent of Product Class 1
shipments and 100 percent of Product Class 2 shipments would already
meet or exceed the efficiency levels required at TSL 1. DOE expects
microwave oven manufacturers to incur approximately
[[Page 39946]]
$2.8 million in product conversion costs to redesign and re-test non-
compliant models and approximately $2.5 million in capital conversion
costs to purchase new tooling and equipment necessary to produce these
redesigned models.
At TSL 2, DOE estimates that impacts on INPV will range from -$37.2
million, which represents a change of -2.6 percent, to no change in
INPV. At TSL 2, industry free cash flow decreases to $82 million, which
represents a decrease of approximately 18.4 percent, compared to the
no-new-standards case value of $100 million in 2025, the year leading
up to the compliance date.
TSL 2 would set the energy conservation standard for both product
classes at EL 2. DOE estimates that 40 percent of Product Class 1
shipments and 64 percent of Product Class 2 shipments would already
meet or exceed the efficiency levels required at TSL 2. DOE expects
microwave oven manufacturers to incur approximately $23.6 million in
product conversion costs to redesign and re-test non-compliant models
and approximately $22.5 million in capital conversion costs to purchase
new tooling and equipment necessary to produce these redesigned models.
At TSL 3, DOE estimates impacts on INPV will range from -$87.5
million, which represents a change of -6.1 percent, to no change in
INPV. At TSL 3, industry free cash flow decreases to $57 million, which
represents a decrease of approximately 43.3 percent compared to the no-
new-standards case value of $100 million in 2025, the year leading up
to the compliance date.
TSL 3 would set the energy conservation standard for both product
classes at max-tech (EL 3). DOE estimates that 11 percent of Product
Class 1 shipments and 5 percent of Product Class 2 shipments would
already meet the efficiency levels required at TSL 3. DOE expects
microwave oven manufacturers to incur approximately $55.0 million in
product conversion costs to redesign and re-test non-compliant models
and approximately $53.3 million in capital conversion costs to purchase
new tooling and equipment necessary to produce these redesigned models.
b. Direct Impacts on Employment
DOE estimates that over 95 percent of microwave oven manufacturing
occurs outside the United States. Furthermore, none of the analyzed
efficiency levels require additional labor and would not impact current
manufacturing labor practices. Therefore, DOE estimates that there will
be no direct impacts on domestic employment at any of the analyzed
TSLs.
c. Impacts on Manufacturing Capacity
DOE assumes manufacturers will meet amended energy conservation
standards for microwave ovens by re-designing the control boards of
non-compliant models. DOE estimates that approximately 89 percent of
Product Class 1 shipments and 95 percent of Product Class 2 shipments
will need to be redesigned to meet the efficiency levels required at
TSL 3. This represents a need to redesign models accounting for
approximately 10.5 million Product Class 1 units and 0.4 million
Product Class 2 units. Manufacturers have expressed concern that
redesigning 90 percent of all microwave oven models in a three-year
time period might not be possible.
At TSL 2, DOE estimates that approximately 60 percent of Product
Class 1 shipments and 36 percent of Product Class 2 shipments will need
to be redesigned to meet the efficiency levels; at TSL 1, DOE estimates
that approximately 15 percent of Product Class 1 shipments and no
Product Class 2 shipments will need to be redesigned to meet the
efficiency levels. Both of the redesign requirements at TSL 1 and TSL 2
are unlikely to cause a significant capacity concern for most microwave
oven manufacturers.
d. Impacts on Subgroups of Manufacturers
Small manufacturers, niche equipment manufacturers, and
manufacturers exhibiting a cost structure substantially different from
the industry average could be affected disproportionately. Using
average cost assumptions developed for an industry cash-flow estimate
is inadequate to assess differential impacts among manufacturer
subgroups.
For the microwave oven industry, DOE identified and evaluated the
impact of amended energy conservation standards on one subgroup--small
manufacturers. The Small Business Administration (``SBA'') defines a
``small business'' as having 1,500 employees or fewer for the North
American Industry Classification System (``NAICS'') code 335220,
``Major Household Appliance Manufacturing.'' \54\ For a discussion of
the impacts on the small manufacturer subgroup, see the regulatory
flexibility analysis in section VI.B of this document and chapter 12 of
the final rule TSD.
---------------------------------------------------------------------------
\54\ Available at www.sba.gov/document/support-table-size-standards (last accessed on Jan. 11, 2023).
---------------------------------------------------------------------------
e. Cumulative Regulatory Burden
One aspect of assessing manufacturer burden involves looking at the
cumulative impact of multiple DOE standards and the regulatory actions
of other Federal agencies and States that affect the manufacturers of a
covered product or equipment. While any one regulation may not impose a
significant burden on manufacturers, the combined effects of several
existing or impending regulations may have serious consequences for
some manufacturers, groups of manufacturers, or an entire industry.
Multiple regulations affecting the same manufacturer can strain profits
and lead companies to abandon product lines or markets with lower
expected future returns than competing products. For these reasons, DOE
conducts an analysis of cumulative regulatory burden as part of its
rulemakings pertaining to appliance efficiency.
DOE evaluates product-specific regulations that will take effect
approximately 3 years before or after the estimated 2026 compliance
date of any amended energy conservation standards for microwave ovens.
This information is presented in Table V.11.
[[Page 39947]]
Table V.11--Compliance Dates and Expected Conversion Expenses of Federal Energy Conservation Standards Affecting
Microwave Oven Manufacturers
----------------------------------------------------------------------------------------------------------------
Number of Industry
manufacturers Industry conversion
Federal energy conservation Number of mfrs affected from Approx. conversion costs costs/product
standard * today's rule standards year (millions$) revenue ***
** (%)
----------------------------------------------------------------------------------------------------------------
Portable Air Conditioners, 85 11 2 2025 $320.9 6.7
FR 1378 (Jan. 10, 2020)..... (2015$)
Room Air Conditioners 8 3 2026 $24.8 0.4
[Dagger].................... (2021$)
Consumer Clothes Dryers, 87 15 9 2027 $149.7 1.8
FR 51734 (Aug. 23, 2022) (2020$)
[dagger]....................
Consumer Conventional Cooking 34 10 2027 $183.4 1.2
Products, 88 FR 6818 (Feb. (2021$)
1, 2023) [dagger][dagger]...
Residential Clothes Washers, 19 5 2027 $690.8 5.2
88 FR 13520 (Mar. 3, 2023) (2021$)
[dagger][dagger]............
Refrigerators, Refrigerator- 49 12 2027 $1,323.6 3.8
Freezers, and Freezers, 88 (2021$)
FR 12452 (Feb. 27, 2023)
[dagger][dagger]............
Miscellaneous Refrigeration 38 7 2029 $126.9 3.1
Products, 88 FR 19382 (Mar. (2021$)
31, 2023) [dagger][dagger]..
----------------------------------------------------------------------------------------------------------------
* This column presents the total number of manufacturers identified in the energy conservation standard rule
contributing to cumulative regulatory burden.
** This column presents the number of manufacturers producing microwave ovens that are also listed as
manufacturers in the listed energy conservation standard contributing to cumulative regulatory burden.
*** This column presents industry conversion costs as a percentage of product revenue during the conversion
period. Industry conversion costs are the upfront investments manufacturers must make to sell compliant
products/equipment. The revenue used for this calculation is the revenue from just the covered product/
equipment associated with each row. The conversion period is the time frame over which conversion costs are
made and lasts from the publication year of the final rule to the compliance year of the energy conservation
standard. The conversion period typically ranges from 3 to 5 years, depending on the rulemaking.
[Dagger] At the time of issuance of this microwave ovens rulemaking, the rulemaking has been issued and is
pending publication in the Federal Register. Once published, the room air conditioners final rule will be
available at: www.regulations.gov/docket/EERE-2014-BT-STD-0059.
[dagger][dagger] Indicates a proposed rulemaking. Values could change upon publication of a final rule.
In addition to the rulemakings listed in Table V.11, DOE has other
ongoing rulemakings for products that microwave oven manufacturers
produce: dishwashers \55\ and dehumidifiers.\56\
---------------------------------------------------------------------------
\55\ www.regulations.gov/docket/EERE-2014-BT-STD-0021.
\56\ www.regulations.gov/docket/EERE-2019-BT-STD-0043.
---------------------------------------------------------------------------
3. National Impact Analysis
This section presents DOE's estimates of the national energy
savings and the NPV of consumer benefits that would result from each of
the TSLs considered as potential amended standards.
a. Significance of Energy Savings
To estimate the energy savings attributable to potential amended
standards for microwave ovens, DOE compared their energy consumption
under the no-new-standards case to their anticipated energy consumption
under each TSL. The savings are measured over the entire lifetime of
products purchased in the 30-year period that begins in the year of
anticipated compliance with amended standards (2026-2055). Table V.12
presents DOE's projections of the national energy savings for each TSL
considered for microwave ovens. The savings were calculated using the
approach described in section IV.H.2 of this document.
Table V.12--Cumulative National Energy Savings for Microwave Ovens; 30 Years of Shipments
[2026-2055]
----------------------------------------------------------------------------------------------------------------
Trial standard level
-----------------------------------------------
1 2 3
----------------------------------------------------------------------------------------------------------------
(quads)
-----------------------------------------------
Primary energy.................................................. 0.01 0.05 0.12
FFC energy...................................................... 0.01 0.06 0.12
----------------------------------------------------------------------------------------------------------------
OMB Circular A-4 \57\ requires agencies to present analytical
results, including separate schedules of the monetized benefits and
costs that show the type and timing of benefits and costs. Circular A-4
also directs agencies
[[Page 39948]]
to consider the variability of key elements underlying the estimates of
benefits and costs. For this rulemaking, DOE undertook a sensitivity
analysis using 9 years, rather than 30 years, of product shipments. The
choice of a 9-year period is a proxy for the timeline in EPCA for the
review of certain energy conservation standards and potential revision
of and compliance with such revised standards.\58\ The review timeframe
established in EPCA is generally not synchronized with the product
lifetime, product manufacturing cycles, or other factors specific to
microwave ovens. Thus, such results are presented for informational
purposes only and are not indicative of any change in DOE's analytical
methodology. The NES sensitivity analysis results based on a 9-year
analytical period are presented in Table V.13. The impacts are counted
over the lifetime of microwave ovens purchased in 2026-2055.
---------------------------------------------------------------------------
\57\ U.S. Office of Management and Budget. Circular A-4:
Regulatory Analysis. September 17, 2003.
obamawhitehouse.archives.gov/omb/circulars_a004_a-4/ (last accessed
January 13, 2023).
\58\ EPCA requires DOE to review its standards at least once
every 6 years, and requires, for certain products, a 3-year period
after any new standard is promulgated before compliance is required,
except that in no case may any new standards be required within 6
years of the compliance date of the previous standards. While adding
a 6-year review to the 3-year compliance period adds up to 9 years,
DOE notes that it may undertake reviews at any time within the 6-
year period and that the 3-year compliance date may yield to the 6-
year backstop. A 9-year analysis period may not be appropriate given
the variability that occurs in the timing of standards reviews and
the fact that for some products, the compliance period is 5 years
rather than 3 years.
Table V.13--Cumulative National Energy Savings for Microwave Ovens; 9 Years of Shipments
[2026-2055]
----------------------------------------------------------------------------------------------------------------
Trial standard level
-----------------------------------------------
1 2 3
----------------------------------------------------------------------------------------------------------------
(quads)
-----------------------------------------------
Source energy................................................... 0.003 0.014 0.034
FFC energy...................................................... 0.003 0.015 0.035
----------------------------------------------------------------------------------------------------------------
b. Net Present Value of Consumer Costs and Benefits
DOE estimated the cumulative NPV of the total costs and savings for
consumers that would result from the TSLs considered for microwave
ovens. In accordance with OMB's guidelines on regulatory analysis,\59\
DOE calculated NPV using both a 7-percent and a 3-percent real discount
rate. Table V.14 shows the consumer NPV results with impacts counted
over the lifetime of products purchased in 2026-2055.
---------------------------------------------------------------------------
\59\ U.S. Office of Management and Budget. Circular A-4:
Regulatory Analysis. September 17, 2003.
obamawhitehouse.archives.gov/omb/circulars_a004_a-4/ (last accessed
December 13, 2022).
Table V.14--Cumulative Net Present Value of Consumer Benefits for Microwave Ovens; 30 Years of Shipments
[2026-2055]
----------------------------------------------------------------------------------------------------------------
Trial standard level
Discount rate -----------------------------------------------
1 2 3
----------------------------------------------------------------------------------------------------------------
(billion 2021$)
-----------------------------------------------
3 percent....................................................... 0.080 0.353 0.710
7 percent....................................................... 0.039 0.164 0.320
----------------------------------------------------------------------------------------------------------------
The NPV results based on the aforementioned 9-year analytical
period are presented in Table V.15. The impacts are counted over the
lifetime of products purchased in 2026-2055. As mentioned previously,
such results are presented for informational purposes only and are not
indicative of any change in DOE's analytical methodology or decision
criteria.
Table V.15--Cumulative Net Present Value of Consumer Benefits for Microwave Ovens; 9 Years of Shipments
[2026-2055]
----------------------------------------------------------------------------------------------------------------
Trial standard level
Discount rate -----------------------------------------------
1 2 3
----------------------------------------------------------------------------------------------------------------
(billion 2021$)
-----------------------------------------------
3 percent....................................................... 0.030 0.127 0.266
7 percent....................................................... 0.020 0.079 0.160
----------------------------------------------------------------------------------------------------------------
[[Page 39949]]
The previous results reflect the use of a default trend to estimate
the change in price for microwave ovens over the analysis period (see
section IV.F.1 of this document). DOE also conducted a sensitivity
analysis that considered one scenario with a lower rate of price
decline than the reference case and one scenario with a higher rate of
price decline than the reference case. The results of these alternative
cases are presented in appendix 10C of the final rule TSD. In the high-
price-decline case, the NPV of consumer benefits is higher than in the
default case. In the low-price-decline case, the NPV of consumer
benefits is lower than in the default case.
c. Indirect Impacts on Employment
DOE estimates that amended energy conservation standards for
microwave ovens will reduce energy expenditures for consumers of those
products, with the resulting net savings being redirected to other
forms of economic activity. These expected shifts in spending and
economic activity could affect the demand for labor. As described in
section IV.N of this document, DOE used an input/output model of the
U.S. economy to estimate indirect employment impacts of the TSLs that
DOE considered. There are uncertainties involved in projecting
employment impacts, especially changes in the later years of the
analysis. Therefore, DOE generated results for near-term timeframes
(2026-2031), where these uncertainties are reduced.
The results suggest that the adopted standards are likely to have a
negligible impact on the net demand for labor in the economy. The net
change in jobs is so small that it would be imperceptible in national
labor statistics and might be offset by other, unanticipated effects on
employment. Chapter 16 of the final rule TSD presents detailed results
regarding anticipated indirect employment impacts.
4. Impact on Utility or Performance of Products
As discussed in section IV.C.1.b of this document, DOE has
concluded that the standards adopted in this final rule will not lessen
the utility or performance of the microwave ovens under consideration
in this rulemaking. Manufacturers of these products currently offer
units that meet or exceed the adopted standards.
5. Impact of Any Lessening of Competition
DOE considered any lessening of competition that would be likely to
result from new or amended standards. As discussed in section III.E.1.e
of this document, EPCA directs the Attorney General of the United
States (``Attorney General'') to determine the impact, if any, of any
lessening of competition likely to result from a proposed standard and
to transmit such determination in writing to the Secretary within 60
days of the publication of a proposed rule, together with an analysis
of the nature and extent of the impact. To assist the Attorney General
in making this determination, DOE provided the Department of Justice
(``DOJ'') with copies of the August 2022 SNOPR and the SNOPR TSD for
review. In its assessment letter responding to DOE, DOJ concluded that
the proposed energy conservation standards for microwave ovens are
unlikely to have a significant adverse impact on competition. DOE is
publishing the Attorney General's assessment at the end of this final
rule.
6. Need of the Nation To Conserve Energy
Enhanced energy efficiency, where economically justified, improves
the Nation's energy security, strengthens the economy, and reduces the
environmental impacts (costs) of energy production. Reduced electricity
demand due to energy conservation standards is also likely to reduce
the cost of maintaining the reliability of the electricity system,
particularly during peak-load periods. Chapter 15 of the final rule TSD
presents the estimated impacts on electricity generating capacity,
relative to the no-new-standards case, for the TSLs that DOE considered
in this rulemaking.
Energy conservation resulting from potential energy conservation
standards for microwave ovens is expected to yield environmental
benefits in the form of reduced emissions of certain air pollutants and
greenhouse gases. Table V.16 provides DOE's estimate of cumulative
emissions reductions expected to result from the TSLs considered in
this rulemaking. The emissions were calculated using the multipliers
discussed in section IV.K of this document. DOE reports annual
emissions reductions for each TSL in chapter 13 of the final rule TSD.
Table V.16--Cumulative Emissions Reduction for Microwave Ovens Shipped in 2026-2055
----------------------------------------------------------------------------------------------------------------
Trial standard level
-----------------------------------------------
1 2 3
----------------------------------------------------------------------------------------------------------------
Power Sector Emissions
----------------------------------------------------------------------------------------------------------------
CO2 (million metric tons)....................................... 0.33 1.74 3.92
CH4 (thousand tons)............................................. 0.03 0.14 0.31
N2O (thousand tons)............................................. 0.00 0.02 0.04
SO2 (thousand tons)............................................. 0.16 0.84 1.89
NOX (thousand tons)............................................. 0.17 0.88 1.98
Hg (tons)....................................................... 0.00 0.01 0.01
----------------------------------------------------------------------------------------------------------------
Upstream Emissions
----------------------------------------------------------------------------------------------------------------
CO2 (million metric tons)....................................... 0.03 0.13 0.30
CH4 (thousand tons)............................................. 2.39 12.50 28.14
N2O (thousand tons)............................................. 0.00 0.00 0.00
SO2 (thousand tons)............................................. 0.00 0.01 0.02
NOX (thousand tons)............................................. 0.38 2.00 4.51
Hg (tons)....................................................... 0.00 0.00 0.00
----------------------------------------------------------------------------------------------------------------
Total FFC Emissions
----------------------------------------------------------------------------------------------------------------
CO2 (million metric tons)....................................... 0.36 1.87 4.21
CH4 (thousand tons)............................................. 2.41 12.64 28.45
[[Page 39950]]
N2O (thousand tons)............................................. 0.00 0.02 0.04
SO2 (thousand tons)............................................. 0.16 0.85 1.91
NOX (thousand tons)............................................. 0.55 2.88 6.49
Hg (tons)....................................................... 0.00 0.01 0.01
----------------------------------------------------------------------------------------------------------------
As part of the analysis for this rule, DOE estimated monetary
benefits likely to result from the reduced emissions of CO2
that DOE estimated for each of the considered TSLs for microwave ovens.
Section IV.L of this document discusses the estimated SC-CO2
values that DOE used. Table V.17 presents the value of CO2
emissions reduction at each TSL for each of the SC-CO2
cases. The time-series of annual values is presented for the selected
TSL in chapter 14 of the final rule TSD.
Table V.17--Present Value of CO2 Emissions Reduction for Microwave Ovens Shipped in 2026-2055
----------------------------------------------------------------------------------------------------------------
SC-CO2 case
---------------------------------------------------------------
Discount rate and statistics
---------------------------------------------------------------
TSL 5% 3% 2.5% 3%
---------------------------------------------------------------
95th
Average Average Average percentile
----------------------------------------------------------------------------------------------------------------
(million 2021$)
---------------------------------------------------------------
1............................................... 3.63 15.19 23.58 46.17
2............................................... 19.00 79.47 123.39 241.61
3............................................... 42.78 178.91 277.80 543.96
----------------------------------------------------------------------------------------------------------------
As discussed in section IV.L.2 of this document, DOE estimated the
climate benefits likely to result from the reduced emissions of methane
and N2O that DOE estimated for each of the considered TSLs
for microwave ovens. Table V.18 presents the value of the
CH4 emissions reduction at each TSL, and Table V.19 presents
the value of the N2O emissions reduction at each TSL. The
time-series of annual values is presented for the selected TSL in
chapter 14 of the final rule TSD.
Table V.18--Present Value of Methane Emissions Reduction for Microwave Ovens Shipped in 2026-2055
----------------------------------------------------------------------------------------------------------------
SC-CH4 case
---------------------------------------------------------------
Discount rate and statistics
---------------------------------------------------------------
TSL 5% 3% 2.5% 3%
---------------------------------------------------------------
95th
Average Average Average percentile
----------------------------------------------------------------------------------------------------------------
(million 2021$)
---------------------------------------------------------------
1............................................... 1.11 3.22 4.46 8.51
2............................................... 5.82 16.83 23.33 44.56
3............................................... 13.10 37.90 52.52 100.31
----------------------------------------------------------------------------------------------------------------
Table V.19--Present Value of Nitrous Oxide Emissions Reduction for Microwave Ovens Shipped in 2026-2055
----------------------------------------------------------------------------------------------------------------
SC-N2O Case
---------------------------------------------------------------
Discount rate and statistics
---------------------------------------------------------------
TSL 5% 3% 2.5% 3%
---------------------------------------------------------------
95th
Average Average Average percentile
----------------------------------------------------------------------------------------------------------------
(million 2021$)
---------------------------------------------------------------
1............................................... 0.01 0.06 0.09 0.15
2............................................... 0.08 0.29 0.45 0.78
3............................................... 0.17 0.66 1.02 1.76
----------------------------------------------------------------------------------------------------------------
[[Page 39951]]
DOE is well aware that scientific and economic knowledge about the
contribution of CO2 and other GHG emissions to changes in
the future global climate and the potential resulting damages to the
global and U.S. economy continues to evolve rapidly. DOE, together with
other Federal agencies, will continue to review methodologies for
estimating the monetary value of reductions in CO2 and other
GHG emissions. This ongoing review will consider the comments on this
subject that are part of the public record for this and other
rulemakings, as well as other methodological assumptions and issues.
DOE notes, however, that the adopted standards would be economically
justified even without inclusion of monetized benefits of reduced GHG
emissions.
DOE also estimated the monetary value of the economic benefits
associated with NOX and SO2 emissions reductions
anticipated to result from the considered TSLs for microwave ovens. The
dollar-per-ton values that DOE used are discussed in section IV.L of
this document. Table V.20 presents the present value for NOX
emissions reduction for each TSL calculated using 7-percent and 3-
percent discount rates, and Table V.21 presents similar results for
SO2 emissions reductions. The results in these tables
reflect application of EPA's low dollar-per-ton values, which DOE used
to be conservative. The time-series of annual values is presented for
the selected TSL in chapter 14 of the final rule TSD.
Table V.20--Present Value of NOX Emissions Reduction for Microwave Ovens
Shipped in 2026-2055
------------------------------------------------------------------------
7% Discount 3% Discount
TSL rate rate
------------------------------------------------------------------------
(million 2021$)
-------------------------------
1....................................... 10.11 23.20
2....................................... 52.89 121.38
3....................................... 119.07 273.27
------------------------------------------------------------------------
Table V.21--Present Value of SO2 Emissions Reduction for Microwave Ovens
Shipped in 2026-2055
------------------------------------------------------------------------
7% Discount 3% Discount
TSL rate rate
------------------------------------------------------------------------
(million 2021$)
-------------------------------
1....................................... 4.17 9.26
2....................................... 21.80 48.47
3....................................... 49.08 109.13
------------------------------------------------------------------------
Not all the public health and environmental benefits from the
reduction of greenhouse gases, NOX, and SO2 are
captured in the values above, and additional unquantified benefits from
the reductions of those pollutants as well as from the reduction of
direct PM and other co-pollutants may be significant. DOE has not
included monetary benefits of the reduction of Hg emissions because the
amount of reduction is very small.
7. Other Factors
The Secretary of Energy, in determining whether a standard is
economically justified, may consider any other factors that the
Secretary deems to be relevant. (42 U.S.C. 6295(o)(2)(B)(i)(VII)) No
other factors were considered in this analysis.
8. Summary of Economic Impacts
Table V.22 presents the NPV values that result from adding the
estimates of the economic benefits resulting from reduced GHG and
NOX and SO2 emissions to the NPV of consumer
benefits calculated for each TSL considered in this rulemaking. The
consumer benefits are domestic U.S. monetary savings that occur as a
result of purchasing the covered products and are measured for the
lifetime of products shipped in 2026-2055. The climate benefits
associated with reduced GHG emissions resulting from the adopted
standards are global benefits, and are also calculated based on the
lifetime of microwave ovens shipped in 2026-2055.
Table V.22--Consumer NPV Combined With Present Value of Climate Benefits and Health Benefits
----------------------------------------------------------------------------------------------------------------
Category TSL 1 TSL 2 TSL 3
----------------------------------------------------------------------------------------------------------------
Using 3% discount rate for Consumer NPV and Health Benefits (billion 2021$)
----------------------------------------------------------------------------------------------------------------
5% Average SC-GHG case.......................................... 0.1 0.5 1.1
3% Average SC-GHG case.......................................... 0.1 0.6 1.3
2.5% Average SC-GHG case........................................ 0.1 0.7 1.4
3% 95th percentile SC-GHG case.................................. 0.2 0.8 1.7
----------------------------------------------------------------------------------------------------------------
Using 7% discount rate for Consumer NPV and Health Benefits (billion 2021$)
----------------------------------------------------------------------------------------------------------------
5% Average SC-GHG case.......................................... 0.1 0.3 0.5
3% Average SC-GHG case.......................................... 0.1 0.3 0.7
2.5% Average SC-GHG case........................................ 0.1 0.4 0.8
3% 95th percentile SC-GHG case.................................. 0.1 0.5 1.1
----------------------------------------------------------------------------------------------------------------
C. Conclusion
When considering new or amended energy conservation standards, the
standards that DOE adopts for any type (or class) of covered product
must be designed to achieve the maximum improvement in energy
efficiency that the Secretary determines is technologically feasible
and economically justified. (42 U.S.C. 6295(o)(2)(A)) In determining
whether a standard is economically justified, the Secretary must
determine whether the benefits of the standard exceed its burdens by,
to the greatest extent practicable, considering the seven statutory
factors discussed previously. (42 U.S.C. 6295(o)(2)(B)(i)) The new or
amended standard must also result in significant conservation of
energy. (42 U.S.C. 6295(o)(3)(B))
In the August 2022 SNOPR, DOE proposed energy conservation
standards for microwave ovens at TSL 2, as constructed for that
analysis. The minimum wattages corresponding to TSL 2 from the August
2022 SNOPR are shown in Table V.23. 87 FR 52282 (Aug. 25, 2022).
[[Page 39952]]
Table V.23--Proposed Energy Conservation Standards for Microwave Ovens
------------------------------------------------------------------------
Maximum allowable
Product class average standby
power (watts)
------------------------------------------------------------------------
PC 1: Microwave-Only Ovens and Countertop Convection 0.6 W
Microwave Ovens.....................................
PC 2: Built-In and Over-the-Range Convection 1.0 W
Microwave Ovens.....................................
------------------------------------------------------------------------
For this final rule, DOE considered the impacts of amended
standards for microwave ovens at each TSL, beginning with the maximum
technologically feasible level, to determine whether that level was
economically justified. Where the max-tech level was not justified, DOE
then considered the next most efficient level and undertook the same
evaluation until it reached the highest efficiency level that is both
technologically feasible and economically justified and saves a
significant amount of energy.
To aid the reader as DOE discusses the benefits and/or burdens of
each TSL, tables in this section present a summary of the results of
DOE's quantitative analysis for each TSL. In addition to the
quantitative results presented in the tables, DOE also considers other
burdens and benefits that affect economic justification. These include
the impacts on identifiable subgroups of consumers who may be
disproportionately affected by a national standard and impacts on
employment.
DOE also notes that the economics literature provides a wide-
ranging discussion of how consumers trade off upfront costs and energy
savings in the absence of government intervention. Much of this
literature attempts to explain why consumers appear to undervalue
energy efficiency improvements. There is evidence that consumers
undervalue future energy savings as a result of (1) a lack of
information; (2) a lack of sufficient salience of the long-term or
aggregate benefits; (3) a lack of sufficient savings to warrant
delaying or altering purchases; (4) excessive focus on the short term,
in the form of inconsistent weighting of future energy cost savings
relative to available returns on other investments; (5) computational
or other difficulties associated with the evaluation of relevant
tradeoffs; and (6) a divergence in incentives (for example, between
renters and owners, or builders and purchasers). Having less than
perfect foresight and a high degree of uncertainty about the future,
consumers may trade off these types of investments at a higher-than-
expected rate between current consumption and uncertain future energy
cost savings.
In DOE's current regulatory analysis, potential changes in the
benefits and costs of a regulation due to changes in consumer purchase
decisions are included in two ways. First, if consumers forego the
purchase of a product in the standards case, this decreases sales for
product manufacturers, and the impact on manufacturers attributed to
lost revenue is included in the MIA. Second, DOE accounts for energy
savings attributable only to products actually used by consumers in the
standards case; if a standard decreases the number of products
purchased by consumers, this decreases the potential energy savings
from an energy conservation standard. DOE provides estimates of
shipments and changes in the volume of product purchases in chapter 9
of the final rule TSD. However, DOE's current analysis does not
explicitly control for heterogeneity in consumer preferences,
preferences across subcategories of products or specific features, or
consumer price sensitivity variation according to household income.\60\
---------------------------------------------------------------------------
\60\ P.C. Reiss and M.W. White. Household Electricity Demand,
Revisited. Review of Economic Studies. 2005. 72(3): pp. 853-883.
doi: 10.1111/0034-6527.00354.
---------------------------------------------------------------------------
While DOE is not prepared at present to provide a fuller
quantifiable framework for estimating the benefits and costs of changes
in consumer purchase decisions due to an energy conservation standard,
DOE is committed to developing a framework that can support empirical
quantitative tools for improved assessment of the consumer welfare
impacts of appliance standards. DOE has posted a paper that discusses
the issue of consumer welfare impacts of appliance energy conservation
standards, and potential enhancements to the methodology by which these
impacts are defined and estimated in the regulatory process.\61\ DOE
welcomes comments on how to more fully assess the potential impact of
energy conservation standards on consumer choice and how to quantify
this impact in its regulatory analysis in future rulemakings.
---------------------------------------------------------------------------
\61\ Sanstad, A.H. Notes on the Economics of Household Energy
Consumption and Technology Choice. 2010. Lawrence Berkeley National
Laboratory. Available at www1.eere.energy.gov/buildings/appliance_standards/pdfs/consumer_ee_theory.pdf (last accessed July
1, 2021).
---------------------------------------------------------------------------
1. Benefits and Burdens of TSLs Considered for Microwave Ovens
Standards
Table V.24 and Table V.25 summarize the quantitative impacts
estimated for each TSL for microwave ovens. The national impacts are
measured over the lifetime of microwave ovens purchased in the 30-year
period that begins in the anticipated year of compliance with amended
standards (2026-2055). The energy savings, emissions reductions, and
value of emissions reductions refer to full-fuel-cycle results. DOE is
presenting monetized benefits in accordance with the applicable
Executive orders and DOE would reach the same conclusion presented in
this notice in the absence of the social cost of greenhouse gases,
including the Interim Estimates presented by the Interagency Working
Group. The efficiency levels contained in each TSL are described in
section V.A of this document.
[[Page 39953]]
Table V.24--Summary of Analytical Results for Microwave Ovens TSLs: National Impacts
----------------------------------------------------------------------------------------------------------------
Category TSL 1 TSL 2 TSL 3
----------------------------------------------------------------------------------------------------------------
Cumulative FFC National Energy Savings
----------------------------------------------------------------------------------------------------------------
Quads........................................................... 0.01 0.06 0.12
----------------------------------------------------------------------------------------------------------------
Cumulative FFC Emissions Reduction
----------------------------------------------------------------------------------------------------------------
CO2 (million metric tons)....................................... 0.36 1.87 4.21
CH4 (thousand tons)............................................. 2.41 12.64 28.45
N2O (thousand tons)............................................. 0.00 0.02 0.04
SO2 (thousand tons)............................................. 0.55 2.88 6.49
NOX (thousand tons)............................................. 0.16 0.85 1.91
Hg (tons)....................................................... 0.00 0.01 0.01
----------------------------------------------------------------------------------------------------------------
Present Value of Benefits and Costs (3% discount rate, billion 2021$)
----------------------------------------------------------------------------------------------------------------
Consumer Operating Cost Savings................................. 0.08 0.43 0.98
Climate Benefits *.............................................. 0.02 0.10 0.22
Health Benefits **.............................................. 0.03 0.17 0.38
Total Benefits [dagger]......................................... 0.13 0.70 1.58
Consumer Incremental Product Costs [Dagger]..................... 0.00 0.08 0.27
Consumer Net Benefits........................................... 0.08 0.35 0.71
Total Net Benefits.............................................. 0.13 0.62 1.31
----------------------------------------------------------------------------------------------------------------
Present Value of Benefits and Costs (7% discount rate, billion 2021$)
----------------------------------------------------------------------------------------------------------------
Consumer Operating Cost Savings................................. 0.040 0.211 0.475
Climate Benefits *.............................................. 0.018 0.097 0.217
Health Benefits **.............................................. 0.014 0.075 0.168
Total Benefits [dagger]......................................... 0.073 0.382 0.860
Consumer Incremental Product Costs [Dagger]..................... 0.002 0.047 0.154
Consumer Net Benefits........................................... 0.039 0.164 0.320
Total Net Benefits.............................................. 0.072 0.336 0.706
----------------------------------------------------------------------------------------------------------------
Note: This table presents the costs and benefits associated with microwave ovens shipped in 2026-2055. These
results include benefits to consumers which accrue after 2055 from the products shipped in 2026-2055.
* Climate benefits are calculated using four different estimates of the SC-CO2, SC-CH4, and SC-N2O. Together,
these represent the global SC-GHG. For presentational purposes of this table, the climate benefits associated
with the average SC-GHG at a 3-percent discount rate are shown, but DOE does not have a single central SC-GHG
point estimate. On March 16, 2022, the Fifth Circuit Court of Appeals (No. 22-30087) granted the Federal
government's emergency motion for stay pending appeal of the February 11, 2022, preliminary injunction issued
in Louisiana v. Biden, No. 21-cv-1074-JDC-KK (W.D. La.). As a result of the Fifth Circuit's order, the
preliminary injunction is no longer in effect, pending resolution of the Federal government's appeal of that
injunction or a further court order. Among other things, the preliminary injunction enjoined the defendants in
that case from ``adopting, employing, treating as binding, or relying upon'' the interim estimates of the
social cost of greenhouse gases--which were issued by the Interagency Working Group on the Social Cost of
Greenhouse Gases on February 26, 2021--to monetize the benefits of reducing greenhouse gas emissions. As
reflected in this rule, DOE has reverted to its approach prior to the injunction and presents monetized
benefits where appropriate and permissible under law.
** Health benefits are calculated using benefit-per-ton values for NOX and SO2. DOE is currently only monetizing
(for NOX and SO2) PM2.5 precursor health benefits and (for NOX) ozone precursor health benefits, but will
continue to assess the ability to monetize other effects such as health benefits from reductions in direct
PM2.5 emissions. The health benefits are presented at real discount rates of 3 and 7 percent. See section IV.L
of this document for more details.
[dagger] Total and net benefits include consumer, climate, and health benefits. For presentation purposes, total
and net benefits for both the 3-percent and 7-percent cases are presented using the average SC-GHG with 3-
percent discount rate.
[Dagger] Costs include incremental equipment costs as well as installation costs.
Table V.25--Summary of Analytical Results for Microwave Ovens TSLs: Manufacturer and Consumer Impacts
----------------------------------------------------------------------------------------------------------------
Category TSL 1 TSL 2 TSL 3
----------------------------------------------------------------------------------------------------------------
Industry NPV (million 2021$) (No-new-standards case 1,422-1,426 1,389-1,426 1,339-1,426
INPV = 1,426).........................................
Industry NPV (% change)................................ (0.3)-0.0 (2.6)-0.0 (6.1)-0.0
----------------------------------------------------------------------------------------------------------------
Consumer Average LCC Savings (2021$)
----------------------------------------------------------------------------------------------------------------
PC 1................................................... $0.25 $0.99 $2.16
PC 2................................................... $0.00 $0.83 $1.95
Shipment-Weighted Average *............................ $0.24 $0.98 $2.15
----------------------------------------------------------------------------------------------------------------
Consumer Simple PBP (years)
----------------------------------------------------------------------------------------------------------------
PC 1................................................... 0.3 1.3 2.0
PC 2................................................... 0.0 0.8 2.6
Shipment-Weighted Average *............................ 0.3 1.3 2.0
----------------------------------------------------------------------------------------------------------------
[[Page 39954]]
Percent of Consumers that Experience a Net Cost
----------------------------------------------------------------------------------------------------------------
PC 1................................................... 0% 5% 12%
PC 2................................................... 0% 7% 42%
Shipment-Weighted Average *............................ 0% 5% 13%
----------------------------------------------------------------------------------------------------------------
DOE first considered TSL 3, which represents the max-tech
efficiency levels. TSL 3 would save an estimated 0.12 quads of energy,
an amount that DOE considers significant. Under TSL 3, the NPV of
consumer benefit would be $0.32 billion using a discount rate of 7
percent, and $0.71 billion using a discount rate of 3 percent.
The cumulative emissions reductions at TSL 3 are 4.21 Mt of
CO2, 1.91 thousand tons of SO2, 6.49 thousand
tons of NOX, 0.012 tons of Hg, 28.45 thousand tons of
CH4, and 0.04 thousand tons of N2O. The estimated
monetary value of the climate benefits from reduced GHG emissions
(associated with the average SC-GHG at a 3-percent discount rate) at
TSL 3 is $0.22 billion. The estimated monetary value of the health
benefits from reduced SO2 and NOX emissions at
TSL 3 is $0.17 billion using a 7-percent discount rate and $0.38
billion using a 3-percent discount rate.
Using a 7-percent discount rate for consumer benefits and costs,
health benefits from reduced SO2 and NOX
emissions, and the 3-percent discount rate case for climate benefits
from reduced GHG emissions, the estimated total NPV at TSL 3 is $0.71
billion. Using a 3-percent discount rate for all benefits and costs,
the estimated total NPV at TSL 3 is $1.31 billion. The estimated total
NPV is provided for additional information; however, DOE primarily
relies upon the NPV of consumer benefits when determining whether a
proposed standard level is economically justified.
At TSL 3, the average LCC impact is a savings of $2.16 for Product
Class 1 and $1.95 for Product Class 2. The simple payback period is 2.0
years for Product Class 1 and 2.6 years for Product Class 2. The
fraction of consumers experiencing a net LCC cost is 11.7 percent for
Product Class 1 and 42.2 percent for Product Class 2.
At TSL 3, the projected change in manufacturer INPV ranges from a
decrease of approximately $87.5 million, which corresponds to a
decrease of approximately 6.1 percent, to no change in INPV. At this
TSL, free cash flow is estimated to decrease by 43.3 percent compared
to the no-new-standards case value in the year before the compliance
year. DOE estimates that industry must invest $108.3 million to comply
with standards set at TSL 3. DOE estimates that approximately 11
percent of Product Class 1 (microwave-only oven and countertop
convection microwave oven) shipments and approximately 5 percent of
Product Class 2 (built-in and over-the-range convection microwave oven)
shipments would meet the efficiency levels analyzed at TSL 3, in the
no-new-standards case. Redesigning approximately 90 percent of
microwave ovens models, which represents approximately 11 million
annual shipments, will significantly strain manufacturers' limited
resources during the 3-year compliance period, given the number of
microwave oven models that need to be redesigned during this time-
period. It is unclear if most microwave oven manufacturers will have
the engineering capacity to complete the necessary redesigns within the
3-year compliance period. If manufacturers require more than three
years to redesign all their non-compliant microwave oven models, they
will likely prioritize redesigns based on sales volume, which could
lead to some microwave oven models being temporary or permanent
unavailable.
DOE has determined through its engineering analysis that many of
the features which comprise the full complement of existing consumer
functionality are implemented in microwave ovens currently available on
the market at or near the max-tech efficiency levels at TSL 3. DOE has
not, however, identified or analyzed any currently available microwave
ovens that include all such features in the same unit. Furthermore, DOE
is aware of several emerging technologies (e.g., television displays
and interior cameras) which would provide additional consumer utility
distinct from existing products. Although DOE research suggests that
the implementation of these emerging technologies would not require a
significant amount of standby power, because microwave ovens that
incorporate them are not yet commercially available, DOE is unable to
verify that products that implemented these technologies along with the
complete set of features that would maintain full consumer utility
could meet the efficiency levels at TSL 3. Accordingly, there is
uncertainty as to whether or not a standard at TSL 3 may stifle
innovation and risk impacting customer utility.
The Secretary concludes that at TSL 3 for microwave ovens, the
benefits of energy savings, positive NPV of consumer benefits, emission
reductions, and the estimated monetary value of the emissions
reductions would be outweighed by the uncertainty of impacts to
customer utility and product innovation and the percentage of consumers
in Product Class 2 that would experience a net LCC cost. Consequently,
the Secretary has concluded that TSL 3 is not economically justified.
DOE then considered TSL 2, which represents efficiency level 2 for
microwave ovens. TSL 2 would save an estimated 0.06 quads of energy, an
amount DOE considers significant. Under TSL 2, the NPV of consumer
benefit would be $0.16 billion using a discount rate of 7 percent, and
$0.35 billion using a discount rate of 3 percent.
The cumulative emissions reductions at TSL 2 are 1.87 Mt of
CO2, 0.85 thousand tons of SO2, 2.88 thousand
tons of NOX, 0.005 tons of Hg, 12.64 thousand tons of
CH4, and 0.02 thousand tons of N2O. The estimated
monetary value of the climate benefits from reduced GHG emissions
(associated with the average SC-GHG at a 3-percent discount rate) at
TSL 2 is $0.10 billion. The estimated monetary value of the health
benefits from reduced SO2 and NOX emissions at
TSL 2 is $0.07 billion using a 7-percent discount rate and $0.17
billion using a 3-percent discount rate.
Using a 7-percent discount rate for consumer benefits and costs,
health benefits from reduced SO2 and NOX
emissions, and the 3-percent discount rate case for climate benefits
from reduced GHG emissions, the estimated total NPV at TSL 2 is $0.34
billion.
[[Page 39955]]
Using a 3-percent discount rate for all benefits and costs, the
estimated total NPV at TSL 2 is $0.62 billion. The estimated total NPV
is provided for additional information; however, DOE primarily relies
upon the NPV of consumer benefits when determining whether a proposed
standard level is economically justified.
At TSL 2, the average LCC impact is a savings of $0.99 for Product
Class 1 and $0.83 for Product Class 2. The simple payback period is 1.3
years for Product Class 1 and 0.8 years for Product Class 2. The
fraction of consumers experiencing a net LCC cost is 5.1 percent for
Product Class 1 and 7.4 percent for Product Class 2.
At TSL 2, the projected change in manufacturer INPV ranges from a
decrease of approximately $37.2 million, which corresponds to a
decrease of approximately 2.6 percent, to no change in INPV. At this
TSL, free cash flow is estimated to decrease by 18.4 percent compared
to the no-new-standards case value in the year before the compliance
year. DOE estimates that industry must invest $46.1 million to comply
with standards set at TSL 2. DOE estimates that approximately 40
percent of Product Class 1 (microwave-only oven and countertop
convection microwave oven) shipments and approximately 64 percent of
Product Class 2 (built-in and over-the-range convection microwave oven)
shipments would meet or exceed the efficiency levels analyzed at TSL 2,
in the no-new-standards case. Manufacturers would be required to
redesign approximately 60 percent of all microwave oven models,
representing 7.3 million annual shipments, to meet the efficiency
levels required at TSL 2.
DOE has determined that the standby power requirements of TSL 2
provide sufficient power budgets for manufacturers to implement the
full complement of features that currently provide consumer utility. In
addition, based on DOE's assessment of the expected standby power
requirements for identified emerging technologies, DOE has concluded
that the standby power levels at TSL 2 do not preclude the
implementation of these technologies or stifle further innovation.
After considering the analysis and weighing the benefits and
burdens, the Secretary has concluded that a standard set at TSL 2 for
microwave ovens would be economically justified. At this TSL, the
average LCC savings for both product classes of microwave ovens is
positive. An estimated 5 percent of Product Class 1 consumers and 7
percent of Product Class 2 consumers would experience a net cost. The
FFC national energy savings are significant and the NPV of consumer
benefits is positive using both a 3-percent and 7-percent discount
rate. Notably, the benefits to consumers vastly outweigh the cost to
manufacturers. At TSL 2, the NPV of consumer benefits, even measured at
the more conservative discount rate of 7 percent, is over four times
higher than the maximum estimated manufacturers' loss in INPV. The
standard levels at TSL 2 are economically justified even without
weighing the estimated monetary value of emissions reductions. When
those emissions reductions are included--representing $0.10 billion in
climate benefits (associated with the average SC-GHG at a 3-percent
discount rate), and $0.17 billion (using a 3-percent discount rate) or
$0.07 billion (using a 7-percent discount rate) in health benefits--the
rationale becomes stronger still.
Accordingly, the Secretary has concluded that TSL 2 would offer the
maximum improvement in efficiency that is technologically feasible and
economically justified and would result in the significant conservation
of energy. Although results are presented here in terms of TSLs, DOE
analyzes and evaluates all possible ELs for each product class in its
analysis. For both Product Class 1 (microwave-only oven and countertop
convection microwave oven) and Product Class 2 (built-in and over-the-
range convection microwave oven), TSL 2 is comprised of the highest
efficiency level below max-tech. The ELs one level below max-tech,
representing the finalized standard levels, result in positive LCC
savings for both classes, reduce the number of consumers experiencing a
net cost, and reduce the decrease in INPV and conversion costs to the
point where DOE has concluded they are economically justified, as
discussed for TSL 2 in the preceding paragraphs.
As stated, DOE conducts the walk-down analysis to determine the TSL
that represents the maximum improvement in energy efficiency that is
technologically feasible and economically justified as required under
EPCA. The walk-down is not a comparative analysis, as a comparative
analysis would result in the maximization of net benefits instead of
energy savings that are technologically feasible and economically
justified, which would be contrary to the statute. 86 FR 70892, 70908.
Therefore, based on the previous considerations, DOE adopts the
energy conservation standards for microwave ovens at TSL 2. The amended
energy conservation standards for microwave ovens, which are expressed
as watts, are shown in Table V.26.
Table V.26--Amended Energy Conservation Standards for Microwave Ovens
------------------------------------------------------------------------
Maximum allowable
Product class average standby
power (watts)
------------------------------------------------------------------------
PC 1: Microwave-Only Ovens and Countertop Convection 0.6
Microwave Ovens.....................................
PC 2: Built-In and Over-the-Range Convection 1.0
Microwave Ovens.....................................
------------------------------------------------------------------------
2. Annualized Benefits and Costs of the Adopted Standards
The benefits and costs of the adopted standards can also be
expressed in terms of annualized values. The annualized net benefit is
(1) the annualized national economic value (expressed in 2020$) of the
benefits from operating products that meet the adopted standards
(consisting primarily of operating cost savings from using less
energy), minus increases in product purchase costs, and (2) the
annualized monetary value of the climate and health benefits.
Table V.27 shows the annualized values for microwave ovens under
TSL 2, expressed in 2021$. The results under the primary estimate are
as follows.
Using a 7-percent discount rate for consumer benefits and costs and
NOX and SO2 reductions, and the 3-percent
discount rate case for GHG social costs, the estimated cost of the
adopted standards for microwave ovens is $4.3 million per year in
increased equipment installed costs, while the estimated annual
benefits are $19.5 million from
[[Page 39956]]
reduced equipment operating costs, $5.2 million in GHG reductions, and
$6.9 million from reduced NOX and SO2 emissions.
In this case, the net benefit amounts to $27.3 million per year.
Using a 3-percent discount rate for all benefits and costs, the
estimated cost of the adopted standards for microwave ovens is $4.3
million per year in increased equipment costs, while the estimated
annual benefits are $23.5 million in reduced operating costs, $5.2
million from GHG reductions, and $9.2 million from reduced
NOX and SO2 emissions. In this case, the net
benefit amounts to $33.5 million per year.
Table V.27--Annualized Benefits and Costs of Adopted Standards (TSL 2) for Microwave Ovens
----------------------------------------------------------------------------------------------------------------
Million 2021$/year
-----------------------------------------------
Low-net- High-net-
Primary benefits benefits
estimate estimate estimate
----------------------------------------------------------------------------------------------------------------
3% discount rate
----------------------------------------------------------------------------------------------------------------
Consumer Operating Cost Savings................................. 23.5 22.2 25.0
Climate Benefits *.............................................. 5.2 5.1 5.4
Health Benefits **.............................................. 9.2 9.0 9.4
-----------------------------------------------
Total Benefits[dagger]...................................... 37.9 36.3 39.8
Consumer Incremental Product Costs [Dagger]..................... 4.3 4.4 4.1
-----------------------------------------------
Net Benefits................................................ 33.5 31.9 35.7
----------------------------------------------------------------------------------------------------------------
7% discount rate
----------------------------------------------------------------------------------------------------------------
Consumer Operating Cost Savings................................. 19.5 18.6 20.5
Climate Benefits * (3% discount rate)........................... 5.2 5.1 5.4
Health Benefits **.............................................. 6.9 6.7 7.1
-----------------------------------------------
Total Benefits [dagger]..................................... 31.6 30.4 32.9
Consumer Incremental Product Costs [Dagger]..................... 4.3 4.3 4.1
-----------------------------------------------
Net Benefits................................................ 27.3 26.0 28.9
----------------------------------------------------------------------------------------------------------------
Note: This table presents the costs and benefits associated with microwave ovens shipped in 2026-2055. These
results include benefits to consumers which accrue after 2055 from the products shipped in 2026-2055. The
Primary, Low Net Benefits, and High Net Benefits Estimates utilize projections of energy prices from the
AEO2022 Reference case, Low Economic Growth case, and High Economic Growth case, respectively. In addition,
incremental equipment costs reflect a medium decline rate in the Primary Estimate, a low decline rate in the
Low Net Benefits Estimate, and a high decline rate in the High Net Benefits Estimate. The methods used to
derive projected price trends are explained in sections IV.F.1 and IV.H.1 of this document. Note that the
Benefits and Costs may not sum to the Net Benefits due to rounding.
* Climate benefits are calculated using four different estimates of the global SC-GHG (see section IV.L of this
document). For presentational purposes of this table, the climate benefits associated with the average SC-GHG
at a 3-percent discount rate are shown, but the Department does not have a single central SC-GHG point
estimate, and it emphasizes the importance and value of considering the benefits calculated using all four
sets of SC-GHG estimates. On March 16, 2022, the Fifth Circuit Court of Appeals (No. 22-30087) granted the
Federal government's emergency motion for stay pending appeal of the February 11, 2022, preliminary injunction
issued in Louisiana v. Biden, No. 21-cv-1074-JDC-KK (W.D. La.). As a result of the Fifth Circuit's order, the
preliminary injunction is no longer in effect, pending resolution of the Federal government's appeal of that
injunction or a further court order. Among other things, the preliminary injunction enjoined the defendants in
that case from ``adopting, employing, treating as binding, or relying upon'' the interim estimates of the
social cost of greenhouse gases--which were issued by the Interagency Working Group on the Social Cost of
Greenhouse Gases on February 26, 2021--to monetize the benefits of reducing greenhouse gas emissions. As
reflected in this rule, DOE has reverted to its approach prior to the injunction and presents monetized
benefits where appropriate and permissible under law.
** Health benefits are calculated using benefit-per-ton values for NOX and SO2. DOE is currently only monetizing
(for SO2 and NOX) PM2.5 precursor health benefits and (for NOX) ozone precursor health benefits, but will
continue to assess the ability to monetize other effects such as health benefits from reductions in direct
PM2.5 emissions. See section IV.L of this document for more details.
[dagger] Total benefits for both the 3-percent and 7-percent cases are presented using the average SC-GHG with 3-
percent discount rate, but the Department does not have a single central SC-GHG point estimate.
[Dagger] Costs include incremental equipment costs as well as installation costs.
VI. Procedural Issues and Regulatory Review
A. Review Under Executive Orders 12866, 13563, and 14094
Executive Order (``E.O.'') 12866, ``Regulatory Planning and
Review,'' 58 FR 51735 (Oct. 4, 1993), as supplemented and reaffirmed by
E.O. 13563, ``Improving Regulation and Regulatory Review, 76 FR 3821
(Jan. 21, 2011) and E.O. 14094, ``Modernizing Regulatory Review,'' 88
FR 21879 (April 11, 2023), requires agencies, to the extent permitted
by law, to (1) propose or adopt a regulation only upon a reasoned
determination that its benefits justify its costs (recognizing that
some benefits and costs are difficult to quantify); (2) tailor
regulations to impose the least burden on society, consistent with
obtaining regulatory objectives, taking into account, among other
things, and to the extent practicable, the costs of cumulative
regulations; (3) select, in choosing among alternative regulatory
approaches, those approaches that maximize net benefits (including
potential economic, environmental, public health and safety, and other
advantages; distributive impacts; and equity); (4) to the extent
feasible, specify performance objectives, rather than specifying the
behavior or manner of compliance that regulated entities must adopt;
and (5) identify and assess available alternatives to direct
regulation, including providing economic incentives to encourage the
desired behavior, such as user fees or marketable permits, or providing
information upon which choices can be made by the public. DOE
emphasizes as well that E.O. 13563 requires agencies to
[[Page 39957]]
use the best available techniques to quantify anticipated present and
future benefits and costs as accurately as possible. In its guidance,
the Office of Information and Regulatory Affairs (``OIRA'') in the
Office of Management and Budget (``OMB'') has emphasized that such
techniques may include identifying changing future compliance costs
that might result from technological innovation or anticipated
behavioral changes. For the reasons stated in this preamble, this final
regulatory action is consistent with these principles.
Section 6(a) of E.O. 12866 also requires agencies to submit
``significant regulatory actions'' to OIRA for review. OIRA has
determined that this final rule does not constitute a ``significant
regulatory action'' under section 3(f) of E.O. 12866. Accordingly, this
action was not submitted to OIRA for review under E.O. 12866.
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'')
and a final regulatory flexibility analysis (``FRFA'') for any rule
that by law must be proposed for public comment, unless the agency
certifies that the rule, if promulgated, will not have a significant
economic impact on a substantial number of small entities. As required
by E.O. 13272, ``Proper Consideration of Small Entities in Agency
Rulemaking,'' 67 FR 53461 (Aug. 16, 2002), DOE published procedures and
policies on February 19, 2003, to ensure that the potential impacts of
its rules on small entities are properly considered during the
rulemaking process. 68 FR 7990. DOE has made its procedures and
policies available on the Office of the General Counsel's website
(www.energy.gov/gc/office-general-counsel).
DOE reviewed this final rule under the provisions of the Regulatory
Flexibility Act and the procedures and policies published on February
19, 2003. DOE certifies that this final rule would not have a
significant economic impact on a substantial number of small entities.
The factual basis of this certification is set forth in the following
paragraphs.
For manufacturers of microwave ovens, the SBA has set a size
threshold, which defines those entities classified as ``small
businesses'' for the purposes of the statute. DOE used the SBA's small
business size standards to determine whether any small entities would
be subject to the requirements of the rule. (See 13 CFR part 121.) The
size standards are listed by NAICS code and industry description and
are available at www.sba.gov/document/support-table-size-standards.
Manufacturing microwave ovens is classified under NAICS 335220, ``Major
Household Appliance Manufacturing.'' The SBA sets a threshold of 1,500
employees or fewer for an entity to be considered as a small business
for this category.
DOE identified manufacturers using DOE's CCD,\62\ the California
Energy Commission's Modernized Appliance Efficiency Database System
(``MAEDbS''),\63\ and prior microwave oven rulemakings. DOE used the
publicly available information and subscription-based market research
tools (e.g., reports from DB Hoovers \64\) to identify 37 companies
that sell microwave ovens covered by this rulemaking in the United
States. Of these 37 companies that sell microwave ovens in the United
States, 19 are private labelers. These private labelers out-source the
manufacturing of the microwave ovens to other companies. Therefore, DOE
estimates there are 18 original equipment manufacturers (``OEMs'') that
manufacture microwave ovens covered by this rulemaking. Of the 18 OEMs,
DOE was not able to identify any OEMs of microwave ovens covered by
this rulemaking with fewer than 1,500 total employees (including parent
companies and subsidiaries), and that are domestically located.
Therefore, DOE did not identify any companies that meet SBA's
definition of a ``small business.''
---------------------------------------------------------------------------
\62\ DOE's Compliance Certification Database is available at
www.regulations.doe.gov/ccms (last accessed January 11, 2023).
\63\ California Energy Commission's MAEDbS is available at
cacertappliances.energy.ca.gov/Login.aspx (last accessed January 11,
2023).
\64\ D&B Hoovers reports can be accessed at: app.dnbhoovers.com.
---------------------------------------------------------------------------
DOE did not receive any comments on the August 2022 SNOPR, which
stated that there were not any small businesses that manufactured
microwave ovens sold in the United States. Therefore, DOE concludes and
certifies that this final rule would not have a significant economic
impact on a substantial number of small entities and has not prepared a
FRFA for this rulemaking.
C. Review Under the Paperwork Reduction Act
Manufacturers of microwave ovens must certify to DOE that their
products comply with any applicable energy conservation standards. In
certifying compliance, manufacturers must test their products according
to the DOE test procedures for microwave ovens, including any
amendments adopted for those test procedures. DOE has established
regulations for the certification and recordkeeping requirements for
all covered consumer products and commercial equipment, including
microwave ovens. (See generally 10 CFR part 429). The collection-of-
information requirement for the certification and recordkeeping is
subject to review and approval by OMB under the Paperwork Reduction Act
(``PRA''). This requirement has been approved by OMB under OMB control
number 1910-1400. Public reporting burden for the certification is
estimated to average 35 hours per response, including the time for
reviewing instructions, searching existing data sources, gathering and
maintaining the data needed, and completing and reviewing the
collection of information.
Notwithstanding any other provision of the law, no person is
required to respond to, nor shall any person be subject to a penalty
for failure to comply with, a collection of information subject to the
requirements of the PRA, unless that collection of information displays
a currently valid OMB Control Number.
D. Review Under the National Environmental Policy Act of 1969
Pursuant to the National Environmental Policy Act of 1969
(``NEPA''), DOE has analyzed this proposed action rule in accordance
with NEPA and DOE's NEPA implementing regulations (10 CFR part 1021).
DOE has determined that this rule qualifies for categorical exclusion
under 10 CFR part 1021, subpart D, appendix B5.1 because it is a
rulemaking that establishes energy conservation standards for consumer
products or industrial equipment, none of the exceptions identified in
B5.1(b) apply, no extraordinary circumstances exist that require
further environmental analysis, and it meets the requirements for
application of a categorical exclusion. See 10 CFR 1021.410. Therefore,
DOE has determined that promulgation of this rule is not a major
Federal action significantly affecting the quality of the human
environment within the meaning of NEPA, and does not require an
environmental assessment or an environmental impact statement.
E. Review Under Executive Order 13132
E.O. 13132, ``Federalism,'' 64 FR 43255 (Aug. 10, 1999), imposes
certain requirements on Federal agencies formulating and implementing
policies or regulations that preempt State law or that have federalism
implications. The Executive order requires agencies to examine the
constitutional and statutory authority supporting any action that
[[Page 39958]]
would limit the policymaking discretion of the States and to carefully
assess the necessity for such actions. The Executive order also
requires agencies to have an accountable process to ensure meaningful
and timely input by State and local officials in the development of
regulatory policies that have federalism implications. On March 14,
2000, DOE published a statement of policy describing the
intergovernmental consultation process it will follow in the
development of such regulations. 65 FR 13735. DOE has examined this
rule and has determined that it would not have a substantial direct
effect on the States, on the relationship between the national
government and the States, or on the distribution of power and
responsibilities among the various levels of government. EPCA governs
and prescribes Federal preemption of State regulations as to energy
conservation for the products that are the subject of this final rule.
States can petition DOE for exemption from such preemption to the
extent, and based on criteria, set forth in EPCA. (42 U.S.C. 6297)
Therefore, no further action is required by Executive Order 13132.
F. Review Under Executive Order 12988
With respect to the review of existing regulations and the
promulgation of new regulations, section 3(a) of E.O. 12988, ``Civil
Justice Reform,'' imposes on Federal agencies the general duty to
adhere to the following requirements: (1) eliminate drafting errors and
ambiguity, (2) write regulations to minimize litigation, (3) provide a
clear legal standard for affected conduct rather than a general
standard, and (4) promote simplification and burden reduction. 61 FR
4729 (Feb. 7, 1996). Regarding the review required by section 3(a) and
section 3(b) of E.O. 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 E.O. 12988 requires executive
agencies to review regulations in light of applicable standards in
section 3(a) and section 3(b) to determine whether they are met or it
is unreasonable to meet one or more of them. DOE has completed the
required review and determined that, to the extent permitted by law,
this final rule meets the relevant standards of E.O. 12988.
G. Review Under the Unfunded Mandates Reform Act of 1995
Title II of the Unfunded Mandates Reform Act of 1995 (``UMRA'')
requires each Federal agency to assess the effects of Federal
regulatory actions on State, local, and Tribal governments and the
private sector. Public Law 104-4, Sec. 201 (codified at 2 U.S.C. 1531).
For a regulatory action likely to result in a rule that may cause the
expenditure by State, local, and Tribal governments, in the aggregate,
or by the private sector of $100 million or more in any one year
(adjusted annually for inflation), section 202 of UMRA requires a
Federal agency to publish a written statement that estimates the
resulting costs, benefits, and other effects on the national economy.
(2 U.S.C. 1532(a), (b)) The UMRA also requires a Federal agency to
develop an effective process to permit timely input by elected officers
of State, local, and Tribal governments on a ``significant
intergovernmental mandate,'' and requires an agency plan for giving
notice and opportunity for timely input to potentially affected small
governments before establishing any requirements that might
significantly or uniquely affect them. On March 18, 1997, DOE published
a statement of policy on its process for intergovernmental consultation
under UMRA. 62 FR 12820. DOE's policy statement is also available at
www.energy.gov/sites/prod/files/gcprod/documents/umra_97.pdf.
DOE has concluded that this final rule may require expenditures of
$100 million or more in any one year by the private sector. Such
expenditures may include (1) investment in research and development and
in capital expenditures by microwave ovens manufacturers in the years
between the final rule and the compliance date for the new standards
and (2) incremental additional expenditures by consumers to purchase
higher-efficiency microwave ovens, starting at the compliance date for
the applicable standard.
Section 202 of UMRA authorizes a Federal agency to respond to the
content requirements of UMRA in any other statement or analysis that
accompanies the final rule. (2 U.S.C. 1532(c)) The content requirements
of section 202(b) of UMRA relevant to a private sector mandate
substantially overlap the economic analysis requirements that apply
under section 325(o) of EPCA and Executive Order 12866. The
SUPPLEMENTARY INFORMATION section and the TSD for this final rule
respond to those requirements.
Under section 205 of UMRA, the Department is obligated to identify
and consider a reasonable number of regulatory alternatives before
promulgating a rule for which a written statement under section 202 is
required. (2 U.S.C. 1535(a)) DOE is required to select from those
alternatives the most cost-effective and least burdensome alternative
that achieves the objectives of the rule unless DOE publishes an
explanation for doing otherwise, or the selection of such an
alternative is inconsistent with law. In accordance with 42 U.S.C.
6295(m), this final rule establishes amended energy conservation
standards for microwave ovens that are designed to achieve the maximum
improvement in energy efficiency that DOE has determined to be both
technologically feasible and economically justified, as required by
6295(o)(2)(A) and 6295(o)(3)(B). A full discussion of the alternatives
considered by DOE is presented in chapter 17 of the TSD for this final
rule.
H. Review Under the Treasury and General Government Appropriations Act,
1999
Section 654 of the Treasury and General Government Appropriations
Act, 1999 (Pub. L. 105-277) requires Federal agencies to issue a Family
Policymaking Assessment for any rule that may affect family well-being.
This rule would not have any impact on the autonomy or integrity of the
family as an institution. Accordingly, DOE has concluded that it is not
necessary to prepare a Family Policymaking Assessment.
I. Review Under Executive Order 12630
Pursuant to E.O. 12630, ``Governmental Actions and Interference
with Constitutionally Protected Property Rights,'' 53 FR 8859 (March
18, 1988), DOE has determined that this rule would not result in any
takings that might require compensation under the Fifth Amendment to
the U.S. Constitution.
J. Review Under the Treasury and General Government Appropriations Act,
2001
Section 515 of the Treasury and General Government Appropriations
Act, 2001 (44 U.S.C. 3516, note) provides for Federal agencies to
review most disseminations of information to the public under
information quality guidelines established by each agency pursuant to
general guidelines issued by OMB. OMB's guidelines were published
[[Page 39959]]
at 67 FR 8452 (Feb. 22, 2002), and DOE's guidelines were published at
67 FR 62446 (Oct. 7, 2002). Pursuant to OMB Memorandum M-19-15,
Improving Implementation of the Information Quality Act (April 24,
2019), DOE published updated guidelines which are available at
www.energy.gov/sites/prod/files/2019/12/f70/DOE%20Final%20Updated%20IQA%20Guidelines%20Dec%202019.pdf. DOE has
reviewed this final rule under the OMB and DOE guidelines and has
concluded that it is consistent with applicable policies in those
guidelines.
K. Review Under Executive Order 13211
E.O. 13211, ``Actions Concerning Regulations That Significantly
Affect Energy Supply, Distribution, or Use,'' 66 FR 28355 (May 22,
2001), requires Federal agencies to prepare and submit to OIRA at OMB,
a Statement of Energy Effects for any significant energy action. A
``significant energy action'' is defined as any action by an agency
that promulgates or is expected to lead to promulgation of a final
rule, and that (1) is a significant regulatory action under Executive
Order 12866, or any successor order; and (2) is likely to have a
significant adverse effect on the supply, distribution, or use of
energy, or (3) is designated by the Administrator of OIRA as a
significant energy action. For any significant energy action, the
agency must give a detailed statement of any adverse effects on energy
supply, distribution, or use should the proposal be implemented, and of
reasonable alternatives to the action and their expected benefits on
energy supply, distribution, and use.
DOE has concluded that this regulatory action, which sets forth
amended energy conservation standards for microwave ovens, is not a
significant energy action because the standards are not likely to have
a significant adverse effect on the supply, distribution, or use of
energy, nor has it been designated as such by the Administrator at
OIRA. Accordingly, DOE has not prepared a Statement of Energy Effects
on this final rule.
L. Information Quality
On December 16, 2004, OMB, in consultation with the Office of
Science and Technology Policy (``OSTP''), issued its Final Information
Quality Bulletin for Peer Review (``the Bulletin''). 70 FR 2664 (Jan.
14, 2005). The Bulletin establishes that certain scientific information
shall be peer reviewed by qualified specialists before it is
disseminated by the Federal Government, including influential
scientific information related to agency regulatory actions. The
purpose of the Bulletin is to enhance the quality and credibility of
the Government's scientific information. Under the Bulletin, the energy
conservation standards rulemaking analyses are ``influential scientific
information,'' which the Bulletin defines as ``scientific information
the agency reasonably can determine will have, or does have, a clear
and substantial impact on important public policies or private sector
decisions.'' 70 FR 2664, 2667.
In response to OMB's Bulletin, DOE conducted formal peer reviews of
the energy conservation standards development process and the analyses
that are typically used and prepared a report describing that peer
review.\65\ Generation of this report involved a rigorous, formal, and
documented evaluation using objective criteria and qualified and
independent reviewers to make a judgment as to the technical/
scientific/business merit, the actual or anticipated results, and the
productivity and management effectiveness of programs and/or projects.
Because available data, models, and technological understanding have
changed since 2007, DOE has engaged with the National Academy of
Sciences to review DOE's analytical methodologies to ascertain whether
modifications are needed to improve DOE's analyses. DOE is in the
process of evaluating the resulting report.\66\
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\65\ The 2007 ``Energy Conservation Standards Rulemaking Peer
Review Report'' is available at energy.gov/eere/buildings/downloads/energy-conservation-standards-rulemaking-peer-review-report-0 (Last
accessed January 23, 2023).
\66\ The report is available at www.nationalacademies.org/our-work/review-of-methods-for-setting-building-and-equipment-performance-standards.
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M. Congressional Notification
As required by 5 U.S.C. 801, DOE will report to Congress on the
promulgation of this rule prior to its effective date. The report will
state that it has been determined that the rule is not a ``major rule''
as defined by 5 U.S.C. 804(2).
VII. Approval of the Office of the Secretary
The Secretary of Energy has approved publication of this final
rule.
List of Subjects in 10 CFR Part 430
Administrative practice and procedure, Confidential business
information, Energy conservation, Household appliances, Imports,
Intergovernmental relations, Reporting and recordkeeping requirements,
and Small businesses.
Signing Authority
This document of the Department of Energy was signed on April 20,
2023, by Francisco Alejandro Moreno, Acting Assistant Secretary for
Energy Efficiency and Renewable Energy, pursuant to delegated authority
from the Secretary of Energy. That document with the original signature
and date is maintained by DOE. For administrative purposes only, and in
compliance with requirements of the Office of the Federal Register, the
undersigned DOE Federal Register Liaison Officer has been authorized to
sign and submit the document in electronic format for publication, as
an official document of the Department of Energy. This administrative
process in no way alters the legal effect of this document upon
publication in the Federal Register.
Signed in Washington, DC, on June 13, 2023.
Treena V. Garrett,
Federal Register Liaison Officer, U.S. Department of Energy.
For the reasons set forth in the preamble, DOE amends part 430 of
chapter II, subchapter D, of title 10 of the Code of Federal
Regulations, as set forth below:
PART 430--ENERGY CONSERVATION PROGRAM FOR CONSUMER PRODUCTS
0
1. The authority citation for part 430 continues to read as follows:
Authority: 42 U.S.C. 6291-6309; 28 U.S.C. 2461 note.
0
2. Section 430.32 is amended by revising paragraph (j)(3) to read as
follows:
Sec. 430.32 Energy and water conservation standards and their
compliance dates.
* * * * *
(j) * * *
(3) Microwave ovens:
(i) Microwave-only ovens and countertop convection microwave ovens
manufactured on or after June 17, 2016, and before June 22, 2026, shall
have an average standby power not more than 1.0 watt. Built-in and
over-the-range convection microwave ovens manufactured on or after June
17, 2016, and before June 22, 2026, shall have an average standby power
not more than 2.2 watts.
(ii) Microwave-only ovens and countertop convection microwave ovens
manufactured on or after June 22, 2026, shall have an average standby
power not more than 0.6 watts. Built-in and over-the-range convection
microwave ovens manufactured on or after June 22, 2026,
[[Page 39960]]
shall have an average standby power not more than 1.0 watt.
* * * * *
Note: The following letter will not appear in the Code of
Federal Regulations.
U.S. Department of Justice
Antitrust Division
Jonathan S. Kanter
Assistant Attorney General
Main Justice Building
950 Pennsylvania Avenue NW
Washington, DC 20530-0001
(202) 514-2401/(202) 616-2645 (Fax)
XXXX XX, 2023
Ami Grace-Tardy
Assistant General Counsel for Legislation, Regulation and Energy
Efficiency
U.S. Department of Energy
Washington, DC 20585
[email protected]
Dear Assistant General Counsel Grace-Tardy:
I am responding to your August 25, 2022 letter seeking the views of
the Attorney General about the potential impact on competition of
proposed energy conservation standards for microwave ovens. Your
request was submitted under Section 325(o)(2)(B)(i)(V) of the Energy
Policy and Conservation Act, as amended (EPCA), 42 U.S.C.
6295(o)(2)(B)(i)(V) and 42 U.S.C. 6316(a), 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 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). The Assistant
Attorney General for the Antitrust Division has authorized me, as the
Policy Director the Antitrust Division, to provide the Antitrust
Division's views regarding the potential impact on competition of
proposed energy conservation standards on his behalf.
In conducting its analysis, the Antitrust Division examines whether
a proposed standard may lessen competition, for example, by
substantially limiting consumer choice or increasing industry
concentration. A lessening of competition could result in higher prices
to manufacturers and consumers. We have reviewed the proposed standards
contained in the Supplemental Notice of Proposed Rulemaking (87 FR
52282 August 24, 2022), and the related technical support documents. We
also reviewed the transcript from the public meeting held on October
11, 2022, and reviewed public comments submitted by industry members in
response to DOE's Request for Information in this matter.
Based on the information currently available, we do not believe
that the proposed energy conservation standards for microwave ovens are
likely to have a significant adverse impact on competition.
Sincerely,
David G.B. Lawrence,
Policy Director.
[FR Doc. 2023-12958 Filed 6-16-23; 8:45 am]
BILLING CODE 6450-01-P