Energy Conservation Program: Energy Conservation Standards for Fluorescent Lamp Ballasts, 70548-70629 [2011-28451]
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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
FOR FURTHER INFORMATION CONTACT:
DEPARTMENT OF ENERGY
10 CFR Part 430
[Docket Number EE–2007–BT–STD–0016]
RIN 1904–AB50
Energy Conservation Program: Energy
Conservation Standards for
Fluorescent Lamp Ballasts
Office of Energy Efficiency and
Renewable Energy, Department of
Energy.
ACTION: Final rule.
AGENCY:
The Energy Policy and
Conservation Act of 1975 (EPCA), as
amended, prescribes energy
conservation standards for various
consumer products and certain
commercial and industrial equipment,
including fluorescent lamp ballasts.
EPCA also requires the U.S. Department
of Energy (DOE) to determine whether
any new or amended standards would
be technologically feasible and
economically justified, and would save
a significant amount of energy. In this
final rule, DOE adopts new and
amended federal energy conservation
standards for fluorescent lamp ballasts.
It has determined that the new and
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
January 13, 2012. Compliance with the
new and amended standards established
for fluorescent lamp ballasts in today’s
final rule is required as of November 14,
2014.
ADDRESSES: The docket for this
rulemaking is available for review at
https://www.regulations.gov, including
Federal Register notices, framework
documents, public meeting attendee
lists and transcripts, comments, and
other supporting documents/materials.
All documents in the docket are listed
in the https://www.regulations.gov index.
However, not all documents listed in
the index may be publicly available,
such as information that is exempt from
public disclosure.
A link to the docket Web page can be
found at: https://www1.eere.energy.gov/
buildings/appliance_standards/
residential/fluorescent_lamp_
ballasts.html. The regulations.gov 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 Ms. Brenda
Edwards at (202) 586–2945 or by email:
Brenda.Edwards@ee.doe.gov.
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SUMMARY:
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Dr. Tina Kaarsberg, U.S. Department of
Energy, Office of Energy Efficiency
and Renewable Energy, Building
Technologies Program, EE–2J, 1000
Independence Avenue SW.,
Washington, DC 20585–0121.
Telephone: (202) 287–1393. Email:
Tina.Kaarsberg@ee.doe.gov.
Ms. Elizabeth Kohl, U.S. Department of
Energy, Office of the General Counsel,
GC–71, 1000 Independence Avenue
SW., Washington, DC 20585–0121.
Telephone: (202) 586–7796. Email:
Elizabeth.Kohl@hq.doe.gov.
SUPPLEMENTARY INFORMATION:
I. Summary of the Final Rule
A. Benefits and Costs to Consumers
B. Impact on Manufacturers
C. National Benefits
D. Conclusion
II. Introduction
A. Authority
B. Background
1. Ballast Efficacy Factor Standards
2. History of Standards Rulemaking for
Fluorescent Lamp Ballasts
III. Issues Affecting the Scope of This
Rulemaking
A. Additional Fluorescent Lamp Ballasts
for Which DOE Is Adopting Standards
1. Scope of EPCA Requirement That DOE
Consider Standards for Additional
Ballasts
2. Identification of the Additional Ballasts
for Which DOE Establishes Standards
3. Summary of Fluorescent Lamp Ballasts
to Which DOE Extends Coverage
B. Off Mode and Standby Mode Energy
Consumption Standards
IV. General Discussion
A. Test Procedures
1. Background
2. Transfer Function
3. Reference Lamp
4. Total Lamp Arc Power
B. Technological Feasibility
1. General
2. Maximum Technologically Feasible
Levels
C. Energy Savings
1. Determination of Savings
2. Significance of Savings
D. Economic Justification
1. Specific Criteria
2. Rebuttable Presumption
V. Methodology and Discussion
A. Product Classes
1. Residential Ballasts
2. Sign Ballasts
3. Starting Method
4. 8-Foot HO
5. Summary
B. Engineering Analysis
1. NOPR Approach
2. Available Test Data
3. NEMA-Provided and DOE BLE Data
Comparison
4. Accounting for Variation and
Compliance Certification Requirements
5. Efficiency Levels
6. Representative Units
7. Scaling to Product Classes Not Analyzed
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8. Manufacturer Selling Prices
9. Results
C. Markups To Determine Product Price
1. Distribution Channels
2. Estimation of Markups
3. Summary of Markups
D. Energy Use Analysis
E. Life-Cycle Cost and Payback Period
Analyses
1. Product Cost
2. Installation Cost
3. Annual Energy Use
4. Energy Prices
5. Energy Price Projections
6. Replacement and Disposal Costs
7. Product Lifetime
8. Discount Rates
9. Compliance Date of Standards
10. Ballast Purchasing Events
F. National Impact Analysis–National
Energy Savings and Net Present Value
Analysis
1. Shipments
2. Site-to-Source Energy Conversion
G. Consumer Sub-Group Analysis
H. Manufacturer Impact Analysis
1. Product and Capital Conversion Costs
2. Markup Scenarios
3. Other Key GRIM Inputs
4. Other Comments From Interested Parties
5. Manufacturer Interviews
6. Sub-Group Impact Analysis
I. Employment Impact Analysis
J. Utility Impact Analysis
K. Environmental Assessment
L. Monetizing Carbon Dioxide and Other
Emissions Impacts
1. Social Cost of Carbon
2. Valuation of Other Emissions
Reductions
VI. Other Issues for Discussion
A. Proposed Standard Levels in April 2011
NOPR
B. Universal Versus Dedicated Input
Voltage
C. Implementation of Adopted Standard
Levels
VII. Analytical Results and Conclusions
A. Trial Standard Levels
B. Economic Justification and Energy
Savings
1. Economic Impacts on Individual
Consumers
2. Economic Impacts on Manufacturers
3. National Impact Analysis
4. Impact on Utility or Performance of
Products
5. Impact of Any Lessening of Competition
6. Need of the Nation To Conserve Energy
C. Conclusions
1. Trial Standard Level 3B
2. Trial Standard Level 3A
D. Backsliding
VIII. Procedural Issues and Regulatory
Review
A. Review Under Executive Orders 12866
and 13563
B. Review Under the Regulatory Flexibility
Act
1. Statement of the Need for, and
Objectives of, the Rule
2. Summary of and Responses to the
Significant Issues Raised by the Public
Comments, and a Statement of Any
Changes Made as a Result of Such
Comments
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3. Description and Estimated Number of
Small Entities Regulated
4. Description and Estimate of Compliance
Requirements
5. Steps Taken To Minimize Impacts on
Small Entities and Reasons Why Other
Significant Alternatives to Today’s Final
Rule Were Rejected.
C. Review Under the Paperwork Reduction
Act
D. Review Under the National
Environmental Policy Act of 1969
E. Review Under Executive Order 13132
F. Review Under Executive Order 12988
G. Review Under the Unfunded Mandates
Reform Act of 1995
H. Review Under the Treasury and General
Government Appropriations Act, 1999
I. Review Under Executive Order 12630
J. Review Under the Treasury and General
Government Appropriations Act, 2001
K. Review Under Executive Order 13211
L. Review Under the Information Quality
Bulletin for Peer Review
M. Congressional Notification
IX. Approval of the Office of the Secretary
I. Summary of the Final Rule
Title III, Part B1 of the Energy Policy
and Conservation Act of 1975 (EPCA or
the Act), Public Law 94–163 (42 U.S.C.
6291–6309, as codified), established the
Energy Conservation Program for
Consumer Products Other Than
Automobiles. Pursuant to EPCA, any
new or amended energy conservation
standard that DOE prescribes for certain
products, such as fluorescent lamp
ballasts (ballasts), shall be designed to
achieve the maximum improvement in
energy efficiency that is technologically
feasible and economically justified. (42
70549
U.S.C. 6295(o)(2)(A)) Furthermore, the
new or amended standard must result in
a significant conservation of energy. (42
U.S.C. 6295(o)(3)(B)) In accordance with
these and other statutory provisions
discussed in this notice, DOE adopts
new and amended energy conservation
standards for ballasts. The new and
amended standards, which are based on
ballast luminous efficiency (BLE), the
ratio of total lamp arc power to ballast
input power as defined in Appendix Q1
of title 10 of the Code of Federal
Regulations (CFR), part 430, are shown
in Table I.1. These new and amended
standards apply to all products listed in
Table I.1 and manufactured in, or
imported into, the United States on or
after the compliance date specified in
the DATES section.
TABLE I.1—NEW AND AMENDED ENERGY CONSERVATION STANDARDS FOR FLUORESCENT LAMP BALLASTS
Fluorescent lamp ballasts * shall have a ballast luminous efficiency no less than A/(1 + B * total lamp arc power∧-C) where A,
B, and C are as follow:
Product Class
A
Instant start and rapid start ballasts (not classified as residential) that
are designed to operate .......................................................................
4-foot medium bipin lamps
2-foot U-shaped lamps
8-foot slimline lamps
Programmed start ballasts (not classified as residential) that are designed to operate .................................................................................
4-foot medium bipin lamps
2-foot U-shaped lamps
4-foot miniature bipin standard output lamps
4-foot miniature bipin high output lamps
Instant start and rapid start ballasts (not classified as sign ballasts)
that are designed to operate 8-foot high output lamps .......................
Programmed start ballasts (not classified as sign ballasts) that are designed to operate 8-foot high output lamps .........................................
Sign ballasts that operate 8-foot high output lamps ...............................
Instant start and rapid start residential ballasts that operate ..................
4-foot medium bipin lamps
2-foot U-shaped lamps
8-foot slimline lamps
Programmed start residential ballasts that are designed to operate ......
4-foot medium bipin lamps
2-foot U-shaped lamps
B
C
Percent
improvement
over current
standard or
baseline **
0.993
0.27
0.25
5.7
0.993
0.51
0.37
10.8
0.993
0.38
0.25
26.5
0.973
0.993
0.993
0.70
0.47
0.41
0.37
0.25
0.25
26.2
15.1
7.2
0.973
0.71
0.37
5.8
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* Fluorescent ballasts that are exempt from these standards are listed in section III.A.3.
** Percent improvement is applicable to the average of ballasts directly analyzed.
A. Benefits and Costs to Consumers
Table I.2 presents DOE’s evaluation of
the economic impacts of today’s
standards on consumers of ballasts for
the product classes analyzed as
representative (see section V.B.6), as
measured by the average life-cycle cost
(LCC) savings and the median payback
period (PBP). The average LCC savings
are positive for all product classes. For
example, the estimated average LCC
savings are $37¥$40 for 2-lamp instant
start (IS) and rapid start (RS) ballasts
that operate 4-foot T8 2 lamps in the
commercial sector. When there was
more than one baseline for a
representative ballast type, DOE
performed separate LCC analyses
comparing replacement lamp-andballast systems to each baseline.
1 For editorial reasons, upon codification in the
U.S. Code, Part B was redesignated Part A.
2 A lamp description in the form ‘‘T8’’ refers to
a lamp that (1) is tubular (linear) and (2) has a
diameter of 8 eighths of an inch (1 inch).
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Because T8 systems are generally more
efficient and have lower overall LCCs
than T12 systems, the LCC savings
relative to the T8 baseline are lower
than when comparing the same
efficiency levels to a T12 baseline. At
the adopted standard levels, however,
LCC savings are positive for all
replacement events and baselines
analyzed.
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TABLE I.2—IMPACTS OF TODAY’S STANDARDS ON CONSUMERS OF BALLASTS
Average LCC savings
(2010$)
Product Class *
IS and RS ballasts (not classified as residential) that operate:
4-foot MBP lamps (T12 baseline) ............................................................................................
4-foot MBP lamps (T8 baseline) ..............................................................................................
8-foot slimline lamps (T12 baseline) ........................................................................................
8-foot slimline lamps (T8 baseline) ..........................................................................................
PS ballasts (not classified as residential) that operate:
4-foot MBP lamps .....................................................................................................................
4-foot MiniBP SO lamps ...........................................................................................................
4-foot MiniBP HO lamps ...........................................................................................................
IS and RS ballasts (not classified as sign ballasts) that operate:
8-foot HO lamps (T12 baseline) ...............................................................................................
Sign ballasts that operate:
8-foot HO lamps .......................................................................................................................
IS and RS residential ballasts that operate:
4-foot MBP lamps .....................................................................................................................
Median payback
period
(years) *
$37 to $40 .................
$3 to $8 .....................
$22 to $33 .................
$5 to $7 .....................
¥1.2 to ¥1.3.
2.7 to 4.4.
0.1.
0.5 to 0.6.
$6 to $35 ...................
$10 to $19 .................
$26 to $28 .................
1.3 to 6.0.
2.4 to 3.8.
2.0 to 2.1.
$134 to $230 .............
¥0.7 to ¥1.3.
$251 to $403 .............
¥0.2 to ¥0.3.
$15 to $21 .................
¥5.5 to ¥9.5.
*IS = instant start; RS = rapid start; MBP = medium bipin; MiniBP = miniature bipin; PS = programmed start;
SO = standard output; HO = high output.
**Negative PBP values indicate standards that reduce operating costs and installed costs.
C. National Benefits
DOE’s analyses indicate that today’s
ballast standards would save a
significant amount of energy over 30
years (2014–2043)—an estimated 2.7–
5.6 quadrillion British thermal units
(quads) of cumulative energy. This
amount is equivalent to the annual
energy use of 14 million to 28 million
U.S. homes.4
The cumulative national net present
value (NPV) of total consumer costs and
savings of today’s ballast standards in
2010$ ranges from $6.7 billion (at a
7-percent discount rate) to $21.6 billion
(at a 3-percent discount rate). This NPV
expresses the estimated total value of
future operating-cost savings less the
estimated increased product costs for
products purchased in 2014–2043,
discounted to 2011.
In addition, today’s ballast standards
would have significant environmental
benefits. The energy savings would
result in cumulative greenhouse gas
emission reductions of 27–106 million
metric tons (Mt) of carbon dioxide (CO2)
from 2014 through 2043. During this
period, the standards would also result
in emissions reductions 5 of 22–39
thousand tons of nitrogen oxides (NOX)
and 0.40–1.47 tons of mercury (Hg).6
The value of the CO2 reductions is
calculated using a range of values per
metric ton of CO2 (otherwise known as
the Social Cost of Carbon, or SCC)
developed by a recent interagency
process. The derivation of the SCC
values is discussed in section V.L. DOE
estimates that the net present monetary
value of the CO2 emissions reductions is
between $0.26 and $3.94 billion,
expressed in 2010$ and discounted to
2011. DOE also estimates that the net
present monetary value of the NOX
emissions reductions, expressed in
2010$ and discounted to 2011, is $3.91
to $40.2 million at a 7-percent discount
rate, and $7.67 to $78.8 million at a 3percent discount rate.7
Table I.3 summarizes the national
economic costs and benefits expected to
result from today’s standards for
fluorescent lamp ballasts.
3 For ballasts, DOE uses a real discount rate of 7.4
percent. DOE’s discount rate estimate was derived
from industry financials then modified according to
feedback during manufacturer interviews.
4 This estimate is based on the energy use of
homes in 2008, which is the most recent data
available. See Rosenfeld, Arthur H. and Satish
Kumar. Tables to Convert Energy or CO2 (saved or
used) to Familiar Equivalents—Cars, Homes, or
Power Plants (US Average Data for 2005). May
2008. https://www.energy.ca.gov/commissioners/
rosenfeld_docs/EquivalenceMatrix2008.doc
5 DOE calculates emissions reductions relative to
the most recent version of the Annual Energy
Outlook (AEO) Reference case forecast. As noted in
TSD chapter 16, this forecast accounts for
regulatory emissions reductions through 2008,
including the Clean Air Interstate Rule (CAIR, 70
FR 25162 (May 12, 2005)), but not the Clean Air
Mercury Rule (CAMR, 70 FR 28606 (May 18, 2005)).
Subsequent regulations, including the currently
proposed CAIR replacement rule, the Clean Air
Transport Rule (75 FR 45210 (Aug. 2, 2010)), do not
appear in the forecast.
6 Results for NO and Hg are presented in short
X
tons. One short ton equals 2000 lbs.
7 DOE is aware of multiple agency efforts to
determine the appropriate range of values used in
evaluating the potential economic benefits of
reduced Hg emissions. DOE has decided to await
further guidance regarding consistent valuation and
reporting of Hg emissions before it once again
monetizes Hg emissions reductions in its
rulemakings.
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B. Impact on Manufacturers
The industry net present value (INPV)
is the sum of the discounted cash flows
to the industry from the base year
through the end of the analysis period
(2014 to 2043). Using a real discount
rate of 7.4 3 percent, DOE estimates that
the INPV for manufacturers of ballasts
in the base case ranges from $733
million to $1.22 billion in 2010 dollars
(2010$). Under today’s standards, DOE
expects that ballast manufacturers may
lose up to 36.7 percent of their INPV,
which is approximately $268.6 million.
Based on DOE’s interviews with the
manufacturers of ballasts, however, DOE
does not expect any plant closings or
significant employment loss. See section
VII.B.2.b and VIII.B.3.b for additional
discussion on this topic.
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TABLE I.3—SUMMARY OF NATIONAL ECONOMIC BENEFITS AND COSTS OF FLUORESCENT LAMP BALLAST ENERGY
CONSERVATION STANDARDS
Present value
Billion 2010$
Category
Discount rate
(percent)
Benefits
Operating Cost Savings ...................................................................................................................................
12.0
24.1
0.26
1.29
2.16
3.94
0.004
0.01
0.04
0.08
13.3
25.4
3.68
6.91
NOX Reduction Monetized Value (at $4,623/ton) * .........................................................................................
Total Benefits† .................................................................................................................................................
7
3
9.62
18.5
CO2 Reduction Monetized Value (at $4.9/t) * ..................................................................................................
CO2 Reduction Monetized Value (at $22.3/t) * ................................................................................................
CO2 Reduction Monetized Value (at $36.5/t) * ................................................................................................
CO2 Reduction Monetized Value (at $67.6/t) * ................................................................................................
NOX Reduction Monetized Value (at $450/ton) * ............................................................................................
7
3
5
3
2.5
3
7
3
7
3
7
3
7
3
Costs
Incremental Installed Costs .............................................................................................................................
Net Benefits
Including CO2 and NOX† .................................................................................................................................
* The CO2 values represent global monetized values of the SCC in 2010 under several scenarios. The values of $4.9, $22.3, and $36.5 per
metric ton (t) are the averages of SCC distributions calculated using 5%, 3%, and 2.5% discount rates, respectively. The value of $67.6/t represents the 95th percentile of the SCC distribution calculated using a 3% discount rate.
† Total Benefits for both the 3% and 7% cases are derived using the SCC value calculated at a 3% discount rate, and the average of the low
and high NOX values used in DOE’s analysis.
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The benefits and costs of today’s
standards, for products sold in 2014–
2043, can also be expressed in terms of
annualized values. The annualized
monetary values are the sum of (1) the
annualized national economic value,
expressed in 2010$, of the benefits from
operating the product (consisting
primarily of operating cost savings from
using less energy, minus increases in
equipment purchase and installation
costs, which is another way of
representing consumer NPV, plus (2) the
annualized monetary value of the
benefits of emission reductions,
including CO2 emission reductions.8
Although adding the value of
consumer savings to the values of
emission reductions provides a valuable
perspective, two issues should be
considered. First, the national operating
cost savings are domestic U.S. consumer
monetary savings that occur as a result
of market transactions, while the value
of CO2 emissions reductions is based on
a global value. Second, the assessments
of operating cost savings and CO2
savings are performed with different
methods that use different time frames
for analysis. The national operating cost
savings are measured for the lifetime of
ballasts shipped in 2014–2043. The SCC
values, alternatively, reflect the present
value of all future climate-related
impacts resulting from the emission of
one metric ton of CO2 in each year, with
impacts continuing well beyond 2100.
Estimates of annualized benefits and
costs of today’s standards are shown in
Table I.4. (The following monetary
values are expressed in 2010$.) The
results under the primary estimate are
as follows. Using a 7-percent discount
rate for benefits and costs other than
CO2 reduction, for which DOE used a 3percent discount rate along with the
SCC series corresponding to a value of
$22.3/ton in 2010, the cost of the
standards in today’s rule is $363 million
per year in increased equipment costs,
while the benefits are $1.2 billion per
year in reduced equipment operating
costs, $92 million in CO2 reductions,
and $2.2 million in reduced NOX
emissions. In this case, the net benefit
amounts to $920 million per year. Using
a 3-percent discount rate for all benefits
and costs and the SCC series
corresponding to a value of $22.3/ton in
2010, the cost of the standards in
today’s rule is $385 million per year in
increased equipment costs, while the
benefits are $1.3 billion per year in
reduced operating costs, $92 million in
CO2 reductions, and $2.4 million in
reduced NOX emissions. In this case, the
net benefit amounts to $1.1 billion per
year.
8 DOE used a two-step calculation process to
convert the time-series of costs and benefits into
annualized values. First, DOE calculated a present
value in 2011, the year used for discounting the
NPV of total consumer costs and savings, for the
time-series of costs and benefits using discount
rates of three and seven percent for all costs and
benefits except for the value of CO2 reductions. For
the latter, DOE used a range of discount rates, as
shown in Table I.3. From the present value, DOE
then calculated the fixed annual payment over a 30year period (2014 through 2043) that yields the
same present value. This payment includes benefits
to consumers which accrue after 2043 from the
ballasts purchased from 2014 to 2043. Costs
incurred by manufacturers, some of which may be
incurred prior to 2014 in preparation for the rule,
are not directly included, but are indirectly
included as part of incremental product costs. The
fixed annual payment is the annualized value.
Although DOE calculated annualized values, this
does not imply that the time-series of cost and
benefits from which the annualized values were
determined is a steady stream of payments.
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TABLE I.4—ANNUALIZED BENEFITS AND COSTS OF NEW AND AMENDED STANDARDS FOR BALLASTS SOLD IN 2014–2043*
Monetized
million 2010$/year
Discount rate
Primary estimate
Low estimate
(emerging technologies, roll-up
scenario)
High estimate
(existing technologies,
shift scenario)
Benefits
Operating Cost Savings .................................
Total (Operating Cost Savings, CO2 Reduction and NOX Reduction)†.
1,189 ..........................
1,344 ..........................
20 ...............................
92 ...............................
151 .............................
280 .............................
2.2 ..............................
2.4 ..............................
1,211 to 1,471 ...........
886 ..............................
934 ..............................
9 ..................................
41 ................................
66 ................................
124 ..............................
1.3 ...............................
1.6 ...............................
896 to 1,011 ................
1,492.
1,754.
30.
143.
237.
435.
3.0.
3.2.
1,525 to 1,930.
7% ..............................
3% ..............................
3% plus CO2 range ...
CO2 Reduction at $4.9/t** ..............................
CO2 Reduction at $22.3/t** ............................
CO2 Reduction at $36.5/t** ............................
CO2 Reduction at $67.6/t** ............................
NOX Reduction at $2,537/t** .........................
7% ..............................
3% ..............................
5% ..............................
3% ..............................
2.5% ...........................
3% ..............................
7% ..............................
3% ..............................
7% plus CO2 range ...
1,283 ..........................
1,438 ..........................
1,366 to 1,626 ...........
928 ..............................
976 ..............................
945 to 1,059 ................
1,637.
1,900.
1,788 to 2,193.
227 ..............................
218 ..............................
498.
553.
Costs
Incremental Product Costs ............................
7% ..............................
3% ..............................
363 .............................
385 .............................
Net Benefits/Costs
Total (Operating Cost Savings, CO2 Reduction and NOX Reduction, Minus Incremental Product Costs)†.
7% plus CO2 range ...
848 to 1,108 ..............
669 to 784 ...................
1,027 to 1,432.
7% ..............................
3% ..............................
3% plus CO2 range ...
920 .............................
1,053 ..........................
981 to 1,241 ..............
700 ..............................
758 ..............................
727 to 842 ...................
1,139.
1,347.
1,235 to 1,640.
* This table presents the annualized costs and benefits associated with fluorescent lamp ballasts shipped between 2014 and 2043. These results include benefits to consumers which accrue after 2043 from the ballasts purchased from 2014 to 2043. Costs incurred by manufacturers,
some of which may be incurred prior to 2014 in preparation for the rule, are not directly included, but are indirectly included as part of incremental product costs. The Primary, Low Benefits, and High Benefits Estimates utilize forecasts of energy prices and housing starts from the
AEO2010 Reference case, with the Low and High Estimates based on forecasted ballast shipments in the Emerging Technologies, Roll-up and
Existing Technologies, Shift scenarios, respectively. In addition, all estimates use incremental product costs that reflect constant prices (no learning rate) for product prices. The different techniques used to evaluate projected price trends for each estimate are discussed in section V.E.1.
** The CO2 values represent global monetized values (in 2010$) of the social cost of CO2 emissions in 2010 under several scenarios. The values of $4.9, $22.3, and $36.5 per metric ton are the averages of SCC distributions calculated using 5-percent, 3-percent, and 2.5-percent discount rates, respectively. The value of $67.6/t represents the 95th percentile of the SCC distribution calculated using a 3-percent discount rate.
The value for NOX (in 2010$) is the average of the low and high values used in DOE’s analysis.
† Total Benefits for both the 3-percent and 7-percent cases are derived using the SCC value calculated at a 3-percent discount rate, which is
$22.3/t in 2010 (in 2010$). In the rows labeled as ‘‘7% plus CO2 range’’ and ‘‘3% plus CO2 range,’’ the operating cost and NOX benefits are calculated using the labeled discount rate, and those values are added to the full range of CO2 values.
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D. Conclusion
II. Introduction
Based on the analyses culminating in
this final rule, DOE found the benefits
to the nation of the standards (energy
savings, consumer LCC savings, positive
NPV of consumer benefit, and emission
reductions) outweigh the costs (loss of
INPV). DOE has concluded that the
standards in today’s final rule represent
the maximum improvement in energy
efficiency that is technologically
feasible and economically justified, and
would result in significant conservation
of energy. DOE further notes that in all
product classes, ballasts achieving the
standard levels are already
commercially available.
The following section briefly
discusses the statutory authority
underlying today’s final rule, as well as
some of the historical background
related to the establishment of standards
for ballasts.
A. Authority
Title III, Part B of the Energy Policy
and Conservation Act of 1975, Public
Law 94–163 (42 U.S.C. 6291–6309, as
codified) established the Energy
Conservation Program for Consumer
Products Other Than Automobiles,9 a
program covering most major household
appliances (collectively referred to as
9 For editorial reasons, upon codification in the
U.S. Code (U.S.C.), Part B was redesignated Part A.
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‘‘covered products’’), which includes
the types of ballasts that are the subject
of this final rule. (42 U.S.C. 6292(a)(13))
EPCA prescribed energy conservation
standards for these products (42 U.S.C.
6295(g)(5), (6), and (8)), and directed
DOE to conduct two cycles of
rulemakings to determine whether to
amend these standards. (42 U.S.C.
6295(g)(7))
Pursuant to EPCA, DOE’s energy
conservation program for covered
products consists essentially of four
parts: (1) Testing; (2) labeling; (3) the
establishment of Federal energy
conservation standards; and (4)
certification and enforcement
procedures. The Federal Trade
Commission (FTC) is primarily
responsible for labeling, and DOE
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implements the remainder of the
program. 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. 6293) 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. Id. The DOE
test procedures for ballasts currently
appear at 10 CFR part 430, subpart B,
appendices Q and Q1. Compliance with
the ballast efficacy factor energy
conservation standards, required until
the compliance date specified in the
DATES section, is determined according
to appendix Q. Compliance with the
BLE standards adopted in this rule must
be determined according to appendix
Q1. The procedures in appendix Q1
were established by the ballast active
mode test procedure final rule. 76 FR
25211 (May 4, 2011).
DOE must follow specific statutory
criteria for prescribing new or amended
standards for covered products. As
indicated in the beginning of section I,
any new or amended standard for a
covered product must be designed to
achieve the maximum improvement in
energy efficiency that is technologically
feasible and economically justified. (42
U.S.C. 6295(o)(2)(A)) Furthermore, 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 ballasts, if no test procedure
has been established for the product, or
(2) if DOE determines by rule that the
new or amended standard is not
technologically feasible or economically
justified. (42 U.S.C. 6295(o)(3)(A)–(B))
In deciding whether a new or amended
standard is economically justified, DOE
must determine whether the benefits of
the standard exceed its burdens. (42
U.S.C. 6295(o)(2)(B)(i)) DOE must make
this determination after receiving
comments on the proposed standard,
and by considering, to the greatest
extent practicable, the following seven
factors:
1. The economic impact of the
standard on manufacturers and
consumers of the products subject to the
standard;
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2. The savings in operating costs
throughout the estimated average life of
the covered products in the type (or
class) compared to any increase in the
price, initial charges, or maintenance
expenses for the covered products that
are likely to result from the imposition
of the standard;
3. The total projected amount of
energy, or as applicable, water, savings
likely to result directly from the
imposition of the standard;
4. Any lessening of the utility or the
performance of the covered products
likely to result from the imposition of
the standard;
5. The impact of any lessening of
competition, as determined in writing
by the Attorney General, that is likely to
result from the imposition of the
standard;
6. The need for national energy and
water conservation; and
7. Other factors the Secretary of
Energy (the Secretary) considers
relevant.
(42 U.S.C. 6295(o)(2)(B)(i)(I)–(VII))
EPCA, as codified, also contains what
is known as an ‘‘anti-backsliding’’
provision, which prevents the Secretary
from prescribing any new or amended
standard that either increases the
maximum allowable energy use or
decreases the minimum required energy
efficiency of a covered product. (42
U.S.C. 6295(o)(1)) Also, the Secretary
may not prescribe a new or amended
standard if interested parties 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))
Further, EPCA, as codified,
establishes a rebuttable presumption
that a standard is economically justified
if the Secretary finds that the additional
cost to the consumer of purchasing a
product complying with an energy
conservation standard level will be less
than three times the value of the energy
savings during the first year that the
consumer will receive as a result of the
standard, as calculated under the
applicable test procedure. See 42 U.S.C.
6295(o)(2)(B)(iii).
Additionally, 42 U.S.C. 6295(q)(1)
specifies requirements when
promulgating a standard for a type or
class of covered product that has two or
more subcategories. DOE must specify a
different standard level than that which
applies generally to such type or class
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70553
of products for any group of covered
products which have the same function
or intended use if products within such
group—(A) consume a different kind of
energy from that consumed by other
covered products within such type (or
class); or (B) have a capacity or other
performance-related feature which other
products within such type (or class) do
not have and such feature justifies a
higher or lower standard. Id. In
determining whether a performancerelated feature justifies a different
standard for a group of products, DOE
must consider such factors as the utility
to the consumer of such a feature and
other factors DOE deems appropriate.
Id. Any rule prescribing such a standard
must include an explanation of the basis
on which such higher or lower level was
established. (42 U.S.C. 6295(q)(2))
Federal energy conservation
requirements generally supersede State
laws or regulations concerning energy
conservation testing, labeling, and
standards. (42 U.S.C. 6297(a)–(c)) DOE
may, however, grant waivers of Federal
preemption for particular State laws or
regulations, in accordance with the
procedures and other provisions set
forth under 42 U.S.C. 6297(d).
Pursuant to the amendments
contained in section 310(3) of the
Energy Independence and Security Act
of 2007 (EISA 2007), 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 the 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)) DOE has determined
that ballasts do not operate in an ‘‘off
mode’’ as defined by EPCA (42 U.S.C.
6291(gg)(1)(A)(ii)), and that the only
ballasts that consume power in a
‘‘standby mode’’ as defined by EPCA (42
U.S.C. 6291(gg)(1)(A)(iii)) are those that
incorporate an electronic circuit
enabling the ballast to communicate
with and be part of a lighting control
system. DOE’s test procedures for
ballasts address such standby mode
energy use. 74 FR 54455 (October 22,
2009) and 76 FR 25211 (May 4, 2011);
10 CFR part 430, subpart B, appendix Q,
section 3.2 and appendix Q1, section 3.
DOE did not adopt standards for
standby mode energy use, however,
because DOE did not find any covered
ballasts capable of operating in this
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mode in its search of the marketplace.
Therefore, this final rule does not
include energy conservation standards
for standby mode energy use. See
section III.B for more detail.
DOE has also reviewed this regulation
pursuant to Executive Order 13563,
issued on January 18, 2011 (76 FR 3281,
Jan. 21, 2011). EO 13563 is
supplemental to and explicitly reaffirms
the principles, structures, and
definitions governing regulatory review
established in Executive Order 12866.
To the extent permitted by law, agencies
are required by Executive Order 13563
to: (1) Propose or adopt a regulation
only upon a reasoned determination
that its benefits justify its costs
(recognizing that some benefits and
costs are difficult to quantify); (2) tailor
regulations to impose the least burden
on society, consistent with obtaining
regulatory objectives, taking into
account, among other things, and to the
extent practicable, the costs of
cumulative regulations; (3) select, in
choosing among alternative regulatory
approaches, those approaches that
maximize net benefits (including
potential economic, environmental,
public health and safety, and other
advantages; distributive impacts; and
equity); (4) to the extent feasible, specify
performance objectives, rather than
specifying the behavior or manner of
compliance that regulated entities must
adopt; and (5) identify and assess
available alternatives to direct
regulation, including providing
economic incentives to encourage the
desired behavior, such as user fees or
marketable permits, or providing
information upon which choices can be
made by the public.
DOE emphasizes as well that
Executive Order 13563 requires agencies
‘‘to use the best available techniques to
quantify anticipated present and future
benefits and costs as accurately as
possible.’’ In its guidance, the Office of
Information and Regulatory Affairs has
emphasized that such techniques may
include ‘‘identifying changing future
compliance costs that might result from
technological innovation or anticipated
behavioral changes.’’ For the reasons
stated in the preamble, DOE concludes
that today’s final rule is consistent with
these principles, including the
requirement that, to the extent
permitted by law, benefits justify costs
and that net benefits are maximized.
Consistent with EO 13563, and the
range of impacts analyzed in this final
rule, the energy efficiency standards
adopted herein by DOE achieve
maximum net benefits.
B. Background
1. Ballast Efficacy Factor Standards
The Federal energy conservation
standards for ballasts expressed in terms
of ballast efficacy factor are set forth in
Table II.1 and Table II.2. The standards
in Table II.1 were adopted in a final rule
published on September 19, 2000,
which completed the first of the two
rulemakings required under 42 U.S.C.
6295(g)(7) to consider amending the
standards for ballasts (hereafter referred
to as the 2000 Ballast Rule). 65 FR
56739. The standards in Table II.2 were
established by amendments to EPCA in
the Energy Policy Act of 2005 (EPAct
2005), Pub. L. 109–58.
TABLE II.1—ENERGY CONSERVATION STANDARDS FROM THE 2000 BALLAST RULE
Ballast input
voltage
Application for operation of *
One F40T12 lamp ............................................................................................................
Total nominal
lamp watts
120
277
120
277
120
277
120
277
Two F40T12 lamps ..........................................................................................................
Two F96T12 lamps ..........................................................................................................
Two F96T12HO lamps ....................................................................................................
40
40
80
80
150
150
220
220
Ballast efficacy
factor
2.29
2.29
1.17
1.17
0.63
0.63
0.39
0.39
* F40T12, F96T12, and F96T12HO are defined in Appendix Q to Subpart B of Part 430.
10 CFR 430.32(m)(3).
TABLE II.2—ENERGY CONSERVATION STANDARDS FROM EPACT 2005
Ballast input
voltage
Application for operation of *
One
Two
Two
Two
F34T12 lamp ............................................................................................................
F34T12 lamps ..........................................................................................................
F96T12/ES lamps ....................................................................................................
F96T12HO/ES lamps ...............................................................................................
Total nominal
lamp watts
120/277
120/277
120/277
120/277
34
68
120
190
Ballast efficacy
factor
2.61
1.35
0.77
0.42
* F34T12, F96T12/ES, and F96T12HO/ES are defined in Appendix Q to Subpart B of Part 430.
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(42 U.S.C. 6295(g)(8)(A); 10 CFR
430.32(m)(5))
In summary, as reflected in the
previous two tables, the ballasts
currently regulated under EPCA consist
of ballasts that are designed to operate:
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• One and two nominally 40-watt (W)
and 34W 4-foot T12 medium bipin
(MBP) lamps (F40T12 10 and F34T12);
10 A notation in the form ‘‘F40T12’’ identifies a
lamp type. This particular notation refers to a lamp
that: (1) Is fluorescent; (2) has a nominal wattage of
40 W; (3) is linear (tubular); and (4) has a diameter
of 12 eighths of an inch.
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• Two nominally 75W and 60W 8foot T12 single-pin (SP) slimline lamps
(F96T12 and F96T12/ES); and
• Two nominally 110W and 95W 8foot T12 recessed double contact high
output lamps (F96T12HO and
F96T12HO/ES) at nominal input
voltages of 120 or 277 volts (V) with an
input current frequency of 60 hertz (Hz).
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In addition, several ballasts are
exempt from standards. These
exemptions consist of ballasts designed
to operate those lamps listed in Table
II.1 that:
• Are designed for dimming to 50
percent or less of its maximum output;
• Are designed for use with two
F96T12 high output (HO) lamps at
ambient temperatures of ¥20 degrees
Fahrenheit (F) or less and for use in an
outdoor sign; or
• Have a power factor of less than
0.90 and are designed and labeled for
use only in residential building
applications.
2. History of Standards Rulemaking for
Fluorescent Lamp Ballasts
EPCA establishes energy conservation
standards for certain ballasts and
requires that DOE conduct two cycles of
rulemaking to determine whether to
amend the standards for these ballasts,
including whether to adopt standards
for additional ballasts. (42 U.S.C.
6295(g)(5)–(8)) As indicated in section
II.B.1, DOE completed the first of these
rulemaking cycles by publishing the
2000 Ballast Rule. 65 FR 56740 (Sept.
19, 2000). In this rulemaking, the
second rulemaking cycle required by 42
U.S.C. 6295(g)(7), DOE is amending the
existing standards for ballasts and
adopting standards for additional
ballasts.
DOE initiated this rulemaking on
January 14, 2008 by publishing in the
Federal Register a notice announcing
the availability of the ‘‘Energy
Conservation Standards Rulemaking
Framework Document for Fluorescent
Lamp Ballasts.’’ (A PDF of the
framework document is available at
https://www1.eere.energy.gov/buildings/
appliance_standards/residential/pdfs/
ballast_framework_011408.pdf.) In that
notice, DOE also announced a public
meeting on the framework document
and requested public comment on the
matters raised in the document. 73 FR
3653 (Jan. 22, 2008). The framework
document described the procedural and
analytical approaches that DOE
anticipated using to evaluate energy
conservation standards for the ballasts,
and identified various issues to be
resolved in conducting this rulemaking.
DOE held the public meeting on
February 6, 2008, where it: Presented
the contents of the framework
document; described the analyses it
planned to conduct during the
rulemaking; sought comments from
interested parties on these subjects; and
in general, sought to inform interested
parties about, and facilitate their
involvement in, the rulemaking.
Interested parties at the public meeting
discussed the active mode test
procedure and several major analyses
related to this rulemaking. At the
meeting and during the period for
commenting on the framework
document, DOE received feedback that
helped identify and resolve issues
involved in this rulemaking.
DOE then gathered additional
information and performed preliminary
analyses to help develop potential
energy conservation standards for
ballasts. DOE published in the Federal
Register an announcement of the
availability of the preliminary technical
support document (TSD) and of another
public meeting to discuss and receive
comments on the following matters:
Product classes; the analytical
framework, models, and tools that DOE
was using to evaluate standards; the
results of the preliminary analyses
performed by DOE; and potential
standard levels that DOE could
consider. 75 FR 14319 (March 24, 2010)
(hereafter referred to as the March 2010
notice). DOE also invited written
comments on these subjects. Id. The
preliminary TSD is available at https://
www1.eere.energy.gov/buildings/
appliance_standards/residential/
70555
fluorescent_lamp_ballasts_
ecs_prelim_tsd.html. In the notice, DOE
also requested comment on other
relevant issues that would affect energy
conservation standards for fluorescent
lamp ballasts or that DOE should
address in the notice of proposed
rulemaking (NOPR). Id. at 14322.
The public meeting announced in the
March 2010 notice took place on April
26, 2010. At that meeting, DOE
presented the methodologies and results
of the analyses set forth in the
preliminary TSD. Interested parties
discussed the following major issues at
the public meeting: The efficiency
metric; how test procedure variation
might affect efficiency measurements;
requirements for ballasts in
environments that are sensitive to
electromagnetic interference (EMI);
product classes; manufacturer selling
prices (MSPs) and overall pricing
methodology; markups; the maximum
technologically feasible ballast
efficiency; cumulative regulatory
burden; and shipments. DOE considered
the comments received since
publication of the March 2010 notice,
including those received at the April
2010 public meeting, in the
development of the NOPR.
In April 2011, DOE proposed new and
amended energy conservation standards
for fluorescent lamp ballasts. In
conjunction with the NOPR, DOE also
published on its Web site the complete
TSD for the proposed rule, which
incorporated the analyses DOE
conducted and technical documentation
for each analysis. The TSD included the
engineering analysis spreadsheets, the
LCC spreadsheet, the national impact
analysis spreadsheet, and the
manufacturer impact analysis (MIA)
spreadsheet—all of which are available
on DOE’s Web site.11 The proposed
standards were as shown in Table II.3.
76 FR 20090, 20091 (April 11, 2011).
TABLE II.3—ENERGY CONSERVATION STANDARDS PROPOSED IN THE APRIL 2011 NOPR
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Product class
Proposed BLE standard
IS and RS ballasts that operate ...............................................................
4-foot MBP lamps
8-foot slimline lamps
PS ballasts that operate ...........................................................................
4-foot MBP lamps
4-foot MiniBP SO lamps
4-foot MiniBP HO lamps
IS and RS ballasts that operate 8-foot HO lamps ...................................
PS ballasts that operate 8-foot HO lamps ...............................................
Ballasts that operate 8-foot HO lamps designed for cold temperature
outdoor signs.
11 The Web site address for all the spreadsheets
developed for this rulemaking proceeding are
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1.32 * ln(total lamp arc power) + 86.11.
1.79 * ln(total lamp arc power) + 83.33.
1.49 * ln(total lamp arc power) + 84.32.
1.46 * ln(total lamp arc power) + 82.63.
1.49 * ln(total lamp arc power) + 81.34.
available at: https://www1.eere.energy.gov/buildings/
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appliance_standards/residential/fluorescent_
ballasts_nopr_analytical_tools.html.
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In the NOPR, DOE invited comment
in particular on the following issues: (1)
The exemption for T8 magnetic 12
ballasts in EMI-sensitive environments;
(2) the appropriateness of establishing
efficiency standards using an equation
dependent on lamp-arc power; (3) the
inclusion of several different ballast
types in the same product class; (4) the
methodology used to calculate
manufacturer selling prices; (5) the
efficiency levels considered; (6) the
maximum technologically feasible level;
(7) markups; (8) the inclusion T12
ballasts in the baseline analysis for life
cycle costs; (9) the magnitude and
timing of forecasted shipments; (10) the
methodology and inputs DOE used for
the manufacturer impact analysis—
specifically, DOE’s assumptions
regarding markups, capital costs, and
conversion costs; (12) the potential
impacts of amended standards on small
fluorescent lamp ballast manufacturers;
(13) the trial standard levels (TSLs)
considered; (14) the proposed standard
level; and (15) potential approaches to
maximize energy savings while
mitigating impacts to certain fluorescent
ballast consumer subgroups. 76 FR
20090, 20177 (April 11, 2011).
DOE held a public meeting on May
10, 2011, to hear oral comments on and
solicit information relevant to the
proposed rule (hereafter the May 2011
public meeting). At this meeting, the
National Electrical Manufacturers
Association (NEMA) presented test data
that they found inconsistent with the
data collected by DOE and that could
affect the standards established in the
final rule. In general, NEMA’s ballast
luminous efficiency values appeared to
be lower than those obtained by DOE.
NEMA and other stakeholders agreed
that there were discrepancies between
the two data sets and emphasized the
importance of identifying the source of
the differences. In addition, DOE
received comments on the methodology
used to account for compliance
certification requirements, design
variation, and lab-to-lab variation and
on the appropriate shape of DOE’s
proposed efficiency level curves.
In light of these discrepancies, DOE
published a notice of data availability
(NODA) on August 24, 2011 to: (1)
Announce the availability of additional
test data collected by DOE and the data
submitted by NEMA; (2) address the
differences between test data obtained
by DOE and test data submitted by
12 When DOE refers to a magnetic ballast
throughout this document, it is referring to a low
frequency ballast as defined by as defined in ANSI
C82.13–2002. Similarly, when DOE refers to an
electronic ballast, it is referring to a high frequency
ballast as defined by the same ANSI standard.
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NEMA; (3) describe the methodological
changes DOE was considering for the
final rule based on the additional data;
(4) present efficiency levels developed
using the revised methodology and all
available test data; and (5) request
public comment on these analyses.13
DOE considered the comments
received in response to both the April
2011 NOPR and the August 2011 NODA
when developing this final rule, and
responds to these comments in the
following sections.
III. Issues Affecting the Scope of This
Rulemaking
A. Additional Fluorescent Lamp
Ballasts for Which DOE is Adopting
Standards
1. Scope of EPCA Requirement That
DOE Consider Standards for Additional
Ballasts
As discussed in section II.A,
amendments to EPCA established
energy conservation standards for
certain fluorescent lamp ballasts and
directed DOE to conduct two
rulemakings to consider amending the
standards. The first amendment was
completed with the publication of the
2000 Ballast Rule. This rulemaking
fulfills the statutory requirement to
determine whether to amend standards
a second time. EPCA specifically directs
DOE, in this second amendment, to
determine whether to amend the
standards in effect for fluorescent lamp
ballasts and whether such standards
should be amended so that they would
be applicable to additional fluorescent
lamp ballasts. (42 U.S.C. 6295(g)(7)(B))
The April 2011 NOPR notes that a
wide variety of fluorescent lamp ballasts
are not currently covered by energy
conservation standards, and thus are
potential candidates for coverage under
42 U.S.C. 6295(g)(7). DOE encountered
similar circumstances in a recent
rulemaking that amended standards for
general service fluorescent and
incandescent reflector lamps (hereafter
referred to as the 2009 Lamps Rule).14
74 FR 34080, 34087–8 (July 14, 2009).
In that rule, DOE was directed by EPCA
to consider expanding its scope of
coverage to include additional general
service fluorescent lamps (GSFL). EPCA
defines GSFLs as fluorescent lamps that
can satisfy the majority of fluorescent
lamp applications and that are not
13 The August 2011 NODA and accompanying
data are available here: https://www1.eere.energy.
gov/buildings/appliance_standards/residential/
notice_of_data_availability.html.
14 Documents for the 2009 Lamps Rule are
available at: https://www1.eere.energy.gov/buildings/
appliance_standards/residential/
incandescent_lamps.html.
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designed and marketed for certain
specified, non-general lighting
applications. (42 U.S.C. 6291(30)(B)) As
such, the term ‘‘general service
fluorescent lamp’’ is defined by
reference to the term ‘‘fluorescent
lamp,’’ which EPCA defines as ‘‘a low
pressure mercury electric-discharge
source in which a fluorescing coating
transforms some of the ultraviolet
energy generated by the mercury
discharge into light,’’ and as including
the four enumerated types of fluorescent
lamps for which EPCA already
prescribes standards. (42 U.S.C.
6291(30)(A); 42 U.S.C. 6295(i)(1)(B)) To
construe ‘‘general service fluorescent
lamp’’ in 42 U.S.C. 6295(i)(5) as limited
to those types of fluorescent lamps
would mean there are no GSFLs that are
not already subject to standards, and
hence, there would be no ‘‘additional’’
GSFLs for which DOE could consider
standards. Such an interpretation would
conflict with the directive in 42 U.S.C.
6295(i)(5) that DOE consider standards
for ‘‘additional’’ GSFLs, thereby
nullifying that provision.
Therefore, DOE concluded that the
term ‘‘additional general service
fluorescent lamps’’ in 42 U.S.C.
6295(i)(5) allows DOE to set standards
for GSFLs other than the four
enumerated lamp types specified in the
EPCA definition of ‘‘fluorescent lamp.’’
As a result, the 2009 Lamps Rule
defined ‘‘fluorescent lamp’’ to include:
(1) Any straight-shaped lamp
(commonly referred to as 4-foot medium
bipin lamps) with medium bipin bases,
a nominal overall length of 48 inches,
and rated wattage of 25 or more;
(2) Any U-shaped lamp (commonly
referred to as 2-foot U-shaped lamps)
with medium bipin bases, a nominal
overall length between 22 and 25
inches, and rated wattage of 25 or more;
(3) Any rapid start lamp (commonly
referred to as 8-foot high output lamps)
with recessed double contact bases and
a nominal overall length of 96 inches;
(4) Any instant start lamp (commonly
referred to as 8-foot slimline lamps)
with single pin bases, a nominal overall
length of 96 inches, and rated wattage
of 52 or more;
(5) Any straight-shaped lamp
(commonly referred to as 4-foot
miniature bipin standard output lamps)
with miniature bipin bases, a nominal
overall length between 45 and 48
inches, and rated wattage of 26 or more;
and
(6) Any straight-shaped lamp
(commonly referred to 4-foot miniature
bipin high output lamps) with miniature
bipin bases, a nominal overall length
between 45 and 48 inches, and rated
wattage of 49 or more.
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10 CFR 430.2
In this rulemaking, DOE is directed to
consider whether any amended
standard should be applicable to
additional fluorescent lamp ballasts. (42
U.S.C. 6295(g)(7)(B)) EPCA defines a
‘‘fluorescent lamp ballast’’ as ‘‘a device
which is used to start and operate
fluorescent lamps by providing a
starting voltage and current and limiting
the current during normal operation.’’
(42 U.S.C. 6291(29)(A)) For this rule,
DOE referenced the definition of
fluorescent lamp adopted by the 2009
Lamps Rule. This definition allows DOE
to consider expanding coverage to
include additional fluorescent lamp
ballasts while not eliminating coverage
of any ballasts for which standards
already exist.
2. Identification of the Additional
Ballasts for Which DOE Establishes
Standards
In considering whether to amend the
standards in effect for fluorescent lamp
ballasts so that they apply to
‘‘additional’’ fluorescent lamp ballasts
as specified in section 325(g)(7)(B) of
EPCA, DOE considered all fluorescent
lamp ballasts (for which standards are
not already prescribed) that operate
fluorescent lamps, as defined in 10 CFR
430.2. For each additional fluorescent
lamp ballast, DOE considered potential
energy savings, technological feasibility
and economic justification when
determining whether to include them in
the scope of coverage. In its analyses,
DOE assessed the potential energy
savings from market share estimates,
potential ballast designs that improve
efficiency, and other relevant factors.
For market share estimates, DOE used
both quantitative shipment data and
information obtained during
manufacturer interviews. DOE also
assessed the potential to achieve energy
savings in certain ballasts by
considering whether those ballasts
could serve as potential substitutes for
other regulated ballasts.
In the April 2011 NOPR, DOE
proposed extending coverage to several
additional ballast types including those
that operate: Additional numbers and
diameters of 4-foot MBP lamps, 8-foot
HO lamps, and 8-foot slimline lamps; 4foot miniature bipin (MiniBP) standard
output (SO) lamps; 4-foot MiniBP HO
lamps; and 8-foot HO cold temperature
lamps commonly used in outdoor signs.
DOE did not propose to extend coverage
to additional dimming ballasts or T8
magnetic ballasts that operate in EMIsensitive environments, provided that
these magnetic ballasts were designed
and labeled for use in EMI-sensitive
environments only and shipped by the
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manufacturer in packages of 10 or fewer
ballasts.
The Northwest Energy Efficiency
Alliance (NEEA) and the Northwest
Power and Conservation Council
(NPCC), the Northeast Energy Efficiency
Partnerships (NEEP), the Appliance
Standards Awareness Project (ASAP),
and in a joint comment, ASAP, the
Alliance to Save Energy, the American
Council for an Energy-Efficient
Economy, the National Consumer Law
Center, and the National Resources
Defense Council (hereafter the ‘‘Joint
Comment’’) supported the proposed
scope of coverage. ASAP and the Joint
Comment stated that the expanded
scope contributes significantly to the
forecasted energy savings for this
rulemaking. (NEEA and NPCC, No. 44 at
p. 2 15; NEEP, No. 49 at p. 2; ASAP,
Public Meeting Transcript, No. 43 at pp.
80–2; Joint Comment, No. 46 at p. 2)
DOE also received several comments
regarding the proposed exemption for
T8 magnetic ballasts that operate in
EMI-sensitive environments, coverage of
residential ballasts, and additional
comments recommending further
exemptions. These comments are
discussed in further detail in the
following sections.
a. Ballasts That Operate in
Environments Sensitive to
Electromagnetic Interference
DOE received comments at the April
2010 public meeting that standards
could eliminate magnetic ballasts that
are currently used in certain EMIsensitive environments. DOE conducted
research and interviews with
fluorescent lamp ballast and fixture
manufacturers to identify the following
applications as potentially sensitive to
EMI: Medical operating room telemetry
or life support systems; airport control
systems; electronic test equipment;
radio communication devices; radio
recording studios; correctional facilities;
clean rooms; facilities with low signalto-noise ratios; and aircraft hangars or
other buildings with predominantly
metal construction.16 DOE learned from
manufacturer interviews that magnetic
ballasts are typically recommended for
situations in which EMI has been or is
expected to be a concern.
Although there are several methods to
reduce electromagnetic interference,
available data do not indicate that EMI15 A notation in the form ‘‘NEEA and NPCC, No.
44 at p. 2’’ identifies a written comment that DOE
has received and has included in the docket of this
rulemaking. This particular notation refers to a
comment: (1) Submitted by NEEA and NPCC; (2) in
document number 44 of the docket; and (3) on page
2 of that document.
16 This list is not all inclusive.
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related issues with electronic ballasts
can be eliminated such that there are no
longer safety concerns. For this reason,
in the April 2011 NOPR DOE proposed
an exemption for T8 magnetic ballasts
designed and labeled for use in EMIsensitive environments only and
shipped by the manufacturer in
packages containing 10 or fewer
ballasts. DOE believed the exemption
was necessary because in some
environments, EMI could pose a serious
safety concern that is best mitigated
with magnetic ballast technology. DOE
did not believe magnetic ballasts would
likely be used as substitutes in current
electronic ballast applications due to
their higher cost and weight. 76 FR
20090, 20100–1 (April 11, 2011).
NEEA and NPCC, NEMA, and ASAP
supported the exemption for magnetic
ballasts in EMI-sensitive locations.
(NEEA and NPCC, No. 44 at p. 2;
NEMA, Public Meeting Transcript, No.
43 at p. 70; NEMA, No. 47 at pp. 2–3;
ASAP, Public Meeting Transcript, No.
43 at pp. 80–2) ASAP and NEEA and
NPCC suggested requiring the
description ‘‘designed, labeled, and
marketed for use in EMI-sensitive
applications’’ to limit the possibility of
exempted ballasts being sold in other
applications. Philips commented that
they are unsure how manufacturers
would be able to control the marketing
through distributors to the proper
market. ASAP and NEEA and NPCC
acknowledged that although
manufacturers cannot control
distribution, they can control how they
market their products. (ASAP, Public
Meeting Transcript, No. 43 at pp. 80–82;
Philips, Public Meeting Transcript, No.
43 at p. 82; NEEA and NPCC, No. 44 at
p. 2)
DOE did not receive any adverse
comment regarding the exemption for
T8 magnetic ballasts in EMI-sensitive
applications and therefore, for the
reasons discussed above, maintains this
exemption in the final rule. DOE agrees
with ASAP and NEEA and NPCC that
this exemption should be designed such
that, to the greatest extent possible, it
does not become a pathway to
circumvent compliance with standards
adopted by this rulemaking. Therefore,
DOE has modified the description of the
exemption to cover ballasts ‘‘designed,
labeled, and marketed for use in EMIsensitive applications.’’ See appendix
5E of the TSD for more details on EMIsensitive applications.
b. Ballasts That Operate in the
Residential Sector
Radionic disagreed with DOE’s
decision to cover residential ballasts
and stated that new residential models
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developed to meet standards are likely
to have a high initial cost. Because
residential consumers are sensitive to
first cost, Radionic stated that
consumers will choose less expensive
and less efficient technologies, thereby
potentially decreasing energy savings.
(Radionic, No. 36 at p. 1)
As discussed in the April 2011 NOPR,
DOE believes that residential ballasts
represent a sizeable portion of the
overall ballast market and represent
significant potential energy savings.
DOE agrees with comments received in
response to the preliminary TSD, stating
that demand for residential fluorescent
ballasts will likely grow substantially as
residential building codes become more
stringent. For example, California,
Oregon, and Washington have codes
that require fluorescent or higherefficacy systems in homes. Similarly,
the 2009 International Energy
Conservation Code requires that 50
percent of all permanently installed
lighting in residences have a minimum
efficacy of 45 lumens per watt. 76 FR
20090, 20099 (April 11, 2011). DOE
projects that increased lighting efficacy
requirements will drive consumers to
continue to purchase fluorescent
systems despite incremental increases
in first cost. Furthermore, DOE notes
that consumers are already purchasing
higher efficiency fluorescent ballasts
despite their higher initial first cost
relative to other lighting technologies.
As discussed in section V.A.1 and
section V.B.5.g, standards for residential
ballasts save significant amounts of
energy, and are technologically feasible
and economically justified. Therefore,
DOE includes residential ballasts in the
scope of coverage for this final rule.
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c. Ballasts That Operate Below
Minimum ANSI Current Levels
At the May 2011 public meeting, the
General Electric Company (GE)
commented that DOE’s efficiency levels
for programmed start (PS) ballasts
assumed high efficiency filament cutout at all arc powers. GE stated,
however, that some low ballast factor
(BF) PS ballasts operate at currents
below minimum American National
Standards Institute (ANSI) levels for T8
and T12 lamps and thus require
filament heating to maintain lamp life.
GE and NEMA noted that these ballasts
would be unable to meet BLE
requirements proposed in the April
2011 NOPR due to cathode heating, but
would offer energy savings due to their
relatively low power levels and use in
conjunction with occupancy sensors.
Thus, GE requested that these low BF
ballasts be exempt from standards. (GE,
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Public Meeting Transcript, No. 43 at pp.
236, 238; NEMA, No. 47 at p. 6)
NEEA and NPCC recognized the
operating limitations presented by these
ballasts, but expressed concern over the
lack of information about their fraction
of shipments, the markets where they
are most commonly sold, and their cost
relative to other, more common ballast
types designed to operate the same type
and number of lamps. Specifically,
NEEA and NPCC commented that these
ballasts might be the kind of currently
exempted product provided to the
residential market, and that their
continuing exemption could result in an
increase in sales and accompanying loss
in energy savings. (NEEA and NPCC,
No. 44 at p. 4) The Joint Comment also
highlighted the possibility of an
increase in the use of these low BF
ballasts in all applications if they were
exempt from standards. They stated that
the current small market share did not
mean that shipments would not increase
substantially in response to an
exemption, thereby decreasing the
potential energy savings due to the
standards adopted by the rulemaking.
(Joint Comment, No. 46 at pp. 2, 3)
DOE reviewed ANSI C78.81–2010 17
and determined that ballasts designed to
operate 4-foot MBP T8 lamps are
required to use some level of cathode
heating when operating lamps at
currents less than 155 milliamperes
(mA). Through testing, DOE learned the
BF of these ballasts was similar to or
less than 0.7. This low BF (which affects
light output) is a unique utility that
might be removed from the market if
these ballasts were held to the
established standard level. DOE
analyzed test data for 4-foot MBP T8
programmed start ballasts with average
currents less than 155 mA to determine
if there was a trend between low current
and low efficiency. DOE determined
that as current decreased, the BLE also
decreased. DOE concluded that none of
the PS ballasts tested with an average
current of less than 140 mA were able
to meet the max tech efficiency levels
analyzed in the PS product class.
Therefore, DOE is exempting these PS
low-current ballasts from the standards
adopted in this final rule.
DOE does not believe that an
exemption for these ballasts will lead to
an increase in their use because when
current is reduced, light output is also
reduced. Consumers have light output
requirements and would not consider a
ballast that does not meet such a
17 American National Standard for Electric
Lamps—Double-Capped Fluorescent Lamps—
Dimensional and Electrical Characteristics,
Approved January 14, 2010.
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requirement to be an adequate
substitute. Reduced light output could
also require additional lighting fixtures
to be purchased in order to meet
expected lighting levels. It is unlikely,
however, that consumers would
purchase additional fixtures due to high
first cost. As a result, DOE establishes
an exemption for these PS, low-current
ballasts. DOE has determined that the
threshold for the exemption will be set
at the current levels indicated in its
testing, 140 mA for 4-foot MBP ballasts.
d. Other Exemptions
Radionic commented that DOE should
consider exempting outdoor ballasts,
cold weather ballasts, ‘‘all ballasts for
less than 30 watts’’, ballasts that have a
normal power factor 18 (a power factor
equal to or greater than 0.6 and less than
0.9), and ballasts that are produced in
small quantities for special applications.
(Radionic, No. 36 at p. 1)
DOE notes that several of the ballasts
mentioned by Radionic are already
subject to standards. For example,
because outdoor and cold weather
ballasts, apart from sign ballasts, are
already covered by current standards,
DOE cannot exempt them from
standards in this rulemaking due to
anti-backsliding statutory provisions
(discussed in section II.A). Similarly,
DOE interpreted ‘‘all ballasts for less
than 30 watts’’ as ballasts that operate
total lamp arc powers less than 30 W.
Some of these ballasts (such as ballasts
that operate F34T12 lamps) are covered
by current standards and cannot be
exempted in this rulemaking. In general,
DOE specifies efficiency levels using a
power law equation that assigns BLE
values as a function of total lamp arc
power. In other words, the equation
takes lower lamp arc power into account
when assigning appropriate standard
levels. Even though they operate lower
wattage lamps, these ballasts still
demonstrate significant potential energy
savings and DOE test data shows they
are capable of meeting the standard
levels adopted by this final rule.
Therefore, DOE will not exempt ballasts
that operate total lamp arc powers less
than 30 W in this final rule.
Ballasts with a normal power factor
are classified as residential ballasts.
DOE continues to cover residential
ballasts as discussed in section III.A.2.b.
For residential ballasts, as well as all
other types listed above, Radionic did
18 As defined by ANSI C82.13–2002, the power
factor is calculated by determining the ratio of the
input power to the apparent power. The input
power is measured with a wattmeter, and the
apparent power is the ballast input voltage
multiplied by the ballast input current. For more
information, see chapter 3 of the TSD.
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not provide DOE with any specific
information regarding ballasts produced
in small quantities for special
applications, or specific data indicating
that these ballasts would be unable to
meet any standards. DOE has looked at
the market and has not identified any
applications, other than those already
defined, in which ballasts are unable to
meet standards and would require an
exemption. For all of the ballast types
Radionic listed, DOE has determined
that the adopted standard levels are
technologically feasible and
economically justified.
3. Summary of Fluorescent Lamp
Ballasts To Which DOE Extends
Coverage
With the exception of the comments
discussed previously in this section,
DOE received no other input related to
coverage of fluorescent lamp ballasts. In
addition, DOE’s revised analyses
indicate that energy conservation
standards for the ballasts for which DOE
proposed coverage in the April 2011
NOPR are still technologically feasible,
economically justified, and would result
in significant energy savings. Therefore,
in summary, this final rule extends
coverage to the following fluorescent
lamp ballasts:
(1) Ballasts that operate 4-foot
medium bipin lamps with a rated
wattage 19 of 25W or more, and an input
voltage at or between 120V and 277V;
(2) Ballasts that operate 2-foot
medium bipin U-shaped lamps with a
rated wattage of 25W or more, and an
input voltage at or between 120V and
277V;
(3) Ballasts that operate 8-foot high
output lamps with an input voltage at or
between 120V and 277V;
(4) Ballasts that operate 8-foot
slimline lamps with a rated wattage of
52W or more, and an input voltage at or
between 120V and 277V;
(5) Ballasts that operate 4-foot
miniature bipin standard output lamps
with a rated wattage of 26W or more,
and an input voltage at or between 120V
and 277V;
(6) Ballasts that operate 4-foot
miniature bipin high output lamps with
a rated wattage of 49W or more, and an
input voltage at or between 120V and
277V;
(7) Ballasts that operate 4-foot
medium bipin lamps with a rated
wattage of 25W or more, an input
voltage at or between 120V and 277V, a
power factor of less than 0.90, and are
designed and labeled for use in
residential applications; and
19 The 2009 Lamps Rule adopted a new definition
for rated wattage that can be found in 10 CFR 430.2.
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(8) Ballasts that operate 8-foot high
output lamps with an input voltage at or
between 120V and 277V, have an
enclosure with an Underwriters
Laboratories (UL) Type 2 rating, and are
designed, labeled, and marketed for use
in outdoor signs.20
The following ballasts are exempt from
coverage:
(1) Additional dimming ballasts;
(2) Low frequency T8 ballasts that are
designed, labeled, and marketed for use
in EMI-sensitive environments and sold
in packages of 10 or fewer;
(3) PS ballasts that operate 4-foot MBP
T8 lamps and deliver on average less
than 140mA to each lamp.
B. Off Mode and Standby Mode Energy
Consumption Standards
EPCA requires energy conservation
standards adopted for a covered product
after July 1, 2010 to address standby
mode and off mode energy use. (42
U.S.C. 6295(gg)(3)) Because DOE is
required by consent decree to publish a
final rule establishing any amended
standards for fluorescent lamp ballasts
by October 28, 2011,21 this rulemaking
is required to consider standby mode
and off mode energy use. DOE
determined that it is not possible for the
ballasts at issue in this final rule to meet
the off-mode criteria because there is no
condition in which a ballast is
connected to the main power source and
is not already in a mode accounted for
in either active or standby mode. In the
test procedure addressing standby mode
energy consumption, DOE determined
that the only ballasts that consume
energy in standby mode are those that
incorporate an electronic circuit that
enables the ballast to communicate with
and be part of a lighting control
interface (e.g., digitally addressable
lighting interface (DALI) enabled
ballasts). 74 FR 54445, 54447–8
(October 22, 2009). DOE believes that
the only commercially available ballasts
that incorporate an electronic circuit to
communicate with a lighting control
interface are dimming ballasts.
20 In the April 2011 NOPR, these ballasts were
described as ‘‘ballasts that operate 8-foot high
output lamps with an input voltage at or between
120V and 277V, and operate at ambient
temperatures of ¥20 degrees F or less and are used
in outdoor signs.’’ For the reasons stated in section
0, DOE uses this revised description for the final
rule.
21 Under the consolidated Consent Decree in New
York v. Bodman, No. 05 Civ. 7807 (S.D.N.Y. filed
Sept. 7, 2005) and Natural Resources Defense
Council v. Bodman, No. 05 Civ. 7808 (S.D.N.Y. filed
Sept. 7, 2005), as amended, the U.S. Department of
Energy is required to publish, as that term is
defined in the consent decree, a final rule amending
energy conservation standards for fluorescent lamp
ballasts no later than October 28, 2011.
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As discussed in the April 2011 NOPR,
DOE did not expand the scope of
coverage to include additional dimming
ballasts. Therefore, the only covered
dimming ballasts are the four products
specified in 10 CFR 430.32(m)(5) that
operate reduced-wattage lamps. DOE
research has not identified any dimming
ballasts currently on the market that
operate these lamps because the fill gas
composition of reduced-wattage lamps
makes them undesirable for use in
dimming applications. Because DOE is
not aware of any other dimming
products that are covered by existing
standards, DOE was unable to
characterize standby mode energy
consumption. Therefore, DOE does not
adopt provisions to address ballast
operation in standby mode as part of the
energy conservation standards that are
the subject of this rulemaking.
IV. General Discussion
A. Test Procedures
1. Background
As noted previously, manufacturers
must use the test procedures for ballasts
at 10 CFR part 430, subpart B, appendix
Q to determine compliance with the
currently applicable ballast efficacy
factor standards. On March 24, 2010,
DOE issued a NOPR in which it
proposed revisions to these test
procedures. 75 FR 14288. The principal
change DOE proposed to the existing
test methods was, in an effort to reduce
measurement variation, to eliminate
photometric measurements used to
determine ballast efficacy factor (BEF).
Instead, DOE proposed to use electrical
measurements to determine ballast
efficiency (BE), which could then be
converted to BEF using empirically
derived transfer equations. The
proposed changes specified that the
ballast operate a resistive load rather
than a lamp load during performance
testing. For consistency with previous
methods, no changes were proposed for
the measurement of BF (which required
photometric measurements). The
preliminary TSD for this rulemaking
considered standards in terms of BEF, as
determined by the methods proposed in
the active mode test procedure NOPR.
After reviewing comments submitted
in response to the active mode test
procedure NOPR (75 FR 14287, March
24, 2010) and conducting additional
research, DOE issued a supplemental
NOPR (SNOPR) proposing a lamp-based
ballast efficiency metric instead of the
resistor-based metric proposed in the
NOPR. 75 FR 71570 (November 24,
2010). The new metric, BLE, was equal
to the total lamp arc power divided by
ballast input power. DOE believed this
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lamp-based metric more accurately
assessed the real-life performance of a
ballast and also reduced measurement
variation relative to the existing test
procedure for BEF. DOE also proposed
a method for calculating the BF of a
ballast by dividing the measured lamp
arc power on the test ballast by the
measured lamp arc power on a reference
ballast. In cases where reference ballast
operating conditions were unavailable,
the SNOPR provided a reference lamp
power (specific to the ballast type) from
an ANSI standard or from empirical
results. The April 2011 NOPR for the
standards rulemaking used the BLE
procedures specified in the test
procedure SNOPR to propose energy
conservation standards.
The final rule for the active mode test
procedure, which was published in the
Federal Register on May 4, 2011,
adopted the BLE metric proposed in the
SNOPR with a few modifications. 76 FR
25211. To account for the increase in
lamp efficacy associated with highfrequency lamp operation versus lowfrequency, DOE had proposed an
adjustment to the BLE of low-frequency
systems. DOE had proposed that lowfrequency BLE be multiplied by 0.9 to
account for the approximately 10
percent increase in lighting efficacy
associated with high-frequency lamp
operation. For the final rule, DOE
assigned specific lamp operating
frequency adjustment factors for each
ballast type considered. The adjustment
factors more accurately approximated
the increase in lighting efficacy
associated with high-frequency lamp
operation. In addition, in the final rule,
DOE did not adopt a BF measurement
procedure because BF was no longer
used to define product classes for
energy conservation standards.
This final rule for energy conservation
standards evaluates standards for
ballasts in terms of the BLE metric
adopted in the active mode test
procedure. Appendix Q1 of 10 CFR part
430 Subpart B will be used to evaluate
compliance with the standards adopted
in this final rule. 76 FR 25211, 25213
(May 4, 2011)
DOE received comments in response
to the April 2011 NOPR regarding the
new fluorescent ballast testing
procedure and BLE metric. Several
stakeholders expressed support for the
BLE metric. The Pacific Gas and Electric
Company, Southern California Edison,
the Southern California Gas Company,
and San Diego Gas and Electric
(hereafter the ‘‘CA Utilities’’)
commented that the new BLE metric is
an improvement over the existing BEF
metric because it allows for efficiency
comparison across a wider range of
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ballasts. (CA Utilities, No. 45 at p. 1)
NEEP and CA Utilities stated that the
new BLE metric successfully simplifies
testing requirements and enables the
vast consolidation of product classes,
which will make the compliance and
enforcement processes easier. (NEEP,
No. 92 at p. 3; CA Utilities, No. 45 at
pp. 1–2) CA Utilities also approved of
the new test procedure, commenting
that they support the use of lamps to
measure lamp arc power instead of sets
of resistor banks designed to simulate
lamps. CA Utilities stated that actual
lamps, which have varying impedance
based on power, more accurately
represent real world loads on ballasts.
They added that maintaining different
sets of resistor banks at every ballast
factor would have increased the testing
burden for manufacturers. (CA Utilities,
No. 45 at p. 2)
DOE also received several comments
requesting clarification on the new test
procedure. These comments are
discussed in the following sections.
2. Transfer Function
GE asked if DOE would be creating
transfer functions, similar to those
proposed in the active mode test
procedure NOPR, to convert BLE to BEF
for marketing purposes. GE noted that as
BEF will continue to be more relevant
for consumers using lumens and system
watts, manufacturers will continue to
publish those numbers even though
they will not test the ballasts with that
metric. (GE, Public Meeting Transcript,
No. 43 at p. 237) As discussed in section
VII.D, to verify that no backsliding had
occurred, DOE developed a method to
convert BEF to BLE in order to compare
current and newly adopted standards.
However, DOE requires manufacturers
to certify compliance in terms of the
BLE metric only and therefore does not
provide a transfer function for
converting BLE to BEF for marketing
purposes.
3. Reference Lamp
GE noted that it is not always clear
what lamp should be used when testing
a ballast and requested clarification on
this matter. (GE, Public Meeting
Transcript, No. 43 at pp. 236–7) DOE
notes that Table A in the ballast test
procedure, Appendix Q1 of 10 CFR part
430 Subpart B, provides the appropriate
lamp wattage, diameter and base to use
in testing for each covered ballast type.
For example, the first row of Table A
shows that ballasts ‘‘that operate
straight-shaped lamps (commonly
referred to as 4-foot medium bipin
lamps) with medium bipin bases and a
nominal overall length of 48 inches’’
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should be tested with 32W T8 MBP
lamps.
4. Total Lamp Arc Power
The People’s Republic of China (P.R.
China) noted that in the April 2011
NOPR, the term ‘‘total lamp arc power’’
was not well-defined. They noted that
ANSI C78.81–2010 specifies ‘‘arc
wattage’’ for various fluorescent tube
lamps but does not define ‘‘total lamp
arc power.’’ Furthermore, while the test
procedure SNOPR included a definition
for ‘‘total lamp arc power,’’ it also
included a table that listed a low and/
or high frequency ‘‘reference lamp arc
power’’ for each covered ballast type. 75
FR 71570, 71592 (November 24, 2010).
P.R. China indicated that these terms
caused confusion regarding the
appropriate value to be used when
calculating the efficiency standard.
Therefore, they suggested DOE clarify
the specific value of ‘‘total lamp arc
power’’ and use consistent terminology
to avoid confusion. (P.R. China, No. 51
at p. 3–4)
CA Utilities and NEEA and NPCC
agreed that it was unclear which arc
power should be used to calculate the
applicable BLE standard. CA Utilities
recommended that DOE require
manufacturers to use the average lamp
arc power of the tested sample to
determine the BLE for a given model.
(CA Utilities, No. 58 at p. 4; NEEA and
NPCC, No. 59 at p. 3)
DOE notes that reference lamp arc
power refers to the arc wattage listed in
ANSI C78.81–2010 and, as shown in
that standard, can vary depending on
whether the reference ballast operates at
low or high frequency settings.22 These
values were provided in the test
procedure SNOPR for the purposes of
calculating ballast factor. However,
because the test procedure final rule did
not adopt a procedure for calculating
ballast factor, reference lamp arc powers
are no longer relevant. Total lamp arc
power is a measured, not listed, value
and is evaluated according to the
recently adopted test procedure.
DOE also notes that 10 CFR 429.26
does not currently reflect the new
ballast luminous efficiency metric. DOE
plans to consider certification
procedures in upcoming rulemakings
related to compliance certification and
enforcement.23 For this final rule, DOE
22 The test procedure defines a low frequency
ballast as a fluorescent lamp ballast that operates at
a supply frequency of 50 to 60 Hz and operates the
lamp at the same frequency as the supply. The test
procedure incorporates the ANSI C82.13 definition
of high frequency ballast as a device which operates
at a supply frequency of 50 or 60 Hz and operates
the lamp at frequencies greater than 10 kHz.
23 Details on certification and enforcement
procedures can be found at: www1.eere.energy.gov/
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computed the reported ballast luminous
efficiency and total lamp arc power
assuming the ballast basic models
would be certified in the following
manner. To certify compliance,
manufacturers would calculate the total
lamp arc power and BLE for each
sample tested according to 10 CFR 430,
Subpart B, Appendix Q1. They would
then average the total lamp arc power of
each sample and input that average into
the appropriate energy conservation
standard efficiency level. The output of
that equation dictates the minimum BLE
that the reported BLE for each basic
model must meet or exceed. To
calculate the reported BLE for each
basic model, manufacturers would
follow the provisions laid out in 10 CFR
429.26(a)(2)(ii).
B. Technological Feasibility
1. General
In each standards rulemaking, DOE
conducts a screening analysis based on
information it has gathered on all
current technology options and
prototype designs that could improve
the efficiency of the products that are
the subject of the rulemaking. As the
first step in such 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 these means for
improving efficiency are technologically
feasible. DOE considers technologies
incorporated in commercially available
products or in working prototypes to be
technologically feasible. 10 CFR 430,
subpart C, appendix A, section 4(a)(4)(i).
Once DOE has determined that
particular technology options are
technologically feasible, it further
evaluates each of them in light of the
following additional screening criteria:
(1) Practicability to manufacture, install,
or service; (2) adverse impacts on
product utility or availability; and (3)
adverse impacts on health or safety. 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 considers an amended
standard for a type or class of covered
product, it must determine the
maximum improvement in energy
efficiency or maximum reduction in
energy use that is technologically
feasible for that product. (42 U.S.C.
6295(p)(1)) Accordingly, DOE
70561
determined the maximum
technologically feasible (‘‘max tech’’)
ballast efficiency in the engineering
analysis, using the design options
identified in the screening analysis (see
chapter 5 of the final rule TSD).
As a first step to identifying the max
tech efficiency level, DOE conducted
testing of commercially available
ballasts. DOE was unable to identify
working prototypes that had a higher
efficiency than the tested products.
Therefore, DOE has determined that
TSL 3B, which is based on the most
efficient commercially available ballasts
tested, represents the highest efficiency
level that is technologically feasible for
a sufficient diversity of commercially
available products (spanning several
ballast factors, number of lamps per
ballast, and types of lamps operated)
within each product class. The max tech
efficiency levels require the use of
electronic ballasts with improved
components (such as high efficiency
transformers, diodes, capacitors, and
transistors). The max tech levels also
require IS instead of RS ballasts, or
some form of cathode cut-out
technology for PS ballasts. Table IV.1
presents the max tech levels for each
product class.
TABLE IV.1—MAX TECH LEVELS
BLE = A/(1 + B * total lamp arc power ∧-C) where A, B, and C are as follows
Product class
A
IS and RS ballasts (not classified as residential) that operate .............................................
4-foot MBP lamps
2-foot U-shaped lamps
8-foot slimline lamps
PS ballasts (not classified as residential) that operate .........................................................
4-foot MBP lamps
2-foot U-shaped lamps
4-foot MiniBP SO lamps
4-foot MiniBP HO lamps
IS and RS ballasts (not classified as sign ballasts) that operate 8-foot HO lamps ..............
PS ballasts (not classified as sign ballasts) that operate 8-foot HO lamps ..........................
Sign ballasts that operate 8-foot HO lamps ..........................................................................
IS and RS residential ballasts that operate ...........................................................................
4-foot MBP lamps
2-foot U-shaped lamps
8-foot slimline lamps
PS residential ballasts that operate: ......................................................................................
4-foot MBP lamps
2-foot U-shaped lamps
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C. Energy Savings
1. Determination of Savings
DOE used its national impact analysis
(NIA) spreadsheet to estimate energy
savings from new or amended standards
for the ballasts that are the subject of
this final rule. (The NIA spreadsheet
model is described in section V.F of this
final rule and in chapter 11 of the final
rule TSD.) DOE forecasted energy
savings for each TSL, beginning in 2014,
the year that compliance with the new
and amended standards is required, and
B
0.993
0.27
0.25
0.993
0.51
0.37
0.993
0.973
0.993
0.993
0.28
0.52
0.47
0.29
0.25
0.37
0.25
0.25
0.973
0.50
0.37
ending in 2043. DOE quantified the
energy savings attributable to each TSL
as the difference in energy consumption
between the standards case and the base
case. The base case represents the
forecast of energy consumption in the
absence of new and amended
buildings/appliance_standards/certification_
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mandatory efficiency standards, and
considers market demand for higherefficiency products. For example, DOE
models a shift in the base case from
covered fluorescent lamp ballasts
toward emerging technologies such as
light emitting diodes (LEDs).
The NIA spreadsheet model calculates
the electricity savings in ‘‘site energy’’
expressed in kilowatt-hours (kWh). Site
energy is the energy directly consumed
by ballasts at the locations where they
are used. DOE reports national energy
savings on an annual basis in terms of
the aggregated source (primary) energy
savings, which is the savings in energy
used to generate and transmit the site
energy. (See final rule TSD chapter 11.)
To convert site energy to source (also
known as primary) energy, DOE derived
time-dependent conversion factors from
the model used to prepare the Energy
Information Administration’s (EIA’s)
Annual Energy Outlook 2010
(AEO2010).
2. Significance of Savings
As noted in section I, under 42 U.S.C.
6295(o)(3)(B) DOE is prohibited from
adopting a standard for a covered
product if such standard would not
result in ‘‘significant’’ energy savings.
While the term ‘‘significant’’ is not
defined in the Act, the U.S. Court of
Appeals, in Natural Resources Defense
Council v. Herrington, 768 F.2d 1355,
1373 (DC Cir. 1985), indicated that
Congress intended ‘‘significant’’ energy
savings in this context to be savings that
were not ‘‘genuinely trivial.’’ The energy
savings for all of the TSLs considered in
this final rule are nontrivial, and
therefore DOE considers them
‘‘significant’’ within the meaning of
section 325 of EPCA.
D. Economic Justification
1. Specific Criteria
As noted in section II.A, EPCA
provides seven factors to be evaluated in
determining whether a potential energy
conservation standard is economically
justified. (42 U.S.C. 6295(o)(2)(B)(i)) The
following sections discuss how DOE
addresses each of those seven factors in
this rulemaking.
mstockstill on DSK4VPTVN1PROD with RULES2
a. Economic Impact on Manufacturers
and Consumers
In determining the impacts of a new
or amended standard on manufacturers,
DOE first determines the quantitative
impacts using an annual cash-flow
approach. This includes both a shortterm assessment—based on the cost and
capital requirements during the period
between the announcement of a
regulation and when the regulation
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requires compliance—and a long-term
assessment over the 30-year analysis
period. The impacts analyzed include
INPV (which values the industry based
on expected future cash flows), cash
flows by year, changes in revenue and
income, and other measures of impact,
as appropriate. Second, DOE analyzes
and reports the impacts on different
types of manufacturers, including an
analysis of 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.
DOE also takes into account cumulative
impacts of different related DOE
regulations and other regulatory
requirements on manufacturers.
For individual consumers, measures
of economic impact include the changes
in LCC and the payback period
associated with new or amended
standards. The LCC, which is separately
specified as one of the seven factors to
consider when determining the
economic justification for a new or
amended standard, (42 U.S.C.
6295(o)(2)(B)(i)(II)), is discussed in the
following section. For consumers in the
aggregate, DOE calculates the NPV from
a national perspective of the economic
impacts on consumers over the forecast
period used in a particular rulemaking.
b. Life-Cycle Costs
The LCC is the sum of the purchase
price of a product (including its
installation) and the operating expense
(including energy, maintenance, and
repair expenditures) discounted over
the lifetime of the product. The LCC
savings for the considered efficiency
levels are calculated relative to a base
case that reflects likely trends in the
absence of new or amended standards.
The LCC analysis requires a variety of
inputs, such as product prices, product
energy consumption, energy prices,
maintenance and repair costs, product
lifetime, and consumer discount rates.
DOE assumes in its analysis that
consumers purchase the product in
2014.
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. A
distinct advantage of this approach is
that DOE can identify the percentage of
consumers estimated to achieve LCC
savings or experiencing an LCC
increase, in addition to the average LCC
savings associated with a particular
standard level. In addition to identifying
ranges of impacts, DOE evaluates the
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LCC impacts of potential standards on
identifiable sub-groups of consumers
that may be disproportionately affected
by a national standard.
c. Energy Savings
While significant conservation of
energy is a separate statutory
requirement for imposing 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))
DOE uses the NIA spreadsheet results in
its consideration of total projected
savings.
d. Lessening of Utility or Performance of
Products
In establishing classes of products,
and in evaluating design options and
the impact of potential standard levels,
DOE seeks to develop standards that
would not lessen the utility or
performance of the products under
consideration. The efficiency levels
considered in this final rule will not
affect any features valued by consumers,
such as starting method, ballast factor,
or cold temperature operation.
Therefore, none of the TSLs presented
in section VII.A would reduce the utility
or performance of the ballasts that are
the subject of this final rule. (42 U.S.C.
6295(o)(2)(B)(i)(IV))
e. Impact of Any Lessening of
Competition
EPCA directs DOE to consider any
lessening of competition likely to result
from standards. It directs the Attorney
General to determine the impact, if any,
of any lessening of competition likely to
result from standards and to transmit
this determination to the Secretary, not
later than 60 days after the publication
of a proposed rule, together with an
analysis of the nature and extent of this
impact. (42 U.S.C. 6295(o)(2)(B)(i)(V)
and (B)(ii)) To assist the Attorney
General in making this determination,
DOE transmitted a copy of the April
2011 NOPR and TSD to the Attorney
General for review. The Attorney
General’s response is discussed in
section VII.B.5, and is reprinted at the
end of this rule.
f. Need of the Nation To Conserve
Energy
The non-monetary benefits of the
standards in this final rule are likely to
be reflected in improvements to the
security and reliability of the nation’s
energy system. Reduced demand for
electricity may also result in reduced
costs for maintaining the reliability of
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the nation’s electricity system. DOE
conducts a utility impact analysis to
estimate how standards may affect the
nation’s needed power generation
capacity.
Energy savings from the standards in
this final rule are also likely to result in
environmental benefits in the form of
reduced emissions of air pollutants and
greenhouse gases (GHG) associated with
energy production. DOE reports the
environmental effects from the new and
amended standards—and from each TSL
it considered for ballasts—in the
environmental assessment contained in
chapter 16 of the final rule TSD. DOE
also reports estimates of the economic
value of reduced emissions reductions
resulting from the considered TSLs.
mstockstill on DSK4VPTVN1PROD with RULES2
g. Other Factors
The Act allows the Secretary of
Energy to consider any other factors he
or she deems relevant in determining
whether a standard is economically
justified. (42 U.S.C. 6295(o)(2)(B)(i)(VII))
Under this provision, DOE considers
subgroups of consumers that may be
adversely affected by the standards
established in this rule. DOE
specifically assesses the impact of
standards on low-income consumers,
institutions of religious worship, and
institutions that serve low-income
populations. In considering these
subgroups, DOE analyzes variations on
electricity prices, operating hours,
discount rates, and baseline ballasts. See
section V.G for further detail.
2. Rebuttable Presumption
As set forth in 42 U.S.C.
6295(o)(2)(B)(iii), EPCA provides for a
rebuttable presumption that an energy
conservation standard is economically
justified if the additional cost to the
consumer of a product that meets the
standard is less than three times the
value of the first-year energy (and, as
applicable, water) savings resulting from
the standard, as calculated under the
applicable DOE test procedure. DOE’s
LCC and PBP analyses generate values
that calculate the payback period for
consumers of potential new and
amended energy conservation
standards. These analyses include, but
are not limited to, the 3-year payback
period contemplated under the
rebuttable presumption test. However,
DOE routinely conducts an economic
analysis that considers the full range of
impacts to the consumer, manufacturer,
nation, and environment, as required
under 42 U.S.C. 6295(o)(2)(B)(i). The
results of this analysis serve as the basis
for DOE to evaluate the economic
justification for a potential standard
level (thereby supporting or rebutting
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the results of any preliminary
determination of economic
justification). The rebuttable
presumption payback calculation is
discussed in section VII.B.1.c.
V. Methodology and Discussion
DOE used three spreadsheets to
estimate the impact of the adopted
standards. The first spreadsheet
calculates LCCs and payback periods of
potential new energy conservation
standards. The second provides
shipments forecasts and then calculates
national energy savings and NPV
impacts of new energy conservation
standards. Through the third, the
Government Regulatory Impact Model
(GRIM), DOE assesses manufacturer
impacts.
Additionally, DOE uses a version of
EIA’s National Energy Modeling System
(NEMS) to estimate the impacts of
energy efficiency standards on electric
utilities and the environment. The
NEMS model simulates the energy
sector of the U.S. economy. The version
of NEMS used for appliance standards
analysis is called NEMS-BT, and is
based on the AEO2010 version of NEMS
with minor modifications. The NEMSBT accounts for the interactions
between the various energy supply and
demand sectors and the economy as a
whole.24
As a basis for this final rule, DOE has
continued to use the spreadsheets and
approaches explained in the April 2011
NOPR. DOE used the same general
methodology as applied in the NOPR,
but revised some of the assumptions
and inputs for the final rule in response
to public comments. The following
sections discuss these revisions.
A. Product Classes
In evaluating and establishing energy
conservation standards, DOE divides
covered products into classes by the
type of energy used, or by capacity or
other performance-related feature that
justifies a different standard for
products having such feature. (See 42
U.S.C. 6295(q)) In deciding whether a
feature justifies a different standard,
DOE must consider factors such as the
utility of the feature to users. Id. DOE
24 The EIA approves the use of the name ‘‘NEMS’’
to describe only an AEO version of the model
without any modification to code or data. Because
the present analysis entails some minor code
modifications and runs the model under various
policy scenarios that deviate from AEO
assumptions, the name ‘‘NEMS-BT’’ refers to the
model as used here. (BT stands for DOE’s Building
Technologies Program.) For more information on
NEMS, refer to The National Energy Modeling
System: An Overview, DOE/EIA–0581 (98)
(Feb.1998), available at: tonto.eia.doe.gov/
FTPROOT/forecasting/058198.pdf.
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70563
establishes energy conservation
standards for different product classes
based on the criteria set forth in 42
U.S.C. 6295(o).
For the April 2011 NOPR, DOE
undertook extensive testing of
fluorescent lamp ballasts to evaluate the
impact of numerous ballast
characteristics on BLE. Using this test
data, DOE empirically found a
relationship between the BLE metric
and lamp arc power. In general, as lamp
arc power increases, BLE increases as
well. DOE believes this association is
due to the fixed losses of a ballast
becoming proportionally less significant
at higher lamp arc powers. This
relationship allowed DOE to set
efficiency levels as a function of total
lamp arc power across a wide range of
power levels, which simplified the
product class structure and the amount
of scaling required among product
classes. In addition, setting efficiency
levels with an equation allows for easier
adaption of standards to future
innovations. For example, an equation
could account for the introduction of
new ballast factors. It would also not
necessarily have to be revised if the test
procedure were modified to require
testing with reduced-wattage lamps,
toward which manufacturers have
commented the market is moving.
NEMA agreed that an efficiency
standard using pure electrical
measurements on a ballast operating a
lamp load is appropriate provided the
equation accounts for different
operating characteristics of the various
ballast types that are grouped into each
product class. (NEMA, No. 47 at p. 3)
NEMA’s specific comments regarding
the appropriate grouping of various
ballast types are discussed later in this
section.
After considering several potential
class-setting factors, DOE proposed in
the April 2011 NOPR to separate
product classes based on starting
method (instant start and rapid start
versus programmed start), ballasts that
operate 8-foot HO lamps, and ballasts
that operate 8-foot HO lamps in coldtemperature outdoor signs. DOE noted
that for each of those three ballast types,
a difference in utility was accompanied
by a difference in the BLE predicted by
the power-efficiency relationship. These
three distinctions resulted in five
product classes for: IS/RS ballasts that
operate 4-foot MBP and 8-foot slimline
lamps; PS ballasts that operate 4-foot
MBP, T5 SO, and T5 HO lamps, IS/RS
ballasts that operate 8-foot HO lamps,
PS ballast that operate 8-foot HO lamps,
and ballasts that operate 8-foot HO
lamps in cold temperature outdoor
signs.
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ASAP and CA Utilities commented
that the reduction from the 70 product
classes considered in the preliminary
analysis to the five product classes
proposed in the NOPR provides a
simpler standard and thus facilitates
compliance and enforcement. (ASAP,
Public Meeting Transcript, No. 43 at p.
80; CA Utilities, No. 45 at pp. 1–2) In
addition, DOE received several
comments related to the inclusion of
residential and commercial ballasts in a
single product class, the definition of
the sign ballast product class, the
grouping of ballasts with different
starting methods, and the potential for
additional subclasses within the 8-foot
HO product class. These comments are
discussed in the following sections.
mstockstill on DSK4VPTVN1PROD with RULES2
1. Residential Ballasts
Separate minimum power factor and
electromagnetic interference
requirements exist for residential and
commercial ballasts. Specifically,
residential ballasts have more stringent
(or lower maximum allowable) EMI
requirements than commercial ballasts;
they also have less stringent (or lower
minimum allowable) power factor
requirements.25 Based on these differing
requirements, in the April 2011 NOPR,
DOE concluded that residential ballasts
offer a unique utility in that they serve
distinct market sectors and applications.
However, because the April 2011 NOPR
test data indicated residential ballasts
could achieve similar levels of
efficiency as commercial ballasts at the
highest standard levels analyzed, DOE
did not propose a separate product class
for residential ballasts. In response to
the April 2011 NOPR, DOE received
several comments regarding this
conclusion.
CA Utilities agreed with DOE’s
proposal that a separate product class is
not necessary for residential ballasts
because no specific characteristic affects
efficiency. They stated that residential
ballasts are not subject to more stringent
FCC standards for EMI because these
standards only apply to devices
operating at frequencies greater than 30
megahertz (MHz). Thus, CA Utilities
emphasized that starting method is
more relevant to the efficiency of the
ballast than the distinction of residential
or commercial. (CA Utilities, No. 58 at
p. 4; CA Utilities, No. 45 at p. 7) NEMA
disagreed, commenting that not only are
residential ballasts subject to more
stringent standards for EMI, but that this
requirement decreases ballast efficiency.
25 ANSI C82.77–2002 requires residential ballasts
to have a minimum power factor of 0.5 and
commercial ballasts to have a minimum power
factor of 0.9.
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NEMA and Universal added that while
they support the inclusion of residential
ballasts in this rulemaking, they oppose
the inclusion of residential ballasts in
the same product class as commercial
ballasts, given their different efficiencies
and application requirements. (NEMA,
No. 47 at p. 4; Universal, Public Meeting
Transcript, No. 43 at pp. 76–7)
Current regulatory requirements
subject residential ballasts to more
stringent conducted EMI requirements
than commercial ballasts. In particular,
DOE notes that separate FCC standards
exist for both radiated and conducted
EMI emissions. The 30 MHz standards
cited by CA Utilities correspond to
radiated EMI emissions frequencies, not
to ballast operating frequencies. Devices
that operate at frequencies less than
1.705 MHz, such as fluorescent lamp
ballasts, are not required to measure
radiated emissions that exist at
frequencies above 30 MHz; therefore,
radiated EMI standards do not apply to
fluorescent lamp ballasts. Ballasts with
conducted EMI emissions in the
frequency range of 0.45 to 30 MHz,
however, must comply with FCC
standards for conducted EMI. The
conducted EMI requirements are
applicable to all fluorescent lamp
ballasts, but are more stringent for
residential ballasts, necessitating added
interference filtration in order to
comply.
CA Utilities also commented that
although residential ballasts are subject
to a lower minimum power factor
requirement, they do not necessarily
have low power factors; in fact, ballasts
with either high or low power factors
can be installed in the residential sector.
CA Utilities concluded that therefore,
many high-efficiency commercial
ballasts available on the market today
can be used in the residential sector
without issue. (CA Utilities, No. 45 at
pp. 6–7) Philips agreed that ballasts
with high power factors can be installed
in the residential sector, noting that the
ENERGY STAR program for residential
fixtures may soon require some level of
power factor correction. Philips
commented that increased power factor
correction actually reduces the
efficiency of residential ballasts because
the losses associated with meeting FCC
Class B requirements become more
significant when including power factor
correction. (Philips, Public Meeting
Transcript, No. 43 at pp. 77–9)
Acuity Brands added that a
residential ballast that achieves the
same efficiency as the most efficient
commercial product would be 50
percent more expensive because of the
FCC EMI requirements. (Acuity Brands,
Public Meeting Transcript, No. 43 at p.
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79) NEMA pointed out that that a higher
price could influence consumers to
migrate from fluorescent luminaires to
lower efficiency incandescent or
halogen fixtures. (NEMA, No. 47 at p. 4)
Edison Electric Institute (EEI) also
expressed concern regarding the prices
of residential ballasts, stating that a
separate product class for residential
ballasts is needed to improve economics
for residential and low-income
consumers. (EEI, No. 48 at p. 2)
DOE agrees that high power factor
ballasts, similar to the power factors
possessed by commercial products, can
be installed in the residential sector.
However, the addition of a power factor
correction stage to a ballast circuit
substantially increases the amount of
electromagnetic interference due to the
presence of high speed switches.
Therefore, to meet the FCC requirements
for residential products, commercial
ballasts would require a more
significant EMI filter and thus incur
additional power losses.
As stated previously, DOE determined
in the April 2011 NOPR that despite the
differences in power factor and EMI
requirements between residential and
commercial 2-lamp 4-foot MBP IS/RS
ballasts, both ballast types could reach
achieve similar levels of efficiency at
the highest levels analyzed. Based on
the similarity in efficiency, DOE
included both ballast types in the same
product class. Since publication of the
April 2011 NOPR, however, DOE has
obtained additional test data for
residential ballasts that indicate a
separate product class for residential
ballasts is warranted. Specifically, DOE
tested 4-lamp residential ballasts and
was unable to confirm that it was
technologically feasible for 4-lamp
residential ballasts to meet the
commercial ballast efficiency levels.
Thus, in the August 2011 NODA, DOE
considered establishing a separate
product class for residential ballasts.
Because DOE proposed extending
coverage to residential ballasts with
both IS/RS and PS starting methods,
DOE considered two new product
classes: (1) IS/RS ballasts that operate 4foot MBP lamps in the residential sector
and (2) PS ballasts that operate 4-foot
MBP lamps in the residential sector. A
separate product class for residential
ballasts would allow DOE to adopt
separate standard levels for these
products based on their associated
consumer economics.
In response to the August 2011
NODA, the CA Utilities, NEEA and
NPCC, and ASAP, the American
Council for an Energy-Efficient
Economy, and the Natural Resources
Defense Council, in a second Joint
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Comment, disagreed with the
establishment of a separate product
class for residential ballasts because
residential ballasts can meet the same
efficiency levels as commercial ballasts.
The second Joint Comment added that
although the data indicates that 4-lamp
residential ballasts cannot achieve the
same efficiency as their commercial
counterparts, DOE should not establish
a separate product class for this reason.
They argued that 2-lamp ballasts are far
more common in the residential sector
than 4-lamp ballasts, which are often
installed in commercial buildings. (CA
Utilities, No. 58 at p. 4; NEEA and
NPCC, No. 59 at p. 3; Second Joint
Comment, No. 57 at p. 1–2)
In addition, the second Joint
Comment, CA Utilities, and NEEA and
NPCC stated that even if there were a
difference in efficiency, DOE has not
demonstrated that residential ballasts
provide a unique consumer utility.
(Second Joint Comment, No. 57 at pp.
1–2; CA Utilities, No. 58 at p. 4; NEEA
and NPCC, No. 59 at p. 3) These
interested parties stated that residential
ballasts are not subject to more stringent
FCC requirements for electromagnetic
interference. CA Utilities added that
even if they were, EMI filters are
available and they do not believe these
components affect efficiency. These
interested parties also reiterated
previous comments that, while
residential ballasts have lower
minimum power factor requirements,
this did not prevent high power factor
ballasts from being installed in this
market sector. The second Joint
Comment, CA Utilities, and NEEA and
NPCC concluded that commercial
ballasts could be used in the residential
sector without issue.
DOE notes that both 2-lamp ballasts
and 4-lamp ballasts are used in the
residential sector. In addition, while 2lamp ballasts may be more popular in
the residential sector, ballasts that
operate different numbers of lamps,
such as the 4-lamp ballasts described by
the second Joint Comment above,
provide a unique utility, as explained in
the following paragraph. EPCA requires
DOE to consider any lessening of the
utility or the performance of the covered
products likely to result from the
imposition of a standard. 42 U.S.C.
6295(o)(2)(B)(i)(IV). EPCA also prohibits
DOE from establishing standards that
are likely to result in the unavailability
of performance characteristics, features,
sizes, capacities and volumes that are
substantially the same as those generally
available in the United States when the
standard is established. 42 U.S.C.
6295(o)(4). EPCA further requires DOE
to prescribe a lower energy efficiency
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level for product classes in which the
products have a performance-related
feature, considering the utility of that
feature to consumers and other factors,
that justifies a lower efficiency level. 42
U.S.C. 6295(q). Available data indicates
that these products cannot achieve the
same efficiencies as their commercial
counterparts and that, therefore, a
separate product class and efficiency
standard is warranted.
DOE disagrees with the assertion that
commercial ballasts can be used as
substitutes for residential products.
Although both ballasts can have high
power factors, residential ballasts are
subject to more stringent FCC standards
for conducted EMI emissions. DOE
agrees that EMI can be mitigated by the
addition of a filter, but disputes the CA
Utilities’ claim that the filter does not
affect efficiency. If a residential ballast
were designed to have a high power
factor, the addition of a power factor
correction stage would increase the
amount of conducted emissions. Thus,
the residential ballast must possess a
stronger EMI filter to comply with FCC
requirements. DOE notes that only one
T8 residential ballast in the data set had
a power factor greater than 0.9, and this
model did not meet the most efficient
EL considered for the residential
product class. For these reasons, DOE
concludes that residential ballasts are
less efficient than commercial ballasts
and also offer unique consumer utility.
Therefore, as stated above, DOE has
established a separate product class for
these products in this final rule.
DOE also received comments
regarding the types of ballasts that
should be included in the residential
product class. NEMA suggested that the
residential ballast product class include
ballasts that operate 8-foot slimline
lamps in addition to ballasts that
operate 4-foot MBP lamps. (NEMA, No.
47 at p. 6) In its search of the market,
DOE discovered a small number of 8foot slimline ballasts in product catalogs
that are intended for use in the
residential sector. DOE also noted that
residential ballasts that are designed to
operate 4-foot MBP lamps can also
operate 2-foot U-shaped lamps. As
described above, DOE finds that
residential ballasts cannot achieve the
same efficiency levels as commercial
ballasts and that they offer the consumer
unique utility. Therefore, DOE has
modified the description of the
residential product class to include: (1)
IS/RS ballasts that operate 4-foot MBP,
2-foot U-shaped, and 8-foot slimline
lamps in the residential sector and (2)
PS ballasts that operate 4-foot MBP and
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70565
2-foot U-shaped lamps in the residential
sector.26
2. Sign Ballasts
In the April 2011 NOPR, DOE
proposed establishing a separate
product class for ballasts that operate 8foot HO lamps in cold temperature
outdoor signs. This proposal was based
on their unique utility and associated
decrease in efficiency relative to
standard 8-foot HO ballasts. Sign
ballasts operate outdoors in wet and
cold temperature environments and
have highly flexible lamp pairing
possibilities, both in terms of varied
individual lamp lengths and different
total lamp length (sum of the length of
all lamps operated by the ballast). In
response to the April 2011 NOPR, DOE
received comments that the proposed
sign ballast product class description
was not sufficient.
ASAP encouraged DOE to ensure that
the definition of the sign ballast product
class is sufficiently narrow. (ASAP, No.
46 at p. 2) CA Utilities commented that
DOE should reevaluate the defining
characteristics of sign ballasts because it
does not seem to accurately capture the
products for which it was intended. In
particular, CA Utilities and ASAP cited
the description ‘‘ballasts that operate 8foot HO lamps’’ as problematic because
it could leave out sign ballasts that are
designed for other lamp lengths. (CA
Utilities, No. 45 at p. 7; ASAP, No. 46
at p. 2)
DOE agrees that sign ballasts capable
of operating other lamp lengths, in
addition to 8-foot lamps, should be
included in the sign ballast product
class. However, DOE does not agree that
ballasts designed to operate solely these
alternate lamps, other than 8-foot HO
lamps, should be considered in the sign
ballast product class or scope of
coverage. In determining the scope of
fluorescent ballasts covered by this
rulemaking, DOE’s research indicated
that the vast majority of sign ballasts are
capable of operating 8-foot HO lamps, in
addition to other lamp lengths. Because
sign ballasts that cannot operate 8-foot
HO lamps were so rare, there was
insufficient available data to analyze the
efficiency potential of these ballasts.
DOE does not include those ballasts that
cannot operate 8-foot HO lamps in the
sign ballast product class. DOE defined
the added scope of sign ballasts based
on their operation of 8-foot HO lamps
and assessed the BLE of sign ballasts
based on their performance when
26 PS ballasts are not used in combination with
8-foot slimline lamps because the base of these
lamps only has a single pin rather than the two
required for electrode heating.
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operating 8-foot HO lamps. Therefore, if
the sign ballast cannot operate an 8-foot
HO lamp, DOE did not include it in the
scope of coverage of this rulemaking.27
CA Utilities also commented that it is
not clear in the NOPR whether the usage
of the phrase ‘‘cold temperature’’ in the
product class description is a key factor
in the definition of sign ballasts. They
pointed out that some standard
commercial ballasts and NEMA
Premium products are rated for negative
20 degree F temperatures. (CA Utilities,
Public Meeting Transcript, No. 43 at pp.
83–5) ASAP and the CA Utilities
encouraged DOE to define the sign
ballast product class in a way that does
not reference cold temperature
operation because it is not unique to
these products. If the definition does not
include better identifying
characteristics, the CA Utilities
expressed concern that sign ballasts that
are not designed for cold temperature
environments might be exempt from
standards (ASAP, Public Meeting
Transcript, No. 43 at p. 87; CA Utilities,
Public Meeting Transcript, No. 43 at pp.
89–90) CA Utilities concluded that DOE
must ensure that products not intended
to provide the specific utility of outdoor
sign ballasts cannot be construed as
outdoor sign ballasts, and that products
which are intended to provide this
utility are covered by the standards. (CA
Utilities, No. 45 at p. 7) Universal
explained that cold temperature does
have an effect on efficiency and is one
of several characteristics that would
separate a sign ballast application from
another application. GE also noted that
more energy is required to strike at a
cold temperature with a longer lamp
and it becomes more difficult for a
system to start as lamp length increases
and as temperature decreases.
(Universal, Public Meeting Transcript,
No. 43 at pp. 84–5; GE, Public Meeting
Transcript, No. 43 at pp. 86–7, 89)
Available data support the CA
Utilities assertion that cold temperature
is not a key factor in the description of
sign ballasts. Although sign ballasts are
rated to operate in cold temperature
environments, often down to ¥20
degrees Fahrenheit, DOE surveyed the
market and found that all ballast types
covered by this rulemaking have
product offerings that include cold
temperature ratings, including 8-foot
HO ballasts designed and marketed for
traditional non-outdoor sign
applications. While a cold-temperature
rating may affect efficiency, DOE found
27 For these same reasons, the test procedure in
Subpart B of 10 CFR Part 430 Appendix Q1
specifies that a sign ballast must be tested with the
maximum number of 8-foot HO (either T8 or T12)
lamps it is designed to operate.
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that these cold temperature rated nonsign ballasts were among the most
efficient ballasts of their respective
types. Therefore, DOE agrees that the
cold-temperature rating is not a
descriptor specific to ballasts intended
to be used in outdoor signs.
Several manufacturers described
alternative characteristics for defining
the sign ballast product class. Universal
and Osram Sylvania (OSI) commented
that a sign ballast has a much longer
striking distance, which requires a
much higher open circuit voltage. GE
added that striking distance and open
circuit voltage add to efficiency losses.
(Universal, Public Meeting Transcript,
No. 43 at pp. 84–5; OSI, Public Meeting
Transcript, No. 43 at p. 87; GE, Public
Meeting Transcript, No. 43 at pp. 86–7,
89) However, Philips pointed out that IS
ballasts are not as affected by wiring
distances. (Philips, Public Meeting
Transcript, No. 43 at pp. 88–9) Philips
also stated that outdoor sign ballasts
have a different weather rating than
traditional ballasts. (Philips, Public
Meeting Transcript, No. 43 at pp. 88–9)
GE added that many manufacturers
design to higher transient ratings for
protection of the ballast in its outdoor
application. (GE, Public Meeting
Transcript, No. 43 at pp. 86–7, 89)
In DOE’s assessment of the market,
electronic sign ballasts use the IS
starting method and therefore may not
be as affected by wiring distances and
increased open circuit voltage as RS
ballasts. DOE also examined the
available product literature to see if the
increased wiring distances led to a
significant difference in open circuit
voltage. Higher open circuit voltages can
require different components capable of
withstanding those high voltages. These
components may have decreased losses
due to their more rugged build. If open
circuit voltage were significantly
different for sign ballasts, DOE could
use that voltage to define the sign ballast
product class. However, because open
circuit voltage information is not readily
available in product specification
sheets, DOE could not further specify
the sign ballast product class using open
circuit voltage. DOE agrees with GE that
higher transient ratings might lead to
increased ballast losses, but was unable
to determine a typical transient rating
specific to sign ballasts from product
literature.
Through a review of product
datasheets, DOE did find that sign
ballasts have a UL Type 2 rating for the
enclosure whereas regular 8-foot HO
ballasts are rated for UL Type 1. Type
2 enclosures are moisture resistant and
have a rust resistant coating so that the
ballast can be used in plastic sign
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applications without a separate metal
enclosure.28 Because the UL Type 2
enclosure rating distinguishes currently
commercially available sign ballasts
from regular ballasts that operate 8-foot
HO lamps, DOE will use this enclosure
rating as a distinction in defining the
sign ballast product class.
ASAP suggested that the phrase
‘‘designed and marketed’’ should be
added to the product class description
for sign ballasts. ASAP also commented
that sign ballasts should be labeled with
the designation ‘‘for use only in outdoor
signs.’’ (ASAP, No. 46 at pp. 2–3) DOE
agrees with ASAP that these types of
descriptors should be added to
strengthen the product class
description. Therefore, DOE has
modified the description of these
products to include ‘‘designed, labeled,
and marketed for use in outdoor signs.’’
In summary, in this final rule, DOE
adopted the description ‘‘ballasts with a
UL Type 2 rating designed, labeled, and
marketed for use in outdoor signs that
operate 8-foot HO lamps’’ to define the
sign ballast product class. DOE finds
that this description is the most specific
definition that can be accurately applied
to all sign ballasts. While redesign of
traditional 8-foot HO ballasts to meet
the definition of the sign ballast product
class is possible, DOE believes this to be
an unlikely scenario due to the added
cost of manufacturing the UL Type 2
enclosure and resulting increased price
to the end-user. Customers currently
purchasing traditional 8-foot HO
systems would likely not tolerate a price
increase resulting from added features
that are not necessary for traditional
applications.
3. Starting Method
In the April 2011 NOPR, based on
DOE’s determination that IS and RS
ballasts provide the same utility to the
consumer, DOE proposed to include
both of these starting methods in one
product class. DOE proposed a separate
product class for PS ballasts because
these ballasts were less efficient yet
increased lamp lifetime in frequent on/
off cycling applications. NEMA
commented that lower performance RS
ballasts should be grouped with PS
ballasts instead of IS, citing their
similarity in applications and operating
characteristics. (NEMA, No. 47 at
p. 3, 6)
DOE acknowledges that ballasts have
different operating characteristics based
on starting method. For example, IS
ballasts are more efficient than RS and
28 Universal Lighting Technologies Inc. The Sign
Ballast Today. 2010. www.signasign.com/news/
signindustry.html.
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PS ballasts because the latter contain
extra components and use extra power
to provide filament heating to the lamp,
thereby increasing the lamp’s lifetime.
In the BLE metric, such cathode heating
is counted as a loss because it does not
directly contribute to the creation of
light. Therefore, RS and PS ballasts will
have lower BLEs than comparable IS
ballasts. DOE confirmed that RS and IS
ballasts were commonly used as
substitutes for each other, indicating
consumers find no added benefit or
utility associated with RS relative to IS.
Both RS and PS ballasts use cathode
heating; however, only PS ballasts limit
the voltage across the lamp tube to
prevent glow discharge during the
initial cathode heating. This prevention
of glow discharge also increases lamp
lifetime in frequent on/off cycling
applications. DOE found PS ballasts
were commonly used in conjunction
with occupancy sensors (a frequent on/
off cycling application). DOE
determined that because of their ability
to limit voltage, PS ballasts offer the
user a distinct utility. As a result of this
unique utility and the difference in
efficiency associated with these ballasts,
DOE decided to establish separate
product classes for programmed start
ballasts.
4. 8-Foot HO
In the April 2011 NOPR, DOE
included ballasts that operate all types
of 8-foot HO lamps in one product class.
NEMA commented that separate
product classes should be established
for ballasts that operate 8-foot HO T8
lamps and those that operate 8-foot HO
T12 lamps. NEMA indicated that 8-foot
T8 HO ballasts are typically electronic.
70567
(NEMA, No. 47 at p. 5) Though T8
electronic ballasts are more efficient
than T12 magnetic and electronic
ballasts, DOE found the two ballast
types were commonly used as
replacements and identified no added
utility associated with 8-foot T8
electronic or 8-foot T12 ballasts.
Therefore, neither lamp diameter nor
electronic versus magnetic ballast type
justifies the creation of different product
classes for 8-foot HO ballasts.
5. Summary
After evaluating potential class-setting
factors, DOE has established separate
product classes for programmed start
ballasts, residential ballasts, ballasts that
operate 8-foot HO lamps, and sign
ballasts. Table V.1 summarizes the
seven product classes.
TABLE V.1—FLUORESCENT LAMP BALLAST PRODUCT CLASSES
Description
Product class No.
IS and RS ballasts (not classified as residential) that operate: ....................................................................................................
4-foot MBP lamps
2-foot U-shaped lamps
8-foot slimline lamps
PS ballasts (not classified as residential) that operate: ................................................................................................................
4-foot MBP lamps
2-foot U-shaped lamps
4-foot MiniBP SO lamps
4-foot MiniBP HO lamps
IS and RS ballasts (not classified as sign ballasts) that operate 8-foot HO lamps ......................................................................
PS ballasts (not classified as sign ballasts) that operate 8-foot HO lamps ..................................................................................
Sign ballasts that operate 8-foot HO lamps ..................................................................................................................................
IS and RS residential ballasts that operate ...................................................................................................................................
4-foot MBP lamps
2-foot U-shaped lamps
8-foot slimline lamps
PS residential ballasts that operate:.
4-foot MBP lamps
2-foot U-shaped lamps
B. Engineering Analysis
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1. NOPR Approach
The engineering analysis develops
cost-efficiency relationships to show the
manufacturing costs of achieving
increased efficiency. In the April 2011
NOPR, DOE used the following
methodology to conduct its engineering
analysis.
Determine Representative Product
Classes and Representative Ballast
Types. When multiple product classes
exist, DOE selects certain classes as
‘‘representative’’ to concentrate
analytical effort. The representative
product classes represent the most
commonly sold ballasts and the majority
of the ballast shipment volume. In the
April 2011 NOPR, DOE analyzed four of
the then five total product classes as
representative. These included, 1) IS/RS
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ballasts that operate 4-foot MBP and 8foot slimline lamps; 2) PS ballasts that
operate 4-foot MBP lamps, 4-foot
MiniBP SO lamps, and 4-foot MiniBP
HO lamps; 3) IS/RS ballasts that operate
8-foot HO lamps; 4) and ballasts that
operate 8-foot HO lamps in cold
temperature outdoor signs. DOE did not
directly analyze PS ballasts that operate
8-foot HO lamps due to their relatively
low market share.
Within each representative product
class, DOE selected at least one
representative ballast type for each lamp
type. For the IS/RS product class, DOE
analyzed ballasts that operate: Two 4foot MBP lamps; (2) four 4-foot MBP
lamps; two 8-foot slimline lamps; and
two 4-foot MBP lamps in the residential
sector. For the PS product class, DOE
analyzed ballasts that operate: (1) Two
4-foot T5 SO lamps; two 4-foot T5 HO;
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1
2
3
4
5
6
7
two 4-foot MBP lamps; and four 4-foot
MBP lamps. For the 8-foot HO IS/RS
product class, DOE analyzed 2-lamp
ballasts as the representative ballast
type, whereas for the sign ballast
product class DOE analyzed 4-lamp
ballasts as representative. DOE limited
its representative ballast types to
include only those ballasts that exhibit
a normal ballast factor 29, as this BF is
most common.
Collecting and Analyzing Test Data.
DOE then tested a range of ballasts from
multiple manufacturers including
extensive testing of the representative
ballast types. DOE attempted to test
29 DOE defines low ballast factor as being less
than or equal to 0.78, normal ballast factor as being
greater than 0.78 but less than 1.10, and high ballast
factor as being greater than or equal to 1.10.
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five 30 samples for ballasts included in
the representative ballast type categories
(purchased over two years) and three
samples for non-representative ballast
types. DOE conducted testing at two
laboratories or ‘‘labs,’’ one primary lab
where the majority of testing occurred
and another lab to analyze possible labto-lab variation. DOE conducted this
testing in accordance with the lampbased ballast luminous efficiency
procedure in Appendix Q1 of 10 CFR
430.
Determine Efficiency Levels. Next,
using the test data, DOE empirically
found a relationship between BLE and
the natural logarithm or ‘‘log’’ of total
lamp arc power. In general, as total
lamp arc power increased, BLE
increased as well. DOE’s hypothesis was
that this behavior was due to the fixed
losses of a ballast becoming
proportionally less significant at higher
arc powers. DOE established efficiency
levels as a natural logarithmic function
of total lamp arc power based on this
power-efficiency relationship.
After compiling the test data, DOE
plotted BLE versus total lamp arc power
for both standard and high efficiency
product lines from multiple
manufacturers. Based on analysis of test
data for representative ballast types,
DOE identified certain natural divisions
in BLE. DOE then adjusted the
coefficient and constant of the
logarithmic power-efficiency equation
to create efficiency levels that
corresponded to these divisions. DOE
found that the more efficient ballast
product lines generally had a reduced
(flatter) slope than the standardefficiency products. To reflect this
observation, DOE decreased the
coefficient of the more efficient EL
equations and increased the coefficient
of the less efficient EL equations. In the
April 2011 NOPR, DOE established
three efficiency levels for each product
class except for sign ballasts, for which
it developed one efficiency level above
the baseline level.
In developing the max tech level, DOE
found that no working prototypes
existed that had a distinguishably
higher BLE than currently available
ballasts. Therefore, DOE established
TSL3 as the highest level at which a
sufficient diversity of products
(spanning several ballast factors,
number of lamps per ballast, and types
of lamps operated) was commercially
available.
30 Because certain models were placed on
backorder due to limited supply/production, only
about 60 percent of representative ballast types in
the April 2011 NOPR were tested with five or more
samples.
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In the April 2011 NOPR, DOE noted
that compliance certification
requirements could affect the reported
efficiency. The active mode test
procedure requires manufacturers to
report the lower of either the sample
average or the value calculated by an
equation intended to account for small
sample sizes. DOE’s analysis of its own
test data showed that it was more likely
that manufacturers would be reporting
the compliance equation result, as it
would be the lower of the two values.
Thus, DOE calculated the average
difference between the output of the
compliance equation and the sample
mean to be 0.2 percent and reduced the
efficiency levels, based on average BLEs,
by this value.
DOE also considered lab-to-lab
variation when determining efficiency
levels in the April 2011 NOPR. While
DOE tested a large number of ballasts at
one primary lab, DOE also tested a
subset of those ballasts at a second lab
to determine the magnitude of any
variation. DOE found that tested
efficiencies for the ballast models sent
to the second lab were slightly lower (by
0.6 percent on average) than the values
measured at the main test facility. DOE
then applied this additional 0.6
reduction to the efficiency levels, which
were based on the primary lab’s test
data.
Select Baseline and More Efficient
Ballasts. For each representative ballast
type, DOE established baseline ballasts
to serve as reference points against
which DOE measures changes from
potential amended energy conservation
standards. Generally, a baseline ballast
is a commercially available ballast that
just meets existing Federal energy
conservation standards and provides
basic consumer utility. If no standard
exists for that specific ballast, the
baseline ballast represents the most
common ballast sold within a
representative ballast type with the
lowest ballast luminous efficiency. DOE
selected specific characteristics such as
starting method, BF, and input voltage
to characterize the most common
ballast. DOE also selected multiple
baseline ballasts for some representative
ballast types to ensure consideration of
varied consumer economics. Because
fluorescent lamp ballasts are designed to
operate fluorescent lamps, DOE also
considered properties of the entire
lamp-and-ballast system. Though
ballasts are capable of operating several
different lamp wattages, in the April
2011 NOPR, DOE chose the fluorescent
lamp most commonly used with each
ballast for analysis.
DOE selected commercially available
ballasts with higher BLEs as
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replacements for each baseline ballast
by considering the design options
identified in the technology assessment
and screening analysis (see chapter 4 of
the NOPR TSD). DOE also included two
substitution cases in the engineering
analysis. In the first substitution case,
the consumer is not able to change the
spacing of the fixture and therefore
replaces one baseline ballast with a
more efficient ballast. This generally
represents the lighting retrofit scenario
where fixture spacing is predetermined
by the existing installation. In this case,
light output is generally maintained to
within 10 percent of the baseline system
lumen output.31 In the second
substitution case, the consumer is able
to change the spacing of the fixture and
purchases either more or fewer ballasts
to maintain light output. This represents
a new construction scenario in which
the consumer has the flexibility to
assign fixture spacing based on the light
output of the new system. In this case,
DOE normalizes the light output relative
to the baseline ballast.
Conduct Price Analysis. In the April
2011 NOPR, DOE developed ballast
manufacturer selling prices using three
main inputs: (1) Teardown data; (2)
manufacturer price lists (blue books);
and (3) confidential manufacturersupplied MSPs and incremental MPC
values. In general, DOE used a
combination of information from
teardowns and manufacturer price lists
throughout the analysis and used the
aggregated manufacturer-supplied MSPs
for comparison purposes. DOE used
ratios of online supplier retail prices to
scale to ELs where data from both
teardowns and manufacturer price lists
were unavailable.
Scaling to Non-Representative
Product Classes. DOE scales ELs from
representative product classes to those
product classes it did not analyze
directly. In the NOPR analysis, DOE
applied a two percent reduction to the
efficiency levels for the 8-foot HO IS/RS
representative product class to
determine efficiency levels for the 8-foot
HO PS product class.
Comments Received. In response to
the April 2011 NOPR and subsequent
NODA, DOE received comments on the
available data, methodology,
engineering results, and efficiency
levels. All of these comments are
discussed in further detail in the
following sections.
31 In some instances (e.g., when switching from
T12 to T8 ballasts), light output exceeds these
limits.
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2. Available Test Data
For the April 2011 NOPR, DOE tested
more than 450 ballasts to develop
proposed energy conservation
standards. At the time the NOPR was
published, DOE posted test data to its
public Web site as Appendix 5C of the
TSD. Appendix 5C contained a listing of
all ballast models tested at DOE’s
primary lab for the April 2011 NOPR,
including identifying characteristics
such as lamp type operated, number of
lamps operated, starting method, ballast
factor, input voltage, and catalog
performance value. For each ballast
model, DOE also reported average 32
tested values for input power, total lamp
arc power, and BLE.33
At the May 2011 public meeting,
NEMA presented data collected from
several manufacturers.34 NEMA’s data
included average BLE test results from
three manufacturers that were
subsequently reduced by 0.8 percent to
account for compliance certification
requirements. Attendees of the public
meeting noted that the BLE values of the
most efficient ballast models tested by
NEMA appeared to be less than the most
efficient ballast models tested by DOE.
NEMA also noted that about 60 percent
of DOE’s test data represented ballast
models with less than four tested
samples, which is not consistent with
the minimum number of samples
required to demonstrate compliance
with DOE’s standards. The CA Utilities
stated that if possible, DOE should
conduct testing of four or more samples
to more accurately reflect the testing
process that must be completed by
manufacturers for certification
purposes. (NEMA, No. 52 at p. 9; CA
Utilities, No. 45 at p. 3)
Following the May 2011 public
meeting, DOE posted to the public
meeting Web site a more comprehensive
set of test data used to develop the April
2011 NOPR, which specified ballasts by
serial numbers, added round robin test
results, and included results for each
sample tested, rather than the average
across several samples for each model
number. DOE also purchased and tested
more than 120 additional ballasts to
increase tested models’ sample size to a
minimum of four samples consistent
with compliance certification
32 The average across several samples for each
model number.
33 DOE obtained these values in accordance with
the active mode test procedure in Appendix Q1 of
10 CFR 430.
34 These test results were contained in a Power
Point presentation that was subsequently posted to
the public meeting Web site at: https://www1.
eere.energy.gov/buildings/appliance_standards/
residential/fluorescent_ballasts_nopr_public_
meeting.html.
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requirements in 10 CFR 429.26.
Furthermore, DOE tested additional
ballast models, particularly for sign
ballasts and residential ballasts, to gain
more market information about these
products. All available test data—the
NEMA-provided data, the data utilized
for the April 2011 NOPR, and the results
of additional testing conducted after
publication of the April 2011 NOPR—
were posted on DOE’s Web site in
conjunction with the publication of the
August 2011 NODA.35
3. NEMA-Provided and DOE BLE Data
Comparison
As described in the previous section,
at the May 2011 public meeting, NEMA
members presented test results for the
highest efficiency NEMA Premium
products. NEMA emphasized that its
results represented only high efficiency
products, which generally exceeded
NEMA Premium efficiency
requirements. Therefore the
comparisons did not include hundreds
of products in lower-efficiency product
lines that would be eliminated at the
proposed standard level. NEMA
compared its results to TSL3, the
proposed standard level in the April
2011 NOPR. Based on its data and
analysis, NEMA determined that 88
percent of its highest efficiency
products failed to meet the proposed
standard level. NEMA added that these
IS and PS ballasts are likely 80 to 85
percent of the total market. NEMA
concluded that the implementation of
the proposed standards would cause a
catastrophic ballast shortage in the
market. (NEMA, Public Meeting
Transcript, No. 43 at pp. 25–7; NEMA,
No. 98 at pp. 2, 6)
A comparison of DOE and NEMA data
sets showed that BLE values reported by
NEMA were consistently lower than
those reported by DOE. For example,
NEMA noted that its data showed no
ballast with a BLE higher than 91
percent at 50 watts, while DOE’s data
showed a BLE as high as 94 percent at
the same wattage. NEMA also found that
the variation between samples of each
ballast model was much smaller within
manufacturer-provided data than within
DOE’s data. NEMA underscored the
significance of its data, stating that it
would submit data derived using these
same methods to demonstrate
compliance with new standards.
(NEMA, Public Meeting Transcript, No.
43 at pp. 47–8, 50, 99; NEMA, No. 98
at p. 6)
35 The August 2011 NODA and accompanying
data are available here: www1.eere.energy.gov/
buildings/appliance_standards/residential/
notice_of_data_availability.html.
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Earthjustice, Northwest Energy
Efficiency Alliance (NEEA), ASAP,
NEEP, and the CA Utilities emphasized
the importance of determining the cause
of the differences between DOE and
NEMA test data. (Earthjustice, Public
Meeting Transcript, No. 43 at p. 66;
NEEA, Public Meeting Transcript, No.
43 at pp. 120–1; ASAP, Public Meeting
Transcript, No. 43 at pp. 46–7; NEEP,
No. 49 at pp. 1, 2; CA Utilities, Public
Meeting Transcript, No. 43 at p. 62; CA
Utilities, No. 45 at p. 2) NEEA noted
that the source of the discrepancy
between DOE and NEMA data should be
determined before any efficiency levels
are fit to either data set. (NEEA, Public
Meeting Transcript, No. 43 at pp. 138–
9) Acuity Brands suggested DOE divide
its test data according to manufacturer
and compare it with the test data from
the individual manufacturers obtained
under non-disclosure agreements.
(Acuity Brands, Public Meeting
Transcript, No. 43 at p. 149)
ASAP suggested DOE continue to use
its own data for the final rule analysis
and any supplemental data provided by
manufacturers should be assessed in its
raw form to ensure comparability with
DOE data. (ASAP, No. 46 at p. 1) CA
Utilities also advised DOE to continue
to use its own test results for the final
rule unless it determined a specific fault
with the testing process of the labs used
by DOE. (CA Utilities, No. 45 at p. 4)
Following the May 2011 public
meeting, under non-disclosure
agreements, several manufacturers
provided the model numbers and
efficiencies for the ballasts included in
NEMA’s data set. Upon receiving this
information, DOE conducted a
comparative analysis between NEMA
data and DOE’s independently tested
data. DOE published the results of its
analysis in the August 2011 NODA.
DOE concluded that its data collection
methods were consistent with Appendix
Q1 of 10 CFR 430 and that, after
removing NEMA’s reduction factor as
discussed in section V.B.3.a, the
remaining differences between the two
data sets arise primarily from normal
measurement variation. Subsequent
comments received on the NODA
reaffirmed DOE’s conclusions.
Therefore, for this final rule, DOE
continued to use its own data and
utilized NEMA-provided data for
comparison. The sections below detail
DOE’s comparative analysis and discuss
several comments by interested parties
suggesting possible sources of
differences between the two datasets.
a. NEMA Reduction Factor
As described above, the data
contained in NEMA’s presentation at
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the May 2011 public meeting
represented the mean of four or five
samples decreased by 0.8 percent to
account for compliance certification
requirements. To calculate this 0.8
reduction factor, NEMA referred DOE to
an analysis NEMA submitted in a
comment in response to the preliminary
TSD. In that analysis, NEMA calculated
the 0.8 percent reduction factor based
on application of the certification
equation described in 10 CFR 429.26.
NEMA assumed that each sample set’s
three standard deviation spread was
equal to five percent of the mean
efficiency (2.5 percent for design
variation and 2.5 percent for
measurement variation). NEMA then
calculated a mean efficiency adjustment
factor (from sample sizes of four and
five) by inserting this standard deviation
into the certification equation. This
adjustment factor represented NEMA’s
estimate of the percent difference
between the sample mean and the value
NEMA anticipated reporting to DOE for
certification. CA Utilities commented
that NEMA’s reduction of its test results
by 0.8 percent may have been a
misinterpretation of the test procedure
and could have caused the discrepancy
between DOE’s and NEMA’s BLEs. (CA
Utilities, No. 45 at p. 2) ASAP agreed
that DOE should not directly compare
its data to NEMA’s reduced points.
(ASAP, No. 46 at p. 1)
In the August 2011 NODA, DOE
stated that to understand potential
discrepancies between NEMA and
DOE’s test data, it was necessary to
ensure that similar calculation
methodologies had been undertaken for
the two data sets. Therefore, for the
purpose of comparing the efficiency
data, DOE removed the 0.8 percent
reduction factor from NEMA’s presented
ballast efficiencies, resulting in values
that represented mean tested
efficiencies. DOE compared these
efficiency values to DOE’s mean tested
efficiencies presented in the April 2011
NOPR.
b. Arc Power Versus Rated Power
Due to the relationship between total
lamp arc power and ballast efficiency,
in the April 2011 NOPR, DOE proposed
establishing efficiency levels as
logarithmic equations dependent on
total lamp arc power. When NEMA
plotted their test data against the DOE
proposed efficiency levels, however,
NEMA paired their ballast efficiency
test data with approximated arc powers
rather than measured arc powers. CA
Utilities and NEEA and NPCC noted
that NEMA appeared to list a batch of
products all at the same ‘‘rated power,’’
and compared the performance of all of
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those products against the same BLE
standard. They stated that their
understanding was that standards are to
be calculated based on the measured
lamp arc power specific to each ballast,
not the rated lamp power. (NEEA and
NPCC, No. 44 at p. 5; CA Utilities, No.
45 at pp. 2–3)
DOE agrees that total lamp arc power,
measured in accordance with the active
mode test procedure, should be used
when comparing manufacturer-provided
data to DOE’s efficiency levels. In the
August 2011 NODA, DOE noted that the
lamp arc power associated with a
particular ballast in NEMA’s data was
an approximation rather than a test
result. DOE found NEMA’s
approximation to be higher than typical
test results in DOE’s data set, with
differences as high as 27.6 percent. As
this discrepancy could potentially cause
NEMA’s test data to appear to have
artificially lower efficiencies relative to
DOE’s efficiency levels, DOE revised
NEMA’s approximate lamp arc powers
using ANSI reference lamp arc powers
to calculate total expected lamp arc
power. 76 FR 52892, 52895–6 (August
24, 2011). These lamp arc powers better
aligned with expected total lamp arc
powers for similar ballast types. DOE
used these calculated powers when
comparing the efficiency levels to the
manufacturer-provided data as
discussed in section V.B.5.
c. Test Procedure and Lab Accreditation
NEMA commented that the difference
between the data it collected and DOE’s
results may be due to DOE’s labs not
having proper accreditation. NEMA
stated that all of the labs used for its
testing were certified according to ANSI
C82.11–2002 and DOE should only test
in similarly certified labs. NEMA
specifically noted that it did not believe
the Lighting Research Center (LRC) was
ANSI C82.11–2002 certified. (NEMA,
Public Meeting Transcript, No. 43 at pp.
30, 116) GE emphasized that labs should
be accredited in accordance with ISO
17025, which is a definition of
laboratory performance and
accreditation for test equipment and test
engineers using that equipment. (GE,
Public Meeting Transcript, No. 43 at p.
116) Similarly, CA Utilities suggested
that the difference between NEMA’s and
DOE’s test results could be because the
BLE test procedure is new and may
require clarification. (CA Utilities, No.
45 at p. 2)
DOE notes that 10 CFR 430.25
requires testing of fluorescent lamp
ballasts to be performed in accordance
with Appendix Q1 of 10 CFR part 430
Subpart B by test laboratories accredited
by National Volunteer Laboratory
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Accreditation Program (NVLAP) or a
NVLAP-recognized organization,
Underwriter Laboratories, or Council of
Canada in accordance with ISO 17025.
76 FR 25211, 25219 (May 4, 2011). ISO
17025 is an international standard that
outlines general requirements for the
competence of testing and calibration
laboratories. NVLAP operates an
accreditation system that requires
applicant laboratories to be assessed
against all ISO 17025 requirements.
As described in the August 2011
NODA, DOE contacted both test
laboratories utilized for DOE testing and
verified each is properly accredited and
that all testing was conducted in
accordance with the active mode test
procedure in Appendix Q1. CA Utilities
stated that this action greatly improved
the overall credibility of DOE’s dataset.
(CA Utilities, No. 58 at pp. 1–2) Given
the verification of data collection
methods, DOE continues to use its own
data in this final rule.
d. Sample Size
NEMA also commented that the
number of samples tested for several
ballast models was too small,
potentially resulting in test data
unrepresentative of the mean
efficiencies of the ballast model’s
population. They pointed out that about
60 percent of DOE’s test data
represented an average efficiency
calculated with fewer than four
samples, which is less than the
minimum number of samples required
to demonstrate compliance with DOE’s
standards. (NEMA, No. 52 at p. 9) CA
Utilities also stated that if possible, DOE
should conduct testing of four or more
samples to more accurately reflect the
testing process that must be completed
by manufacturers for compliance. (CA
Utilities, No. 45 at p. 3)
Since the publication of the April
2011 NOPR, DOE has conducted
additional testing to increase the sample
size of selected ballast models. More
than 90 percent of tested ballast models
now have a minimum of four samples.
Only in those cases where models have
been discontinued or were unavailable
for purchase was DOE unable to test a
minimum of four samples. DOE posted
a complete set of test data on its Web
site at the time the August 2011 NODA
was published.
CA Utilities and NEEA and NPCC
commended DOE for conducting
additional testing to increase the sample
size to a minimum of four ballast
samples, consistent with the
certification requirements in 10 CFR
429.26. NEEA and NPCC stated that the
additional testing conducted improved
the dataset’s accuracy and credibility,
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which contributed to the development
of appropriate standard levels. (CA
Utilities, No. 58 at p. 2; NEEA and
NPCC, No. 59 at p. 2) DOE discusses
how it utilized all available data in
sections V.B.4 and V.B.5.
e. Measured Versus Calculated BLE
In response to the April 2011 NOPR,
NEMA commented that it found several
samples of DOE test data in which the
measured BLE reported in appendix 5C
of the NOPR TSD was not consistent
with the BLE calculated by NEMA.
Though some of the differences were
small, NEMA provided examples of four
ballast models with differences up to
8 percent. (NEMA, Public Meeting
Transcript, No. 43 at pp. 28–9) DOE
addressed these discrepancies in the
August 2011 NODA.
For the small discrepancies identified
by NEMA, DOE noted that the
information provided by NEMA was
consistent with calculating the BLE
values by dividing the average arc
power of all samples by the average
input power of all samples. This method
is not consistent with the active mode
test procedure. In contrast, DOE’s
average BLE reported in appendix 5C of
the TSD was determined, as required in
the test procedure, by averaging the BLE
of each individual sample. Based on
DOE’s analysis, this difference in
methodology accounts for the small
discrepancies observed between the
values reported in appendix 5C and
those calculated by NEMA.
DOE also worked to resolve the large
differences cited by NEMA. DOE
identified six samples with measuredversus-calculated BLE differences
ranging from 7.8 to 8.0 percentage
points, which included the specific
examples cited by NEMA. These six
samples were all magnetic ballasts; in
accordance with the active mode test
procedure (see Table A, Appendix Q1 of
10 CFR part 430 Subpart B), DOE
calculated BLE for these samples by
reducing the measured ballast efficiency
(total lamp arc power divided by ballast
input power) by a frequency adjustment
factor (1.00 for high-frequency ballasts
and values ranging from 0.93 to 0.95 for
low-frequency ballasts). These larger
discrepancies are consistent with NEMA
not including this adjustment factor in
its calculation of BLE. Thus, given the
above explanation and the absence of
any additional comments regarding this
subject, DOE’s measured BLE values are
correctly calculated and consistent with
the active mode test procedure.
f. Ballast Factor
NEMA also identified differences in
appendix 5C of the NOPR TSD between
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catalog and tested values for ballast
factor, in some cases as large as 10 or
15 percent. NEMA reported that based
on its own tests, it would expect the
average difference between catalog BF
and tested BF to be 1.5 percent. (NEMA,
Public Meeting Transcript, No. 43 at pp.
27–8) DOE acknowledges that there
might be differences between ballast
factor values reported in catalogs and
DOE’s test data. Catalogs generally
report ballast factor using the procedure
in Appendix Q of 10 CFR part 430
subpart B, which requires photometric
measurements. DOE calculated ballast
factor in the April 2011 NOPR using
electrical measurements by measuring
the lamp arc power for the test ballast
and dividing it by the reference lamp
arc power as specified by ANSI
standards. Available information
suggests that manufacturing variation,
coupled with application of a different
test procedure to determine BF,
accounts for the difference between
catalog BF and DOE measured BF.
Because DOE did not establish product
classes or standards using BF and the
active mode test procedure final rule
did not adopt a new method for its
calculation, however, ballast factor is
not relevant to this rulemaking.
g. Variation Within DOE’s Data
Stakeholders also questioned the
variation present within DOE’s data and
offered several suggestions on how to
measure variation within the test
results. Lutron and NEMA suggested
DOE perform a gauge repeatability and
reproducibility (R&R) analysis, a
recognized technique to reconcile
differences among measurements.
(Lutron, Public Meeting Transcript, No.
43 at pp. 118–9; NEMA, Public Meeting
Transcript, No. 43 at p. 121) Philips
suggested that DOE look at the variation
among each unit and among each lab,
and then use the total variation to
conduct a 3-sigma 36 analysis. Philips
noted, however, that three samples is
not a very statistically large sample size
in examining this kind of variation.
(Philips, Public Meeting Transcript, No.
43 at p. 113)
As described in the previous sections,
DOE evaluated several factors to verify
the integrity of its data. DOE has
confirmed that testing was conducted in
accordance with the active mode test
procedure and that its calculations of
BLE are accurate. Furthermore,
additional testing has increased sample
size such that it is consistent with
36 3-sigma is a statistical calculation that refers to
data within three standard deviations from a mean.
It is based on the rule that for a normal distribution,
nearly all values lie within three standard
deviations of the mean.
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compliance certification requirements.
After accounting for the above items,
DOE believes that variation in its data
reflects expected measurement, design,
and lab-to-lab variation. DOE addresses
these sources of variation in the
following sections.
4. Accounting for Variation and
Compliance Certification Requirements
In the April 2011 NOPR, DOE
accounted for lab-to-lab variation and
compliance certification requirements
by calculating reduction factors for each
and adjusting the efficiency levels
accordingly. DOE calculated a 0.6
percent reduction factor for lab-to-lab
variation by comparing the data from
the primary laboratory, which
conducted the majority of DOE’s testing,
with data from its secondary laboratory,
which tested a limited number of
identical samples. DOE applied the 0.6
percent lab-to-lab variation reduction to
the efficiency curves so that the
standard level could, on average, be met
by ballasts tested at the less efficient lab.
To account for certification
requirements, DOE calculated the
difference between the output of the
compliance certification equation in 10
CFR 429.26 and the sample mean of
DOE’s test data to be 0.2 percent. As
DOE’s certification requirements at 10
CFR 429.26 require manufacturers to
report the lower of these two values,
DOE reduced the efficiency levels,
based on average BLEs, by this value.
OSI and Lutron Electronics Co., Inc.
(Lutron) commented that in addition to
lab-to-lab variation, both design and
measurement variation need to be taken
into account when setting a standard to
make sure that the average of different
tested samples will meet the minimum
BLE requirements. OSI commented that
design tolerances exist because different
components are used in different
production runs. OSI estimated this
variation to be about two percent. (OSI,
Public Meeting Transcript, No. 43 at pp.
137–8, 152; Lutron, Public Meeting
Transcript, No. 43 at pp. 151–2)
NEMA submitted analyses in
response to the NOPR recommending
modifications to DOE’s methodology of
accounting for certification
requirements and variation. NEMA’s
first analysis used an assumed design
variation and measurement variation
(each 2.5 percent) in the compliance
certification equation to adjust each
ballast efficiency data point. After
analyzing the more detailed set of data
posted after the May 2011 public
meeting, NEMA submitted a similar
analysis but used an assumed design
variation and a calculated measurement
variation. NEMA then suggested that
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DOE base its efficiency levels on the
adjusted data points rather than mean
BLE values. Specifically, NEMA
determined the mean BLE for each
ballast model by averaging all tested
values of that particular model. NEMA
then calculated the maximum
measurement variation across labs for
each category of fluorescent lamp ballast
(e.g., 4-foot MBP, 4-foot MiniBP, or
8-foot high output). NEMA added this
highest calculated measurement
variation for each ballast type to a 2.5
percent assumed design tolerance to
characterize the total variation. NEMA
then entered these variations into the
compliance equation to calculate a
reduction factor based on sample size of
each tested model. NEMA commented
that DOE should make similar
allowances in the standard levels to
account for the variation present in
DOE’s own data. (NEMA, No. 52 at pp.
8–10)
The CA Utilities also conducted an
analysis using the data DOE provided
following the May 2011 public meeting.
They agreed with NEMA that
compliance certification requirements
should be considered when assessing
whether products will meet each
standard level. However, they pointed
out that NEMA had employed methods
to characterize the certification
procedures that were not consistent
with the requirements specified in 10
CFR 429.26. Instead, the CA Utilities
used individual samples of DOE’s
efficiency data to calculate both the
sample mean and the value determined
by the compliance certification equation
in 10 CFR 429.26. Then, as directed by
the compliance certification regulations,
they represented the reported efficiency
as the lower of the two values. They
suggested that DOE base its efficiency
levels on these reported values. (CA
Utilities, No. 45 at pp. 3, 4–5)
Consistent with the April 2011 NOPR,
DOE recognizes the importance of
considering the variation present in the
test data when developing efficiency
levels. DOE acknowledges that due to
design and measurement variation, the
reported value for compliance
certification may deviate from the
sample mean and this difference must
be accounted for. As described in the
following sections, DOE has modified
its approach to account for variation and
compliance certification procedures
based on the comments provided.
a. Design Variation and Compliance
Certification Requirements
As stated earlier, 10 CFR 429.26
requires manufacturers to test a
minimum of four fluorescent lamp
ballasts and report the lower of either
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the mean efficiency of the samples or
the output of a compliance certification
equation based on the lower 99 percent
confidence limit of the sample. The
lower 99 percent confidence limit
equation requires a calculation of the
standard deviation of the sample set to
account for measurement variation.
Because over 90 percent of ballast
models tested by DOE include samples
obtained during two different years, the
standard deviation for these models also
incorporates design variation that is
present in the sample set.
Both NEMA and the CA Utilities had
previously commented that, in order to
develop efficiency levels, DOE should
adjust its mean efficiency data points to
represent values similar to those
manufacturers would report to DOE for
compliance certification. However, their
approaches differed in how they
computed the standard deviation input
for the compliance certification
equation. The CA Utilities calculated
the standard deviation among all
samples of a particular ballast model
tested at a single lab. NEMA, however,
calculated the standard deviation by
assuming a 2.5 percent design variation
and then adding an additional factor
based on DOE’s lab-to-lab test data for
each ballast category.
In the August 2011 NODA, DOE
disagreed with NEMA’s method of
applying the compliance certification
requirements. First, the compliance
requirements direct manufacturers to
calculate the standard deviation of the
tested sample, rather than an assumed
population standard deviation. Second,
in practice, this calculation would likely
not include data from more than one lab
unless manufacturers chose to test their
samples of a single ballast model at
more than one location. DOE agreed that
lab-to-lab variation was important, but
considered accounting for it as a
separate adjustment to efficiency levels
as discussed below in section V.B.4.b.
The CA Utilities evaluated both the
sample mean and compliance equation
for each ballast model and compared the
lower of the two, the reported value, to
the standard level. DOE believed the CA
Utilities’ approach for accounting for
compliance certification requirements
was consistent with the procedures laid
out in 10 CFR 429.26 and therefore, in
the August 2011 NODA, considered
using this methodology for the final
rule. To facilitate this approach, as
discussed earlier, DOE conducted
additional testing after publication of
the NOPR to increase the sample size of
several ballast models in accordance
with compliance certification
requirements. To account for these
requirements, DOE calculated a new
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data set that represented the reported
value for all ballast models. DOE used
these reported values to develop the
efficiency levels described in the August
2011 NODA.
CA Utilities and NEEA and NPCC
supported DOE’s methodology of
accounting for certification
requirements when setting standard
levels. They stated that the use of
reported values accounts for design
variation within a product line and
measurement variation among multiple
test runs within a single lab. These
organizations also commented that this
approach is more accurate than DOE’s
previous proposal to apply a 0.2 percent
reduction to all efficiency levels. (CA
Utilities, No. 58 at p. 2; NEEA and
NPCC, No. 59 at p. 2)
NEMA, however, disagreed with the
methodology presented in the August
2011 NODA. Specifically, NEMA
claimed that the correction factor they
calculated is essential to account for
manufacturing and component variance.
NEMA commented that because DOE’s
samples were acquired when market
demand was low, the manufacturing
variation present in DOE’s test data was
not representative of typical variation.
They reasoned that manufacturers could
be more selective when purchasing
components for products manufactured
during that time period. Under normal
market conditions, manufacturers
compete for the same component supply
and often obtain parts that vary in
quality and cost. NEMA commented
that DOE should have tested a
statistically representative sample set
for each model (i.e., a larger sampling
from multiple productions lots,
assembled over time) and that, absent
this, DOE should have used a
statistically derived method for
determining an appropriate reduction
rather than empirical data. (NEMA, No.
56 at pp. 2, 4)
As described previously, DOE
believes that NEMA’s recommended 0.8
percent reduction does not reflect
appropriate certification procedures. As
stated in 10 CFR 429.26, manufacturers
are required to evaluate the certification
equation using the standard deviation of
the samples tested, not the expected
variation in the population.
Furthermore, NEMA included lab-to-lab
variation when calculating its reduction
factor. This calculation would likely not
include data from more than one lab,
however, unless manufacturers chose to
test their samples of a single ballast
model at more than one location. In
addition, NEMA utilized a normal
distribution critical value for the 99th
percentile rather than the specified
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t-statistic for the 99th percentile in
evaluating the compliance equation.37
As explained in the preceding
paragraphs, DOE considered both design
variation and certification requirements
when developing efficiency levels using
the methodology presented in the
August 2011 NODA. DOE purchased
samples over several years,
encompassing more than one
production lot. While NEMA states that
DOE purchased samples at a time when
manufacturers could easily obtain the
most efficient components, DOE also
purchased ballasts (for the purpose of
increasing sample size) during years in
which interviewed manufacturers stated
that they faced component shortages.
Furthermore, consistent with 10 CFR
429.26, over 90 percent of models tested
had a sample size of 4 or more. For
these reasons, DOE continues to use the
methodology described in the August
2011 NODA in this final rule.
NEMA commented that half of all
borderline but compliant products will
fail to meet the standard if an
adjustment factor is calculated using
average empirical data, such as DOE’s
method described above. (NEMA, No.
56 at p. 2) DOE notes that the
certification requirements do not
mandate that every sample tested must
meet or exceed the standard level, rather
they require that the average of the
tested samples meet or exceed the
standard. A compliant product may still
have samples that test below the
standard, provided that the average BLE
meets or exceeds the level adopted in
this final rule. NEMA’s concern may be
regarding a situation where all ballast
samples are selected from a production
run in which lower-quality components
cause all samples to test at the lower
end of the expected range attributable to
design variation. However, there is no
requirement that all samples be selected
from the same production run. In fact,
10 CFR 429.26 states that samples
should be randomly chosen.
Manufacturers can also choose to test
more than the minimum number of
samples to address concerns about a
borderline product.
b. Lab-to-Lab Variation
As described in section V.B.1, DOE
accounted for lab-to-lab variation in the
April 2011 NOPR by comparing data
from two different labs and calculating
a 0.6 percent reduction factor to apply
to efficiency levels. NEMA noted that
37 The compliance equation found in 10 CFR
429.26 requires the use of a t-statistic, to calculate
the reported value. NEMA used a different
statistical distribution, the standard normal
distribution, in the calculation of its reduction
factor.
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DOE’s data showed significant variation
between labs and stressed the
importance of accurately quantifying
this variation. (NEMA, Public Meeting
Transcript, No. 43 at pp. 140–1) NEMA
pointed out that DOE typically only
used one lab to make measurements
rather than validating variation using
multiple labs. (NEMA, No. 52 at p. 7)
Philips suggested that, after evaluating
data among multiple labs, DOE should
apply a reduction representative of the
maximum variation present in the data
rather than average variation. (Philips,
Public Meeting Transcript, No. 43 at p.
113–5)
In the August 2011 NODA, DOE
considered revising its methodology to
account for lab-to-lab variation. DOE
received test data from NEMA following
the May 2011 public meeting and also
received test data from NEMA-member
manufacturers. The information from
manufacturers allowed DOE to match
NEMA test data with the same ballast
models tested at DOE’s primary and
secondary labs. Using the modelspecific test data supplied by
manufacturers (representative of three
different manufacturer labs) and DOE’s
BLE data (representative of the two labs
used by DOE), DOE determined that on
average, the BLE test data from DOE’s
primary lab was 0.7 percent more
efficient than the average test lab. DOE
attributed this offset to systematic labto-lab variation and therefore
considered reducing the efficiency
levels by 0.7 percent so that they are
representative of ballasts tested at the
average test lab. This approach was
slightly different than that taken in the
April 2011 NOPR, which applied a 0.6
percent reduction to efficiency levels,
representing the average offset between
DOE’s primary lab and the least efficient
lab (in that case, DOE’s secondary lab).
DOE believed that adjusting efficiency
levels so that they represent the average
test lab better characterized the mean
performance of products currently being
sold.
CA Utilities, NEEA, and NPCC
commented that DOE should not use
NEMA’s data to calculate lab-to-lab
variation. CA Utilities stated that
because NEMA provided an
approximation for arc power instead of
measured arc power, their data is not
useful for assessing lab-to-lab variation.
They suggested DOE use its own data
from the primary and secondary test
labs to quantify this type of variation.
(CA Utilities, No. 58 at p. 2; NEEA and
NPCC, No. 59 at p. 2)
DOE believes that NEMA’s data
reflects correct application of the active
mode test procedure, given confidential
data received from individual
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manufacturers and NEMA’s description
of testing provided during the public
meeting. (NEMA, Public Meeting
Transcript, No. 43 at p. 51) Although
interested parties expressed concern
that NEMA did not provide the
measured lamp arc power for each
model, DOE notes that its approach for
calculating lab-to-lab variation does not
incorporate measured lamp arc power.
Rather, DOE directly compares the BLE
for a given ballast model to the BLE
provided by NEMA for the same model.
Although some stakeholders suggested
that DOE only utilize its own results,
DOE believes it should incorporate all
available data. By doing so, the number
of labs included in the calculation
increases from two to five and the
number of models available for
comparison between labs increases as
well. Therefore, DOE maintains the
methodology described in the August
2011 NODA for this final rule.
5. Efficiency Levels
a. Curve Shape
As described in section V.B.1, DOE
concluded in the April 2011 NOPR that
a logarithmic relationship best modeled
the observed trend between total lamp
arc power and BLE and therefore
proposed efficiency levels using this
equation form. Several manufacturers
commented that, based on the test data
they collected, the shape of the
proposed efficiency levels was not a
good fit for all commercially available
products. GE commented that it found
larger discrepancies between its test
data and minimum BLE requirements
for ballasts with lower input power than
higher input power. GE reported that
none of its ballasts met the proposed
standard efficiency in the low power
range. (GE, Public Meeting Transcript,
No. 43 at p. 58) NEMA also noted that
at approximately 80 W and below, very
few manufacturers had products
meeting the programmed start minimum
BLE requirements. (NEMA, Public
Meeting Transcript, No. 43 at pp. 66–7;
NEMA, No. 47 at p. 6) NEMA suggested
an alternative equation in which they
increased the natural log constant and
decreased the additive constant to
increase the curvature of the proposed
standard and better fit the dataset.
(NEMA, Public Meeting Transcript, No.
43 at p. 59) NEMA also recommended
breaking up the power ranges into
separate product classes to have the
formulas fit the test data better and
suggested a breaking point somewhere
in the 50 to 100W range. (NEMA, Public
Meeting Transcript, No. 43 at pp. 75–6)
Acuity Brands expressed concern that
DOE was not considering can size when
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ballasts with small can sizes to remain
on the market.
Stakeholders had provided comments
on a potential new equation form during
the May 2011 public meeting, when
DOE presented a power law equation fit
to the data provided by NEMA. Several
manufacturers commented that upon
initial review, the new power law
equation appeared to be a better fit to
the NEMA data. (Philips, Public
Meeting Transcript, No. 43 at pp. 136–
7, NEMA, No. 47 at p. 3 OSI, Public
Meeting Transcript, No. 43 at pp. 137–
8) NEMA further stated that the
logarithmic equation in the April 2011
NOPR was more stringent at lower
wattages relative to higher wattages. A
lower wattage ballast’s efficiency is
more affected by fixed losses than a
higher wattage ballast. The new power
law equation seemed to accommodate
this difference in efficiency (NEMA, No.
47 at p. 11)
NEEA and NPCC supported the use of
a logarithmic equation dependent on
lamp arc power and based on the data
presented by DOE in the April 2011
NOPR. However, NEEA and NPCC
noted that the NEMA data does have a
different shape and could be better fit by
the power law equation presented
during the May 2011 NOPR public
meeting. The CA Utilities agreed, stating
that the data supported the new curve
shape. (NEEA and NPCC, No. 44 at p.
4–6; CA Utilities, No. 45 at p. 5–6)
Based on an application of several
equation forms for efficiency levels,
DOE concluded in the August 2011
NODA that a power law equation fit
both the NEMA data and DOE data
better than the logarithmic relationship
proposed in the April 2011 NOPR. A
power law equation takes the form:
different exponent for ballasts that use
the PS starting method. PS ballasts have
proportionately higher fixed losses due
to internal control circuitry and heating
of lamp electrodes (cathode heating). As
such losses are a larger proportion of
total losses at lower powers, the PS
product classes have a steeper slope
across the range of wattages
corresponding to a larger exponent ‘‘C’’
of 0.37.
Once the exponents were established
for the two starting method categories,
DOE fit the power law equation to the
reported value data (calculated in
accordance with 10 CFR 429.26 as
discussed in section V.B.4) by adjusting
the coefficient ‘‘B’’ to delineate among
criteria such as different product lines,
lines, ballasts that operate different
lamp types, and other clusters in
efficiency data. The most efficient
(maximum technologically feasible) ELs
approximate the April 2011 NOPR
proposals for the highest wattages, but
better follow product line efficiency
trends at lower wattages. DOE
confirmed the impacts of efficiency
levels considered in the August 2011
NODA by comparing the levels to both
DOE’s and NEMA’s data.
In subsequent comments, NEMA
supported the use of a power law
equation to develop efficiency levels.
The exponent ‘‘C’’ determines the
shape of the equation. Because NEMA’s
test data included a greater number of
low wattage ballasts, DOE determined
the exponent ‘‘C’’ by fitting a power law
regression to NEMA’s data. For the IS/
RS product class (product class 1 in
Table V.1), DOE found the exponent
‘‘C’’ to be 0.25. The exponent 0.25 is
also a quantity used in relating power to
relative losses (analog of efficiency) for
distribution transformers, and
fluorescent lamp ballasts similarly
employ transformers and inductors. The
PS NEMA data, however, yielded a
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transportation costs. (NEMA, Public
Meeting Transcript, No. 43 at pp. 32–3,
35–7; Acuity Brands, Public Meeting
Transcript, No. 43 at pp. 99–100, 107–
9, 171–2)
CA Utilities and NEEA and NPCC
commented that lower standards are not
needed to accommodate ballasts of the
smallest can size, and CA Utilities noted
that they were not aware of any unique
utility provided by N-cans. CA Utilities
also stated that NEMA had not
presented data demonstrating that Ncans are less efficient than A-cans or
that smaller can size can reduce the use
of steel. (CA Utilities, No. 45 at p. 6)
NEEA and NPCC strongly urged the
Department to proceed with the
proposed standards unless conclusive
data is presented on these issues that
would suggest a different standard is
warranted. (NEEA and NPCC, No. 44 at
p. 8–9)
Upon analysis, NEMA’s test data
showed a larger efficiency decrease at
lower wattages than DOE’s data
indicated. Although DOE and NEMA
generally tested the same types of
ballasts, NEMA tested more
permutations of ballast factor and
number of lamps for each product line,
particularly at lower wattages. For
example, NEMA’s data contained BLE
values for 1-lamp 4-foot MBP ballasts
with both low and high ballast factors,
whereas DOE’s data included 1-lamp 4foot MBP ballasts with only normal
ballast factors. For these reasons, in the
August 2011 NODA, DOE considered
changing the contour of the efficiency
levels to better fit all of the available
data. DOE acknowledges that industry is
migrating to smaller can sizes, and the
methodology described below allows
Where: power = average total lamp arc
power.
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determining what types of ballasts met
proposed standards. NEMA reported
that consumer demand has moved the
ballast market into smaller can sizes,
specifically to A- and N-cans, from Fcans. NEMA stated that three
representative ballast types in A-cans
currently make up 80 percent of the
total U.S. market, and the market is in
the process of migrating to even smaller
N-cans. NEMA explained that smaller
ballasts enable reduced fixture size and
plenum height in buildings. Not only is
this convention in accordance with
green building practices, but smaller can
sizes allow for a reduction of gas and
waste, and a 10 to 15 percent reduction
of steel in the manufacturing process.
NEMA and Acuity Brands added that
the smaller can sizes also increase the
photometric efficiency of the fixture by
two to six percent (for fixtures housing
an A-can compared to an F-can). The
small can allows better optical control
and fuller use of the reflector as the
thinner ballast housing blocks less light
than larger cans. The smaller ballasts are
also easier to access in the event that the
ballast needs replacing. The limited
space constrains the technology and
components used, however, limiting
possible efficiency gains. NEMA argued
that, given the size of A- and N-cans,
industry is currently developing the
highest practical efficiency with NEMA
Premium products. NEMA emphasized
that while ballasts in the larger F-can
can have higher efficiencies, consumer
demand and fixture design makes
moving to larger cans unsustainable.
Acuity Brands asserted that if standard
levels eliminate the smaller can sizes,
DOE must, in its analysis, account for
the additional costs of fixture redesign,
engineering time, and incremental
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(NEMA, No. 56 at p. 3) DOE received no
adverse comment regarding this
approach, and therefore maintains the
use of this equation form for the final
rule.
b. Max Tech Ballast Efficiency
As described in the April 2011 NOPR
and appendix 5D of the NOPR TSD,
DOE was not able to identify any
working prototypes with efficiencies
higher than those of commerciallyavailable ballasts. DOE therefore
established the maximum
technologically feasible efficiency level
as the highest level that is
technologically feasible for a sufficient
diversity of commercially available
products (spanning several ballast
factors, number of lamps per ballast,
and types of lamps operated) within
each product class.
NEEA and NPCC agreed that no
additional information suggests that
higher efficiency levels exist above the
most efficient levels analyzed for each
product class in the April 2011 NOPR.
(NEEA and NPCC, No. 44 at p. 6) NEMA
reiterated this point by commenting that
there were no improvements possible
over the level of efficiency proposed by
DOE in the April 2011 NOPR. NEMA
stated that electronic ballasts perform
functions that require some fixed level
of power consumption including:
Switching losses related to power
conversion from AC to DC and back to
AC, cathode preheating, striation
control, and end of life protection.
NEMA commented that using lower loss
switches would increase cost
dramatically, and that lower loss
magnetic components would necessitate
an overall increase in ballast size, which
the market would not accept. (NEMA,
No. 47 at pp. 6–7)
The CA Utilities, NEEA and NPCC,
and the second Joint Comment
commented that the max tech levels
could be more stringent for higher
wattage ballasts such as those that
operate four 4-foot MBP lamps. They
noted that among the 4-lamp 4-foot MBP
IS/RS ballasts tested by DOE, a high
percentage met the max tech level, and
there was typically a greater range of
efficiency among those ballasts that met
the standard. (CA Utilities, No. 45 at p.
5–6; Second Joint Comment, No. 57 at
p. 1; CA Utilities, No. 58 at p. 3; NEEA
and NPCC, No. 59 at p. 2)
DOE determined the max tech level
for today’s final rule to be the highest
level that is technologically feasible for
a sufficient diversity of lamp types,
ballast factors, and numbers of lamps,
regardless of manufacturer. DOE
developed EL3 for the IS/RS product
class in accordance with this criteria.
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For some ballast types in this class,
there is only one product available at
the max tech level and therefore raising
this level would remove these products
from the marketplace. Therefore, DOE
has concluded that EL3 represents the
highest level for the IS/RS product class
that is technologically feasible for a
sufficient diversity of products and
maintains this level for the final rule.
The following sections describe the
impact of each efficiency level in more
detail.
c. IS and RS Ballasts
DOE developed three efficiency levels
for the IS/RS product class. The least
efficient level (EL1) was designed to
eliminate 4-foot MBP T12 ballasts while
allowing 4-foot MBP T8 and 8-foot
slimline ballasts to comply with energy
conservation standards. EL2
corresponds to a level which allows the
highest-efficiency product lines from
each of the four major ballast
manufacturers to comply. DOE defines a
full product line as spanning a sufficient
diversity of products (spanning several
ballast factors, numbers of lamps per
ballast, and types of lamps operated).
EL3 is the maximum technologically
feasible level and allows nearly two
manufacturer product lines comply.
d. PS Ballasts
DOE developed three efficiency levels
for the PS product class (product class
number 2 in Table V.1). The least
efficient level (EL1) was designed to
eliminate the least efficient 4-foot MBP,
4-foot T5 standard output, and 4-foot T5
high output PS ballasts. This also
corresponds to a level at which each of
the four major fluorescent lamp ballast
manufacturers maintain a diversity of
products. EL2 allows full product lines
from two major manufacturers. Finally,
EL3, the maximum technologically
feasible level, was designed to represent
the most efficient PS ballasts tested by
DOE. EL3 is the highest level that allows
one full line of products to meet
standards, regardless of manufacturer.
e. Eight-Foot HO Ballasts
For the 8-foot HO IS/RS product class
(product class 3 in Table V.1), DOE
developed three efficiency levels. For
this product class, DOE tested ballasts
that operate two lamps, the most
common lamp-and-ballast combination.
EL1 was designed to just allow the least
efficient T12 electronic ballasts,
eliminating magnetic ballasts. EL2
allows the least efficient T8 ballast
tested and eliminates the vast majority
of T12 electronic ballasts. Finally, EL3
was designed to just allow the most
efficient T8 ballast tested by DOE.
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f. Sign Ballasts
The sign ballast market is primarily
comprised of magnetic and electronic
ballasts that operate T12 HO lamps.
DOE tested sign ballasts that operate up
to one, two, three, four, or six 8-foot T12
HO lamps. The test data showed that
sign ballasts exist at two levels of
efficiency. Therefore, DOE analyzed a
baseline and one efficiency level above
that baseline. EL1 was designed to allow
a full line of electronic sign ballasts,
including ballasts that operate up to six
8-foot HO lamps.
g. Residential Ballasts
In the April 2011 NOPR, DOE had
proposed that both residential and
commercial ballasts could achieve
similar levels of efficiency at the highest
levels analyzed. Based on the similarity
in efficiency, DOE included both ballast
types in the same product class.
However, for the final rule, DOE
conducted additional testing which
indicates that 4-lamp residential ballasts
are not able to achieve the same levels
as commercial ballasts. Therefore, DOE
has established a separate product class
for residential ballasts and adjusted the
efficiency levels for these ballasts to
reflect the new data. EL1 was designed
to just allow the least efficient T8 MBP
ballasts, eliminating T12 residential
ballasts. EL2, the maximum
technologically feasible level, is the
highest level that allows a full range of
T8 products (including both two- and
four-lamp ballasts) to comply.
6. Representative Units
a. Baseline Ballasts
For each ballast type analyzed, DOE
selected a baseline ballast from which to
measure improvements in efficiency.
Baseline ballasts are what DOE believes
to be the most common, least efficacious
ballasts for each representative ballast
type. For ballasts subject to existing
Federal energy conservation standards,
a baseline ballast is a commercially
available ballast that just meets existing
standards and provides basic consumer
utility. If no standard exists for that
specific ballast type, the baseline ballast
represents the most common ballast
sold within a representative ballast type
with the lowest tested ballast luminous
efficiency. In cases where two types of
ballasts (each operating a different lamp
diameter) are included in the same
representative ballast type, DOE chose
multiple baseline ballasts.
NEMA commented that magnetic
ballasts should not be used as baselines.
(NEMA, Public Meeting Transcript, No.
43 at pp. 38–9). DOE notes that while
magnetic ballasts are not appropriate
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baselines for the majority of ballast
types, for certain ballast types they
represent the most common, least
efficient ballasts that meet existing
energy conservation standards. For
example, as most magnetic 4-foot MBP
and 8-foot slimline ballasts do not meet
the BEF standards set forth by the 2000
Ballast Rule and EPACT 2005, DOE
chose electronic baselines for these
ballast types. DOE used a magnetic
ballast as a baseline for 8-foot HO
ballasts, however, because a T12
magnetic ballast represents the least
efficient ballast that meets existing
energy conservation standards.
Consistent with projections that a
significant portion of 8-foot HO ballasts
sold in 2014 (the compliance year of the
new and amended standards in this
final rule) will be electronic T8HO
ballasts, DOE analyzes a T8 electronic
ballast as a second baseline for this
ballast type. DOE also used a magnetic
ballast as a baseline for sign ballasts,
which is typical of the least efficient
products that are commercially
available. In addition, according to
DOE’s shipment estimates, magnetic
ballasts constitute a significant portion
of the sign ballast market. For these
reasons, DOE continues to analyze both
electronic and magnetic baselines for
the 8-foot HO and sign representative
ballast types in this final rule.
While NEAA and NPCC supported the
use of T12 ballasts as an analytical
baseline, EEI reasoned that due to the
2009 Lamps Rule, only T8 lamps will be
able to comply with the new lamp
efficacy standards. Therefore, T8 lampand-ballast systems will be the baseline
(in terms of product availability) for all
consumers as of July 2012. (NEEA and
NPCC, No. 44 at p. 6; EEI, No. 48 at
p. 2)
DOE has concluded that both T8 and
T12 ballasts are appropriate baselines.
Although many T12 lamps will not meet
the standards adopted in the 2009
Lamps Rule, several manufacturers have
already introduced T12 lamp models
that are not covered by these standards.
Therefore, DOE projects that T12
products will be offered in 2014, the
compliance year for this rulemaking.
For example, DOE projects that in 2014
shipments (in the base case with
existing technologies), while T8 ballasts
will have a 78 percent market share, T12
ballasts will still have a market share of
4 percent of covered shipments, or
about 5.3 million ballasts.38 Thus, DOE
continues to use T12 ballasts as
baselines in this final rule.
38 T5 ballasts comprise the remaining market
share.
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b. Representative Units
DOE then selected representative
units at each efficiency level with
higher BLEs as replacements for each
baseline ballast. Representative units are
typically ballasts that just meet the EL
requirements based on the
representative units’ lamp arc power.
Because DOE revised the shape of the
efficiency levels, it also reevaluated its
selection of representative units. DOE
selected three new representative units
based on the revised EL requirements.
The revised representative units
included the EL3 units for 2-lamp 4-foot
MBP and 2-lamp 8-foot slimline ballasts
in the IS/RS product class, and the EL2
unit for 2-lamp 4-foot MBP ballasts in
the residential IS/RS product class. See
chapter 5 of the TSD for more details.
c. Reduced Wattage Lamps
In the April 2011 NOPR, DOE paired
each ballast with a representative lamp
type to develop system input power and
lumen output characteristics for use in
the LCC and NIA. Based on the active
mode test procedure for fluorescent
lamp ballasts, DOE used full wattage
lamps for T8 and T5 ballasts and
reduced wattage lamps for T12 ballasts.
For example, for ballasts that operate 4foot MBP lamps, DOE paired an F32T8
lamp with T8 ballasts and an F34T12
lamp with T12 ballasts. NEMA
commented that due to the prevalence
of energy-saving lamps in the market
today, the standard 32 watt lamp is not
an appropriate selection for the 4-foot
MBP T8 system. (NEMA, Public Meeting
Transcript, No. 43 at pp. 38–9)
DOE agrees that all ballasts do not
operate full-wattage lamps and thus
revised the engineering analysis to
incorporate the distribution of full- and
reduced-wattage lamps on the market.
In the 2009 Lamps Rule, DOE estimated
the distribution of lamps by wattage that
would be compliant with the 2012
energy conservation standards. For this
final rule, DOE used those distributions
to develop weighted-average lamp
wattages (e.g., a rated wattage of 30.8 W
for 4-foot MBP T8 lamps) to pair with
T8 and T5 ballasts. In addition, DOE
also updated the ballast luminous
efficiency, system input power, system
lumen output, lamp lifetime, and lamp
price to reflect the distribution of lamp
wattages. See chapter 5 of the final rule
TSD for additional details.
7. Scaling to Product Classes Not
Analyzed
In the April 2011 NOPR, DOE did not
analyze 8-foot HO PS ballasts directly.
Thus, it developed a scaling
relationship for this starting method. To
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do so, DOE compared 4-foot MBP IS
ballasts to their PS counterparts. DOE
found the average reduction in BLE
from IS to PS to be 2 percent and
therefore applied this reduction to the
efficiency levels for the 8-foot HO IS/RS
product class.
P.R. China found this approach
potentially lacking scientific basis and
suggested DOE provide a more detailed
explanation of its methodology. (P.R.
China, No. 51 at p. 4) As discussed in
section V.B.6, DOE identified and
selected certain product classes as
‘‘representative’’ product classes where
DOE would concentrate its analytical
effort. DOE chose these representative
product classes and the representative
units within them primarily because of
their high market volumes. DOE then
scaled from these representative classes
to those not directly analyzed. In the
NOPR, DOE calculated a 2 percent
reduction factor to scale between IS/RS
and PS product classes. This factor was
determined by comparing pairs of
ballasts in which the only characteristic
that differed was starting method.
Absent new information, DOE continues
to use the 2 percent reduction factor.
However, because DOE has established
different efficiency level shapes for the
IS/RS versus PS product classes, DOE
has revised its methodology for scaling
an IS/RS efficiency level to a PS
efficiency level in this final rule.
To establish residential PS and 8-foot
HO PS efficiency levels, DOE input the
arc power of the representative unit at
each EL into the IS/RS efficiency level
equation to calculate the minimum
required BLE. DOE then fit an efficiency
level with a PS exponent (the exponent
‘‘C’’ is 0.37 for PS ballasts) such that it
passed through the minimum required
BLE by adjusting the coefficient ‘‘B’’.
Then, DOE applied the 2 percent
reduction factor to the overall equation
to account for the expected difference in
efficiency between IS and PS ballasts.
Because multiple representative ballast
types existed in the same product class,
DOE sought to match the stringency of
the PS curve to the IS curve at the
highest arc power within that product
class.
8. Manufacturer Selling Prices
DOE received comments on the
process used to develop manufacturer
selling prices (MSPs). NEMA
commented that published blue book
values account for only a small fraction
of market prices and are skewed to be
higher relative to the rest of the market.
(NEMA, No. 47 at p. 7) DOE recognizes
that blue book values are often
significantly higher than MSPs and
therefore used teardown data and
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confidential manufacturer-supplied
MSPs in combination with blue book
values to determine more accurate
MSPs. DOE determined these MSP
values by applying manufacturerspecific ratios between blue book prices
and teardown- or aggregated
manufacturer-sourced MSPs to blue
book prices. By applying the
manufacturer-specific ratios, the blue
book price was reduced to reflect more
realistic MSPs.
NEMA also commented that they do
not think the price analysis method
employed by DOE in the April 2011
NOPR accurately accounts for
manufacturing variances among
companies and circuit topology. In
particular, NEMA disagreed with DOE’s
determination that higher efficiency
ballasts were less expensive to
manufacture than normal efficiency
ballasts. (NEMA, No. 47 at p. 5) Based
on DOE’s assessment, certain higher
efficiency ballasts are less expensive
than lower efficiency ballasts. DOE
notes that these trends are consistent
with confidential manufacturer cost
data received during interviews. Several
low efficiency ballasts are magnetic
ballasts, which are comprised of
materials different from electronic
ballasts. The difference in materials,
such as the use of larger amounts of
electrical steel and copper or aluminum
windings in magnetic ballasts, would
account for the higher cost. Similarly,
DOE found some electronic T12 ballasts
to carry a higher MSP than a more
efficient T8 electronic ballast. Though
these electronic ballasts utilize similar
components, the low demand for T12
ballasts reduces the potential for highvolume discounts leading to a higher
MSP relative to the T8 ballast.
NEMA questioned DOE’s statement in
the April 2011 NOPR that teardown
prices are independent of long term
commodity prices. (NEMA, No. 47 at p.
7) DOE acknowledges that a teardown
analysis may be sensitive to the
dynamic nature of the electrical
component market, but continues to use
the teardown results given that limited
pricing information is publicly
available. In the April 2011 NOPR, DOE
amended its teardown approach such
that incremental differences between
two efficiency levels were based on
pricing differences between single
70577
manufacturers’ ballasts rather than
basing prices directly from teardowns of
different manufacturers. DOE notes that
the industry did not provide average
incremental MPC values. Instead, some
manufacturers provided confidential
data on an individual basis. DOE has
not identified any new information that
would affect its conclusion in the April
2011 NOPR, and therefore maintains
this approach for the final rule.
9. Results
In this final rule, DOE establishes
efficiency levels in terms of a power law
equation that relates total lamp arc
power to BLE. When developing
efficiency level equations, DOE plotted
the reported value for each ballast
model to account for certification
requirements. DOE then applied a
reduction factor to the efficiency level
equations based on an analysis of lab-tolab variation. Table V.2 summarizes the
efficiency levels developed by DOE for
each product class. Costs associated
with ballasts that meet these efficiency
levels are presented in chapter 5 of the
TSD.
TABLE V.2—EFFICIENCY LEVELS FOR REPRESENTATIVE PRODUCT CLASSES
BLE = A/(1+B*total lamp arc power∧-C) where A, B, and C are as follows:
Representative product class
Efficiency
level
A
B
C
IS and RS ballasts (not classified as residential) that operate .......................................................
4-foot MBP lamps
2-foot U-shaped lamps
8-foot slimline lamps
PS ballasts (not classified as residential) that operate ...................................................................
4-foot MBP lamps
2-foot U-shaped lamps
4-foot MiniBP SO lamps
4-foot MiniBP HO lamps
IS and RS ballasts (not classified as sign ballasts) that operate 8-foot HO lamps ........................
EL 1
EL 2
EL 3
0.993
0.46
0.31
0.27
0.25
EL 1
EL 2
EL 3
0.993
0.60
0.55
0.51
0.37
Sign ballasts that operate 8-foot HO lamps ....................................................................................
IS and RS residential ballasts that operate .....................................................................................
4-foot MBP lamps
2-foot U-shaped lamps
8-foot slimline lamps
EL
EL
EL
EL
EL
EL
1
2
3
1
1
2
0.25
0.993
1.01
0.38
0.28
0.47
0.41
0.29
A
B
C
0.993
0.993
0.25
0.25
TABLE V.3—EFFICIENCY LEVELS FOR SCALED PRODUCT CLASSES
BLE = A/(1 + B * total lamp arc power∧-C) where A, B, and C are as follows:
Efficiency
level
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Scaled product class
PS ballasts (not classified as sign ballasts) that operate 8-foot HO lamps ....................................
PS residential ballast that operate ..................................................................................................
4-foot MBP lamps
2-foot U-shaped lamps
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EL
EL
EL
EL
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1
2
3
1
2
0.973
0.973
14NOR2
1.86
0.70
0.52
0.71
0.50
0.37
0.37
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C. Markups to Determine Product Price
By applying markups to the MSPs
estimated in the engineering analysis,
DOE estimated the amounts consumers
would pay for baseline and more
efficient products. At each step in the
distribution channel, companies mark
up the price of the product to cover
business costs and maintain a profit
margin. Identifying the appropriate
markups and ultimately determining
consumer product price depend on the
type of distribution channels through
which the product moves from
manufacturer to consumer.
In response to the April 2011 NOPR,
DOE received no comments regarding
its markups analysis, and therefore
retained this approach for this final rule.
DOE’s markups analysis method and
results are discussed in the following
sections.
1. Distribution Channels
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Before it could develop markups, DOE
needed to identify distribution channels
(i.e., how the products are distributed
from the manufacturer to the end user)
for the ballast designs addressed in this
final rule. Most ballasts used in
commercial and industrial applications
pass through one of two types of
distribution channels—an original
equipment manufacturer (OEM) channel
and a wholesaler channel. The OEM
distribution channel applies to ballasts
shipped in fixtures. In this distribution
channel, the ballast passes from the
manufacturer to a fixture OEM which in
turn sells it to an electrical wholesaler
(i.e., distributor); from the wholesaler it
passes to a contractor, and finally to the
end user. The wholesaler distribution
channel applies to ballasts not shipped
in fixtures (e.g., replacement ballasts). In
this distribution channel, the ballast
passes from the manufacturer to an
electrical wholesaler, then to a
contractor, and finally to the end user.
DOE assumed a separate home
improvement retailer distribution
channel for residential ballasts, because
DOE could not obtain retail sales data
detailing the breakdown between fixture
ballasts and replacement ballasts, DOE
assumed for the markups analysis that
the manufacturer sells the residential
ballast to a fixture OEM who in turn
sells it in a fixture to a home
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improvement retailer, where it is
purchased by the end user.
2. Estimation of Markups
Publicly-owned companies must
disclose financial information regularly
through filings with the U.S. Securities
and Exchange Commission (SEC). Filed
annually, SEC form 10–K provides a
comprehensive overview of the
company’s business and financial
conditions. To estimate OEM,
wholesaler, and retailer markups, DOE
used financial data from 10–K reports
from publicly owned lighting fixture
manufacturers, electrical wholesalers,
and home improvement retailers.
DOE’s markup analysis developed
both baseline and incremental markups
to transform the ballast MSP into an end
user product price. DOE used the
baseline markups to determine the price
of baseline designs. Incremental
markups are coefficients that relate the
change in the MSP of higher-efficiency
designs to the change in the OEM,
wholesaler, and retailer sales prices.
These markups refer to higher-efficiency
designs sold under market conditions
with new and amended energy
conservation standards. The calculated
average baseline markups for fixture
OEM companies, electrical wholesalers,
and home improvement retailers were
1.50, 1.23, and 1.51, respectively. The
average incremental markups for OEMs,
wholesalers, and home improvement
retailers were 1.17, 1.05, and 1.15,
respectively.
While recognizing that SEC form
10–K data is not product-specific, actual
product markups are generally businesssensitive. For this rule, DOE contacted
the National Association of Electrical
Distributors (NAED) and received
feedback from two NAED member
companies, both confirming that DOE’s
calculated wholesaler markups were
consistent with their actual markups for
commercial and industrial ballast
designs. DOE also contacted Home
Depot and Lowe’s regarding price
markups for residential fluorescent
lighting products, but both
organizations declined to comment,
citing competition concerns.
Consequently, DOE based its estimated
markups for commercial, industrial and
residential ballast designs on financial
data from 10–K reports.
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For ballasts used in commercial and
industrial applications, DOE adjusted
the calculated average baseline and
incremental markups to reflect
estimated proportions of ballasts sold
through the OEM and wholesaler
distribution channels. DOE assumed
ballasts in the fixture OEM channel
represent 63 percent of the market and
ballasts in the wholesaler channel
represent 37 percent. These percentages
are from chapter 3 (engineering
analysis) of the final TSD for the 2000
Ballast Rule and were based on a
comment submitted by NEMA for that
rulemaking. For the current ballast
rulemaking, neither NEMA nor other
interested parties provided updated
estimates of distribution channel
proportions, or offered adverse
comment regarding DOE’s assumed
proportions.
DOE then multiplied the resulting
weighted average markups by a
contractor markup of 1.13 (also from the
2000 Ballast Rule, and used in the 2009
Lamps Rule) and sales tax to develop
total weighted baseline and incremental
markups, which reflect all individual
markups incurred in the ballast
distribution channels. DOE has not
identified a more recent estimate for
contractor markups, and did not receive
related data or estimates from interested
parties in response to the ballasts
preliminary TSD or April 2011 NOPR.
For residential ballasts, DOE assumed
that end users purchased ballasts—
already installed in fixtures—directly
from home improvement retailers with
no contractor involvement or markup.
DOE used OEM and retailer markups
and sales tax to calculate total baseline
and incremental markups for residential
ballasts.
The sales tax represents state and
local sales taxes applied to the end user
equipment price. DOE derived state and
local taxes from data provided by the
Sales Tax Clearinghouse.39 These data
represent weighted averages that
include state, county and city rates.
DOE then derived population-weighted
average tax values for each census
39 The Sales Tax Clearinghouse. Available at
https://thestc.com/STRates.stm. (Last accessed May
16, 2011.)
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census division and large state values.
This approach provided a national
average tax rate of 7.25 percent.
division and large state, and then
derived U.S. average tax values using a
population-weighted average of the
70579
3. Summary of Markups
3. Summary of Markups
TABLE V.4—SUMMARY OF BALLAST DISTRIBUTION CHANNEL MARKUPS
Commercial/industrial ballasts
OEM distribution
(ballasts shipped in fixtures)
Residential ballasts
Wholesaler distribution
(individual ballasts only)
Retailer distribution
(ballasts shipped in fixtures)
Baseline
Fixture OEM .................................
Electrical Wholesaler (Distributor)
Home Improvement Retailer ........
Contractor or Installer ..................
Incremental
Baseline
Incremental
Baseline
Incremental
1.50
1.23
..........................
1.13
1.17
1.05
..........................
1.13
..........................
1.23
..........................
1.13
..........................
1.05
..........................
1.13
1.50
..........................
1.51
..........................
1.17
..........................
1.15
..........................
Sales Tax .....................................
1.07
Overall ..........................................
2.24
Assumed Market Percentage ......
Overall (Weighted) ................
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1.27
1.96 (Baseline)
1.41 (Incremental)
For the energy use analysis, DOE
estimated the energy use of ballasts in
the field (i.e., as they are actually used
by consumers in commercial, industrial
and residential applications). The
energy use analysis provided the basis
for other DOE analyses, particularly
assessments of the energy savings and
the savings in consumer operating costs
that could result from DOE’s adoption of
new and amended standard levels.
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1.49
37
D. Energy Use Analysis
18:36 Nov 10, 2011
1.48
1.07
63
In response to the April 2011 NOPR,
NEMA said it disagreed with DOE’s
incremental markups for OEMs,
contractors and home improvement
retailers, citing current economic
conditions, price compression and
commodity fluctuations. NEMA did not
provide details about or suggested
revisions to incremental markups.
(NEMA, No. 47 at p. 7) DOE was not
able to obtain confidential pricing and
markups data from OEMs and home
improvement retailers to validate its
estimated baseline and incremental
markups. Absent representative
markups data, DOE retained its
previously-vetted approach using SEC
form 10–K financial reports to estimate
markups for OEMs and home
improvement retailers. Similarly, no
new data to support different contractor
markups were available, so DOE
retained its NOPR markups for this final
rule.
Using these markups, DOE generated
ballast end user prices for each
efficiency level it considered. Chapter 7
of the final rule TSD provides additional
detail on the markups analysis.
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1.07
To develop annual energy use
estimates, DOE multiplied annual usage
(in hours per year) by the lamp-andballast system input power (in watts).
DOE characterized representative lampand-ballast systems in the engineering
analysis, which provided measured and
normalized system input power ratings
(the latter used to compare baseline- and
standards-case systems on an equal
light-output basis). To characterize the
country’s average use of lamp-andballast systems for a typical year, DOE
developed annual operating hour
distributions by sector, using data
published in the U.S. Lighting Market
Characterization: Volume I (LMC),40 the
Commercial Building Energy
Consumption Survey (CBECS),41 the
Manufacturer Energy Consumption
Survey (MECS),42 and the Residential
Energy Consumption Survey (RECS).43
40 U.S. Department of Energy, Office of Energy
Efficiency and Renewable Energy. U.S. Lighting
Market Characterization. Volume I: National
Lighting Inventory and Energy Consumption
Estimate. 2002. Available at https://apps1.eere.
energy.gov/buildings/publications/pdfs/corporate/
lmc_vol1.pdf.
41 U.S. Department of Energy, Energy Information
Administration. Commercial Building Energy
Consumption Survey: Micro-Level Data, File 2
Building Activities, Special Measures of Size, and
Multi-building Facilities. 2003. Available at https://
www.eia.doe.gov/emeu/cbecs/public_use.html.
42 U.S. Department of Energy, Energy Information
Administration. Manufacturing Energy
Consumption Survey, Table 1.4: Number of
Establishments Using Energy Consumed for All
Purpose. 2006. Available at https://www.eia.doe.gov/
emeu/mecs/mecs2006/2006tables.html.
43 U.S. Department of Energy, Energy Information
Administration. Residential Energy Consumption
Survey: File 1: Housing Unit Characteristics. 2005.
Available at https://www.eia.doe.gov/emeu/recs/
recspubuse05/pubuse05.html.
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2.43
1.43
100
2.43
1.43
DOE assumed, based on its market and
technology assessment, that PS ballasts
operating 4-foot MBP T8 lamps in the
commercial sector were operated on
occupancy sensors. Based on its survey
of available literature, DOE assumed
that occupancy sensors would result, on
average, in a 30-percent reduction in
annual operating hours.
DOE received no comments on the
April 2011 NOPR regarding the energy
use analysis for ballasts and retains this
approach for today’s final rule. Chapter
6 of the final rule TSD provides a more
detailed description of DOE’s energy use
analysis.
E. Life-Cycle Cost and Payback Period
Analyses
DOE conducted LCC and PBP
analyses to evaluate the economic
impacts of potential energy conservation
standards for ballasts on individual
consumers. For any given efficiency
level, DOE measures the PBP and the
change in LCC relative to an estimated
baseline product efficiency level. The
LCC is the total consumer expense over
the life of a product, consisting of
purchase, installation, and operating
costs (expenses for energy use,
maintenance, and repair). To compute
the operating costs, DOE discounted
future operating costs to the time of
purchase and summed 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
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change in purchase cost (normally
higher) by the change in average annual
operating cost (normally lower) that
results from the more efficient standard.
Inputs to the calculation of total
installed costs include the cost of the
product—which includes MSPs,
distribution channel markups, and sales
taxes—and installation costs. Inputs to
the calculation of operating expenses
include annual energy consumption,
energy prices and price projections,
repair and maintenance costs, product
lifetimes, discount rates, and the year
that compliance with new and amended
standards is required. To account for
uncertainty and variability, DOE created
probability distributions for inputs such
as operating hours, electricity prices,
discount rates and sales tax rates, and
disposal costs. For example, DOE
created a probability distribution of
annual energy consumption in its
energy use analysis based, in part, on a
range of annual operating hours. The
operating hour distributions capture
variation across census divisions and
large states, building types, and lampand-ballast systems for three sectors
(commercial, industrial, and
residential). Because ballast MSPs were
specific to the representative ballast
designs evaluated in DOE’s engineering
analysis and price markups were based
on limited publicly-available financial
data, DOE used discrete values instead
of distributions for these inputs.
The computer model DOE uses to
calculate the LCC and PBP, which
incorporates Crystal Ball (a
commercially available software
program), relies on a Monte Carlo
simulation to incorporate uncertainty
and variability into the analysis. The
Monte Carlo simulations randomly
sample input values from probability
distributions of these values, performing
more than 10,000 iterations per
simulation run. The final rule TSD
chapter 8 and its appendices provide
details on the spreadsheet model and all
inputs to the LCC and PBP analyses.
Table V.5 summarizes the approach
and data DOE used to derive inputs to
the LCC and PBP calculations for the
April 2011 NOPR as well as the changes
made for this final rule. The subsections
that follow discuss the model inputs
and DOE’s changes to them.
TABLE V.5—SUMMARY OF INPUTS AND KEY ASSUMPTIONS IN THE LCC AND PBP ANALYSES *
Inputs
NOPR
Changes for the final
rule
Product Cost ...................
Installation Cost ..............
Derived by multiplying ballast MSPs by distribution channel markups and sales tax ..........
Derived costs using estimated labor times, and applicable labor rates from RS Means
Electrical Cost Data (2007) and U.S. Bureau of Labor Statistics.
Determined operating hours by associating building type-specific operating hours with regional distributions of various building types using lighting market and building energy
consumption survey data: LMC (2002), CBECS (2003), MECS (2006), and RECS
(2005) 44 (see section V.D).
Electricity: Based on EIA’s Form 826 data for 2010 .............................................................
Variability: Energy prices determined at state level.
Forecasted using Annual Energy Outlook 2010 (AEO2010) ................................................
Commercial/Industrial: Included labor and materials costs for lamp replacement, and disposal costs for failed lamps.
Residential: Included only materials cost for lamps, with no lamp disposal costs.
Variability: Assumed commercial and industrial consumers pay recycling costs in approximately 30 percent of lamp failures and 5 percent of ballast failures.
Ballasts: Lifetime based on average lifetimes from the 2000 Ballast Rule (and used in the
2009 Lamps Rule).
Lamps: Assumed as 91 percent—94 percent of rated life, to account for lamp type and
relamping practices.
Commercial/Industrial: Estimated cost of capital to affected firms and industries; developed weighted average of the cost to the company of equity and debt financing.
Residential: Estimated by examining all possible debt or asset classes that might be
used to purchase ballasts.
Variability: Developed a distribution of discount rates for each end-use sector.
2014 .......................................................................................................................................
No change.
Updated labor rates from
2009$ to 2010$.
No change (newer data
unavailable).
Assessed two events: Ballast failure and new construction/renovation ...............................
No change.
Annual Energy Use .........
Energy Prices ..................
Energy Price Projections
Replacement and Disposal Costs.
Product Lifetime ..............
Discount Rates ................
Compliance Date of
Standards.
Ballast Purchasing
Events.
No change.
No change.45
Updated labor rates from
2009$ to 2010$.
No change.
No change.
No change.
* References for the data sources mentioned in this table are provided in the sections following the table or in chapter 8 of the final rule TSD.
1. Product Cost
To calculate consumer product costs,
DOE multiplied the MSPs developed in
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44 RECS
was updated in 2009, but these updates
did not address lighting usage; therefore, DOE used
RECS 2005 data for this final rule.
45 DOE continues to use AEO2010 in its final rule
analyses. The comment period on DOE’s NODA,
discussed previously, closed on September 14,
2011, and DOE is required by consent decree to
publish the final amended standards for fluorescent
lamp ballasts by October 28, 2011. (State of New
York, et al. v. Bodman et al., 05 Civ. 7807 (LAP)
and Natural Resources Defense Council, et al. v.
Bodman, et al., 05 Civ. 7808 (LAP) (Nov. 3, 2006),
as amended on June 20, 2011.) The additional time
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the engineering analysis by the
distribution channel markups described
required for DOE to consider the comments and
information submitted by interested parties did not
allow sufficient time for DOE to update the final
rule analyses using AEO2011. DOE has determined,
however, that the AEO2011 30-year annual growth
rates for energy consumption (electric power) and
electricity generating capacity are almost identical
to those in AEO2010. The forecasted near-term
electricity prices in AEO2010 are slightly higher
than in AEO2011, and would produce slightly
shorter payback periods. However, these payback
periods and other LCC and NIA results are not
expected to vary significantly using AEO2010 and
AEO2011.
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in section V.C.1 (along with sales taxes).
DOE used different markups for baseline
products and higher-efficiency
products, because the markups
estimated for incremental costs differ
from those estimated for baseline
models.
DOE received comments on the April
2011 NOPR questioning its product cost
assumptions for residential ballasts.
NEEA and NPCC noted that residential
consumers would more likely replace an
entire fluorescent lamp fixture upon
ballast failure, and that these fixtures
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would be less expensive than DOE’s
estimated ballast prices. (NEEA, Public
Meeting Transcript, No. 43 at pp. 169–
170; NPCC, Public Meeting Transcript,
No. 43 at pp. 163–164; NEEA and NPCC,
No. 44 at p. 6) DOE notes that
fluorescent fixture and ballast price are
highly variable, but maintains that its
estimated residential ballast prices
(approx. $10–12) are comparable with
those for inexpensive fixtures (e.g., shop
lights) that residential consumers might
replace upon ballast failure. DOE also
notes that fixture price data that
correspond with individual ballast
efficiency levels are not readily
available. Therefore, DOE retained its
residential ballast product cost
approach for this final rule.
On February 22, 2011, DOE published
a Notice of Data Availability (NODA, 76
FR 9696) stating that DOE may consider
improving regulatory analysis by
addressing product and equipment price
trends. DOE notes that learning curve
analysis characterizes the reduction in
production cost mainly associated with
labor-based performance improvement
and higher investment in new capital
equipment at the microeconomic level.
Experience curve analysis tends to focus
more on entire industries and aggregates
over various casual factors at the
macroeconomic level: ‘‘Experience
curve’’ and ‘‘progress function’’
typically represent generalizations of
the learning concept to encompass
behavior of all inputs to production and
cost (i.e., labor, capital, and materials).’’
The economic literature often uses these
two terms interchangeably. The term
‘‘learning’’ is used here to broadly cover
these general macroeconomic concepts.
Consistent with the February 2011
NODA, DOE examined historical
producer price indices (PPI) for
fluorescent ballasts and found both
positive and negative real price trends
depending on the specific time period
examined. Therefore, in the absence of
a definitive trend, DOE assumed in its
price forecasts for the NOPR that the
real prices of fluorescent ballasts are
constant in time and that fluorescent
ballast prices will trend the same way
as prices in the economy as a whole.
DOE is aware that there have been
significant changes in both the
regulatory environment and mix of
fluorescent ballast and controls
technologies that create analytical
challenges for estimating longer-term
product price trends from the productspecific PPI data. DOE performed price
trends sensitivity calculations to
examine the dependence of the analysis
results on different analytical
assumptions.
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DOE received no comments on the
April 2011 NOPR regarding its ballast
price trend basis. For this final rule,
DOE also considered adjusting ballast
prices using forecasted price indices
(called deflators) used by EIA to develop
the AEO. When adjusted for inflation,
the deflator-based price indices decline
from 100 in 2010 to approximately 54 in
2043. The effect is diminished
significantly when discounting is taken
into account. Deflator-based net present
value (NPV) results from the national
impacts analysis (NIA) were
approximately 9 percent higher than
NPV values based on constant real
prices for ballasts. Given this minor
difference in estimated NPV, and that
DOE did not receive negative comments
on its constant real price basis in the
NOPR, DOE retained its constant real
price approach for this final rule. A
more detailed discussion of price trend
modeling and calculations is provided
in Appendix 8B of the final rule TSD.
2. Installation Cost
The installation cost is the total cost
to the consumer to install the
equipment, excluding the marked-up
consumer product price. Installation
costs include labor, overhead, and any
miscellaneous materials and parts. As
detailed in the final rule TSD, DOE
considered the total installed cost of a
lamp-and-ballast system to be the
consumer product price (including sales
taxes) plus the installation cost. DOE
applied installation costs to lamp-andballast systems installed in the
commercial and industrial sectors,
treating an installation cost as the
product of the average labor rate and the
time needed for installation. Using the
same approach, DOE assumed that
residential consumers must pay for the
installation of a fixture containing a
lamp-and-ballast system, and calculated
installation price in the same manner.
DOE received no comments on the April
2011 NOPR concerning its installation
costs for the LCC analysis, and retained
this approach for this final rule.
3. Annual Energy Use
As discussed in section V.D, DOE
estimated the annual energy use of
representative lamp-and-ballast systems
using system input power ratings and
sector operating hours. The annual
energy use inputs to the LCC and PBP
analyses are based on weighted average
annual operating hours, whereas the
Monte Carlo simulation draws on a
distribution of annual operating hours
to determine annual energy use.
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4. Energy Prices
For the LCC and PBP, DOE derived
average energy prices for 13 U.S.
geographic areas consisting of the nine
census divisions, with four large states
(New York, Florida, Texas, and
California) treated separately. For
census divisions containing one of these
large states, DOE calculated the regional
average excluding the data for the large
state. The derivation of prices was based
on data from 2010 EIA Form 826,
‘‘Monthly Electric Utility Sales and
Revenue Data.’’ DOE received no
comments on the April 2011 NOPR
concerning its derivation of energy
prices for the LCC analysis and retained
this approach for this final rule.
5. Energy Price Projections
To estimate the trends in energy
prices, DOE used the price forecasts in
AEO2010. To arrive at prices in future
years, DOE multiplied current average
prices by the forecast of annual average
price changes in AEO2010. Because
AEO2010 forecasts prices to 2035, DOE
followed past EIA guidelines and used
the average rate of change from 2020 to
2035 to estimate the price trend for
electricity from 2035 to 2043. In
addition, the spreadsheets that DOE
used to conduct the LCC and PBP
analyses allow users to select price
forecasts from AEO’s low-growth, highgrowth, and reference case scenarios to
estimate the sensitivity of the LCC and
PBP to different energy price forecasts.
DOE received no specific comments on
the April 2011 NOPR concerning its
energy price forecasting method for the
LCC analysis and retained this approach
for this final rule.
6. Replacement and Disposal Costs
In the April 2011 NOPR, DOE
addressed lamp replacements occurring
within the analysis period as part of
operating costs for considered lampand-ballast system designs.
Replacement costs in the commercial
and industrial sectors included the labor
and materials costs associated with
replacing a lamp at the end of its
lifetime, discounted to 2011. For the
residential sector, DOE projected that
consumers would install their own
replacement lamps and incur no related
labor costs.
Some consumers recycle failed lamps
and ballasts, thus incurring a disposal
cost. For the 2009 Lamps Rule, DOE
found average recycling costs of 10
cents per linear foot for GSFL and $3.50
for each ballast. DOE surveyed current
online recycling cost data for this
rulemaking, and determined that its
2009 recycling cost estimates were still
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valid. A 2004 report by the Association
of Lighting and Mercury Recyclers
noted that approximately 30 percent of
lamps used by businesses and 2 percent
of lamps in the residential sector are
recycled nationwide.46 Consistent with
the 2009 Lamps Rule, DOE considered
the 30-percent lamp-recycling rate to be
significant and incorporated lamp
recycling costs into the LCC analysis for
commercial and industrial consumers.
DOE was unable to obtain reliable
ballast recycling rate data, but projected
that the likely higher ballast recycling
costs would largely discourage
voluntary ballast recycling by
commercial and industrial consumers.
DOE therefore did not include ballast
recycling costs in the LCC analysis.
Given the low (2 percent) estimated
lamp recycling rate in the residential
sector, DOE assumed that residential
consumers would be even less likely to
voluntarily incur the higher recycling
costs for ballasts. Therefore, DOE
excluded the recycling costs for lamps
or ballasts from the LCC analysis for
residential ballast designs.
DOE received no comments on the
April 2011 NOPR concerning these
assumed recycling rates and costs, and
retained this approach in the final rule
LCC analysis. The Monte Carlo
simulation for the final rule allowed
DOE to examine variability in recycling
practices; consequently, DOE assumed
that commercial and industrial
consumers pay recycling costs in 5
percent of ballast failures—as well as
the 30 percent of lamp failures assumed
in the LCC analysis. As in the LCC
analysis, DOE assumed that residential
lamp and ballast disposal rates were
insignificant, and excluded the related
disposal costs from the Monte Carlo
simulation for residential ballast
designs.
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7. Product Lifetime
Chapter 8 of the final rule TSD details
DOE’s basis for its calculation of average
ballast lifetimes. DOE used assumptions
from the 2000 Ballast Rule and the 2009
Lamps Rule. DOE explicitly sought
comment on these assumptions but
received no additional information
upon which to base changes to them in
today’s final rule. For ballasts in the
commercial and industrial sectors, DOE
used an average ballast lifetime of
49,054 hours that, when combined the
respective average annual operating
hours, yielded average ballast lifetimes
of approximately 13 and 10 years in the
46 Association of Lighting and Mercury Recyclers,
‘‘National Mercury-Lamp Recycling Rate and
Availability of Lamp Recycling Services in the
U.S.’’ Nov. 2004.
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commercial and industrial sectors,
respectively. Consistent with the 2000
Ballast Rule and the 2009 Lamps Rule,
DOE assumed an average ballast lifetime
of approximately 15 years in the
residential sector, which corresponds
with 11,835 hours total on an assumed
789 hours per year operating schedule.
To account for a range of relamping
practices (e.g., group and spot
relamping, where lamps are replaced
preemptively or after failure,
respectively), DOE assumed that lamps
operated, on average, for 91–94 percent
of rated life, depending on lamp type.
DOE also assumed that ballast
lifetimes can vary due to both physical
failure and economic factors (e.g., early
replacements due to retrofits). DOE
accounted for variability in lifetime in
LCC and PBP via the Monte Carlo
simulation (using repeated random
sampling), and in the shipments and
NIA analyses by assuming a Weibull
distribution for lifetimes that represents
failures and replacements. DOE received
no adverse comments on the April 2011
NOPR concerning its product lifetime
assumptions and retained this approach
for this final rule.
8. Discount Rates
The discount rate is the rate at which
future expenditures are discounted to
estimate their present value. In the April
2011 NOPR, DOE estimated separate
discount rates for commercial,
industrial, and residential consumers.
For both the proposed and final rules,
DOE also developed a distribution of
discount rates for each end-use sector
from which the Monte Carlo simulation
samples.
For the industrial and commercial
sectors, DOE assembled data on debt
interest rates and the cost of equity
capital for representative firms that use
ballasts. DOE determined a distribution
of the weighted-average cost of capital
for each class of potential owners using
data from the Damodaran online
financial database.47 DOE used the same
distribution of discount rates for the
commercial and industrial sectors. The
average discount rates, weighted by the
shares of each rate value in the sectoral
distributions, are 6.9 percent for
commercial end users and 7.2 percent
for industrial end users.
For the residential sector, DOE
assembled a distribution of interest or
return rates from sources including the
Federal Reserve Board’s ‘‘Survey of
Consumer Finances’’ (SCF) in 1989,
1992, 1995, 1998, 2001, 2004 and 2007.
DOE assigned weights in the
47 The data are available at https://
pages.stern.nyu.edu/∼adamodar.
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distribution based on the shares of each
financial instrument in household
financial holdings according to SCF
data. The weighted-average discount
rate for residential product owners is
estimated to be 5.6 percent.
DOE received no comments on the
April 2011 NOPR concerning its
estimated discount rates for the LCC
analysis and retained this approach for
this final rule.
9. Compliance Date of Standards
The compliance date is when a
covered product is required to meet a
new or amended standard. EPCA
requires that any new or amended
standards established in this rule apply
to products manufactured after a date
that is five years after—(i) the effective
date of the previous amendment; or (ii)
if the previous final rule did not amend
the standards, the earliest date by which
a previous amendment could have been
effective; except that in no case may any
amended standard apply to products
manufactured within three years after
publication of the final rule establishing
such amended standard. (42 U.S.C.
6295(g)(7)(C)). DOE is required by a
2006 consent decree, as amended, to
publish any amended standards for
ballasts by October 28, 2011.48 In
accordance with 42 U.S.C. 6295(g)(7)(C),
the compliance date is three years after
the publication of any final new and
amended standards. DOE calculated the
LCC for all end users as if each one
would purchase a new ballast in the
year compliance with the standard is
required.
10. Ballast Purchasing Events
DOE based the LCC and PBP analyses
for this rulemaking on scenarios where
consumers must purchase a ballast.
Each of these purchasing events may
involve a different set of ballast or lampand-ballast designs and, therefore, a
different set of LCC savings for a certain
efficiency level. The two scenarios are
(1) ballast failure and (2) new
construction/renovation. In the ballast
failure scenario, DOE assumed that the
consumer of the failed ballast would
replace it with a standards-compliant
lamp-and-ballast combination such that
the system light output never drops
more than 10 percent below that of the
baseline system. For the ballast failure
scenario, DOE used rated system input
power to calculate annual energy use.
For new construction/renovation, DOE
assumed that consumers may design a
new installation that matches the
48 State of New York, et al. v. Bodman et al., 05
Civ. 7807 (LAP) and Natural Resources Defense
Council, et al. v. Bodman, et al., 05 Civ. 7808 (LAP)
(Nov. 3, 2006), as amended on June 20, 2011.
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overall light output of the base-case
system. DOE used normalized system
input power, adjusted to yield
equivalent light output from both the
baseline and substitute new
construction/renovation systems.
DOE received no comments on the
April 2011 NOPR concerning its
assumed ballast purchasing events for
the LCC analysis and retained this
approach for this final rule.
F. National Impact Analysis—National
Energy Savings and Net Present Value
Analysis
DOE’s NIA assessed the national
energy savings (NES) and the NPV of
total consumer costs and savings that
would be expect from new or amended
standards at specific efficiency levels.
(‘‘Consumer’’ in this context refers to
users of the regulated product.)
DOE used a spreadsheet model to
calculate the energy savings and the
national consumer costs and savings for
each TSL. The TSD and other
documentation for the rulemaking
explain the models and how to use
them, allowing interested parties to
review DOE’s analyses by changing
various input quantities within the
spreadsheet.
DOE used the NIA spreadsheet to
calculate the NES and NPV, based on
the annual energy consumption and
total installed cost data from the energy
use and LCC analyses. DOE forecasted
the energy savings, energy cost savings,
product costs, and NPV of consumer
benefits for each product class for
products sold from 2014 through 2043.
The forecasts provided annual and
cumulative values for these four output
parameters. DOE examines sensitivities
in the NIA by analyzing different
efficiency scenarios, such as Roll-up
and Shift.
DOE evaluated the national impacts of
new and amended standards for ballasts
by comparing base-case projections with
standards-case projections. The basecase projections characterize energy use
70583
and consumer costs for each product
class in the absence of new or amended
energy conservation standards. DOE
compared these projections 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. In
characterizing the base and standards
cases, DOE considered historical
shipments, the mix of efficiencies sold
in the absence of new standards, and
how that mix may change over time.
Additional information about the NIA
spreadsheet is in final rule TSD chapter
11.
Table V.6 summarizes the approach
and data DOE used to derive the inputs
to the NES and NPV analyses for the
April 2011 NOPR, as well as the
changes to the analyses for the final
rule. A discussion of selected inputs
and changes follows. See chapter 11 of
the final rule TSD for further details.
TABLE V.6—APPROACH AND DATA USED FOR NATIONAL ENERGY SAVINGS AND CONSUMER NET PRESENT VALUE
ANALYSES
Changes for the final
rule
Inputs
NOPR
Shipments .............................
Compliance Date of Standard.
Annual Energy Consumption
per Unit.
Derived annual shipments from shipments model ..........................................................
2014 .................................................................................................................................
See Table V.7.
No change.
Established in the energy use analysis (NOPR TSD chapter 6) .....................................
Rebound Effect .....................
Electricity Price Forecast ......
Energy Site-to-Source Conversion Factor.
Discount Rate .......................
Present Year ........................
1% in commercial and industrial sectors, 8.5% in residential sector ..............................
AEO2010 ..........................................................................................................................
Used marginal conversion factors generated by NEMS–BT; factors held constant after
2035.
3% and 7% real ...............................................................................................................
2011 .................................................................................................................................
Energy use analysis updated using most recent available inputs.
No change.
No change.
No change.
1. Shipments
Product shipments are an important
input to any estimate of the future
impact of a standard. To develop the
shipments portion of the NIA
spreadsheet, DOE used a three-step
process to: (1) Estimate historical
shipments; (2) calculate installed ballast
stock; and (3) develop annual shipment
projections for the analysis period
2014–2043. Table V.7 summarizes the
approach and data DOE used to derive
the inputs to the shipments analysis for
No change.
No change.
the April 2011 NOPR and the changes
DOE made for today’s final rule. A
discussion of these inputs and changes
follows. For details on the shipments
analysis, see chapter 10 of the final rule
TSD.
TABLE V.7—APPROACH AND DATA USED FOR THE SHIPMENTS ANALYSIS
Inputs
NOPR
Historical Shipments ...........
Used historical shipments for 1990–2005 to develop shipments and stock projections for the analysis period; changed lifetime distribution and growth assumptions, mitigating oscillations in shipment projections.
Based projections on the shipments that survive up to a given date; assumed
Weibull lifetime distribution.
Used 2010 AEO projections for floorspace growth ......................................................
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Ballast Stock .......................
Growth .................................
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No change.
No change.
Revised growth rate for residential sector.
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TABLE V.7—APPROACH AND DATA USED FOR THE SHIPMENTS ANALYSIS—Continued
Inputs
NOPR
Changes for the final rule
Base Case Scenarios .........
Analyzed both existing technology and emerging technology scenarios .....................
Standards Case Scenarios
Analyzed Shift and Roll-up scenarios based on both existing and emerging technology cases.
Added dimming ballast penetration rate to the
emerging technology scenario; revised efficiency
apportionments for commercial sector ballasts
operating 4-foot MBP
lamps.
No change.
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a. Historical Shipments
For the April 2011 NOPR, DOE used
U.S. Census Bureau Current Industrial
Reports (CIR) to estimate historical
(1990–2005) shipments for each
representative ballast type. The census
CIR data cover NEMA shipments for
individual ballast designs (e.g., 2-lamp
F96T8), as well as aggregated shipments
for multiple designs to prevent
disclosing data for individual
companies. For lower-volume ballast
designs, the CIR withheld shipments
data to avoid disclosing individual
company data.
For CIR reporting years for which
specific shipments data are too
aggregated or unavailable, DOE
estimated historical shipments using
trends within the available data and/or
market trends identified in ballast
manufacturer interviews, the 2009
Lamps Rule, and the 2000 Ballast Rule.
DOE then adjusted these estimates to
account for the volume of ballasts that
non-NEMA companies import or
manufacture. DOE received no
comments on the April 2011 NOPR
regarding historical ballast shipments
data and estimates. DOE also found no
historical ballast shipment data to
validate its NOPR shipments analysis
because neither NEMA nor its member
companies typically retain data of the
vintage in question (1990–2005). DOE
therefore concluded that census data
remain the best available data for
estimating historical ballast shipments
and retained its approach for this final
rule.
b. Ballast Stock Projections
In its shipments analysis for the April
2011 NOPR, DOE calculated the
installed ballast stock using historical
shipments estimated from U.S. Census
Bureau CIR data (1990–2005) and
projected shipments for future years.
DOE estimated the installed stock
during the analysis period by
calculating how many ballasts will
survive up to a given year based on a
Weibull lifetime distribution for each
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ballast type. DOE received no comments
on the April 2011 NOPR regarding its
ballast stock projection method and
retained this approach for this final rule.
c. Projected Shipments
By modeling ballast market segments
(i.e., purchasing events) and applying
lifetime distribution, growth and
emerging technologies penetration rate
assumptions, and efficiency scenarios,
DOE developed annual shipment
projections for the analysis period
(2014–2043). The following subsections
address the lifetime, base-case market
share apportionment, emerging
technology, market trend, and efficiency
scenario issues that DOE considered in
its shipments analysis for the final rule.
i. Ballast Lifetime Assumptions
In its shipments analysis for the April
2011 NOPR, DOE retained the average
ballast physical lifetimes used in its
preliminary analysis, and combined
them with Weibull distributions for
lifetimes to model ballast failures and
retrofits. DOE received no comments on
the April 2011 NOPR regarding its
assumed average ballast lifetimes and
lifetime distributions and retained this
approach for this final rule.
ii. Base-Case Market Share
Apportionments
When choosing lighting systems,
consumers consider attributes such as
lifetime, efficiency, price, lumen output,
rated wattage, and total system power.
Therefore, within each product class,
DOE developed efficiency level market
share apportionments to account for the
mix of system attributes that consumers
select in the base case. These market
share apportionments were used to
estimate base case historical shipments
and installed stock for each ballast
design.
DOE was not able to obtain detailed
historical ballast shipment data to
develop percentage market shares for
the analyzed ballast designs. Based on
initial manufacturer interviews,
however, DOE was able to develop a
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general assumed market-share
apportionment using shipments of
electronic ballasts for 4-foot T8 MBP
systems. DOE then applied this general
apportionment to each product class in
the base case, assigning 69 percent of
shipments to the baseline ballast design,
and dividing the remaining 31 percent
of shipments among the higher
efficiency designs.
For the April 2011 NOPR, DOE
received several comments regarding
base case market share apportionments
and their effects on estimated energy
savings and economic benefits.
Universal questioned DOE assigning a
majority market share to baseline ballast
designs, noting at least 80 percent of
NEMA manufacturers’ current ballast
shipments are classified as NEMA
Premium. (Universal, Public Meeting
Transcript, No. 43 at p. 38; NEMA, No.
56 at p. 4) Philips and Universal further
contended that DOE’s baseline
apportionments—including magnetic
ballast designs—effectively
underestimated the efficiency of the
installed ballast stock and overestimated
the resulting energy savings and
economic benefits of the proposed
efficiency standards. (Philips, Public
Meeting Transcript, No. 43 at p. 64;
Universal, Public Meeting Transcript,
No. 43 at p. 38)
DOE agrees that the ballast market is
shifting to higher efficiency designs, but
notes that its baseline representative
ballasts (excluding ballasts operating
two 8-foot T12 lamps, and four-lamp
sign ballasts) are electronic designs.
Therefore, less-efficient magnetic
baseline designs did not have a
significant effect on DOE’s NIA results.
However, DOE reviewed the prevalence
of NEMA Premium products in its
tested ballasts (including baseline
products), and adjusted the market
share apportionments of higher
efficiency level ballasts in the IS and
RS, and PS product classes accordingly.
DOE could not verify NEMA’s estimated
80 percent market share for higher
efficiency designs. Based on its review,
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however, DOE assigned a 64-percent
market share to the higher efficiency
level designs and a 36-percent market
share to baseline ballast designs in these
product classes in the base case for the
final rule shipments analysis.
iii. Emerging Technologies Shipment
Forecasts
In its previous analyses, DOE
modeled separate existing and emerging
technologies shipment scenarios to
characterize the uncertainty in ballast
market penetration by emerging solidstate lighting (SSL) technologies. The
existing technologies scenario generally
considers only the market penetration of
technologies that are mature in terms of
price and efficiency, largely excluding
SSL. In the emerging technologies
scenario, the shipments and installed
stock of ballasts (e.g., ballasts operating
4-foot MBP T8 lamps) decrease due to
significant replacement by SSL. This
scenario effectively lowers the energy
savings of new fluorescent lamp ballast
standards. DOE acknowledges both
scenarios and the likelihood that actual
results will fall between them by
presenting the two scenarios’ energy
savings and economic effects as a range.
Consistent with the 2009 Lamps Rule
and its current research, DOE assumed
no SSL penetration for residential linear
fluorescent applications. DOE stated in
the April 2011 NOPR that residential
energy codes will drive the market
toward higher efficacy lighting systems,
but that the related market growth will
be greater for compact fluorescent lamp
(CFL)-based fixtures than for 4-foot MBP
fluorescent systems. As discussed in
DOE’s SSL Multi Year Program Plan
(updated May 2011), the vast majority of
residential sockets are dedicated to
incandescent lamps, for which screwbase compact fluorescent and SSL
lamps are direct replacements.49 DOE’s
review of available residential fixture
surveys confirms that linear fluorescent
fixtures are typically relegated to utility
room, laundry, and some kitchen
applications. A comparison of recent
California residential lighting data for
2005 and 2009 shows no significantly
increased installation of linear
fluorescent systems, and DOE believes
that residential consumers will continue
to opt for lower-first-cost fluorescent
systems rather than installing more
expensive SSL replacements for linear
fluorescent lamps and fixtures. DOE
49 U.S. Department of Energy—Office of Energy
Efficiency and Renewable Energy. Solid-State
Lighting Research and Development: Multi Year
Program Plan. March 2011 (Updated May 2011).
Washington, DC Available at https://apps1.eere.
energy.gov/buildings/publications/pdfs/ssl/ssl_my
pp2011_web.pdf.
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received no adverse comments to the
April 2011 NOPR for not including SSL
penetration in its residential ballast
shipments. Given the limited residential
applications for linear fluorescent
systems, DOE retained this approach for
this final rule.
For the April 2011 NOPR, DOE
received comments regarding how
regulations requiring use of dimming
ballasts could affect future shipments of
fixed-output ballasts. Commenters
referenced proposed regulations in
California that would require
controllable ballasts in non-residential
applications. (ASAP, Public Meeting
Transcript, No. 43 at p. 209; Lutron,
Public Meeting Transcript, No. 43 at pp.
207–208; Philips, Public Meeting
Transcript, No. 43 at p. 179) Philips
further suggested that SSL and dimming
ballasts in combination could largely
eliminate the fixed-output ballast
market by 2040. (Philips, Public
Meeting Transcript, No. 43 at p. 187)
As part of its 2013 Title 24 updates
(effective in 2014), the state of California
is considering mandatory requirements
for controllable light sources that could
require dimming ballasts for nonresidential linear fluorescent systems.50
These proposed changes to Title 24
would build upon existing requirements
for stepped lighting controls, requiring
significantly increased granularity of
control at the individual fixture level. It
is uncertain, however, whether these
proposed changes to Title 24 will be
enacted. It is also not certain that other
building standards, such as the
American Society of Heating,
Refrigerating and Air-Conditioning
Engineers standard 90.1 (ASHRAE 90.1),
would adopt the ballast controllability
requirements being considered in
California. DOE projects that a
significant number of fluorescent
lighting installations where dimming is
not practical or possible (such as spaces
without daylighting, or where
occupancy/vacancy sensing can
extinguish lighting) will remain, thus
maintaining demand for fixed-output
ballasts.
In its comments to the April 2011
NOPR, NEMA generally affirmed DOE’s
shipment projections, but asserted that
DOE underestimated the current and
future penetration of SSL in the
emerging technologies scenario. (NEMA,
No. 47 at pp. 8–9) NEEA stated that the
emerging technologies forecast is the
more likely of DOE’s two shipment
scenarios, and that DOE should increase
50 California Energy Commission’s 2013 Building
Energy Efficiency Standards Rulemaking Web page.
Available at https://www.energy.ca.gov/title24/
2013standards/prerulemaking/. (Last accessed May
27, 2011.)
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the penetration of SSL and controllable
lighting to lower the projected
shipments of fixed-output ballasts.
(NEEA and NPCC, No. 44 at p. 7)
As described previously in this
section, DOE developed existing and
emerging technologies shipment
scenarios to investigate uncertainties in
ballast market penetration by other
technologies. Although dimming
ballasts are an existing technology, DOE
considered them an ‘‘emerging
application’’ for fluorescent lighting
applications and included dimming
ballasts with SSL products in its
emerging technologies shipments
scenario for this final rule. As discussed
in chapter 10 of the final rule TSD,
because SSL penetration has increased
since the inception of this rulemaking,
DOE increased its estimated penetration
rate earlier in the shipments analysis
period. DOE also increased the
maximum penetration of 40.6 percent
(for SSL in the April 2011 NOPR) to a
maximum penetration of 75 percent (for
SSL and dimming ballasts combined).
This increased penetration resulted in
decreased shipments for affected ballast
types for the lower boundary, base case
shipments scenario.
iv. Anticipated Market Trends
DOE received comments on the April
2011 NOPR regarding its shipment
projections for residential ballasts.
NEEA and NPCC questioned whether
DOE overestimated residential ballast
shipments, based on the commenters’
understanding of ballast lifetimes and
new construction growth rates. (NEEA,
Public Meeting Transcript, No. 43 at pp.
194–195; NPCC, Public Meeting
Transcript, No. 43 at p. 195) DOE
calculates shipments of ballasts due to
new construction, retrofits and
replacements for failed ballasts. After
reviewing its assumptions for these
three purchasing events, DOE adjusted
its estimated shipments downward by
approximately 30 percent for the final
rule shipments analysis. See chapter 10
of the final rule TSD for additional
details.
v. Efficiency Scenarios
Several of the inputs for determining
NES (e.g., the annual energy
consumption per unit) and NPV (e.g.,
the total annual installed cost and the
total annual operating cost savings)
depend on product efficiency.
For the April 2011 NOPR, DOE used
two shipment efficiency scenarios:
‘‘Roll-up’’ and ‘‘Shift.’’ The Roll-up
scenario is a standards case in which all
product efficiencies in the base case that
do not meet the standard would roll up
to meet the new standard level.
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Consumers in the base case who
purchase ballasts above the standard
level are not affected as they are
assumed to continue to purchase the
same base-case ballast or lamp-andballast system. The Roll-up scenario
characterizes consumers primarily
driven by the first-cost of the analyzed
products. In contrast, the Shift scenario
models a standards case in which the
standard affects all base-case consumer
purchases (regardless of whether their
base-case efficiency is below the
standard). In this scenario, any
consumer may purchase a more efficient
ballast, preserving the same relationship
to the baseline ballast efficiency. For
example, if a consumer purchased a
ballast one efficiency level above the
baseline, that consumer would do the
same after a standard is imposed. In this
scenario, DOE assumed product
efficiencies in the base case that do not
meet the standard would roll up to meet
the new standard level, as in a roll-up
scenario. However, product efficiencies
at or above the new standard level
would shift to higher efficiency levels.
As the standard level increases, market
share incrementally accumulates at the
highest standard level because it
represents max tech (i.e., moving
beyond this efficiency level is not
achievable with today’s technology).
DOE received no comments on the
April 2011 NOPR regarding its Roll-up
and Shift efficiency scenarios and
retained this approach for the final rule
shipments analysis.
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2. Site-to-Source Energy Conversion
To estimate the national energy
savings expected from appliance
standards, DOE uses a multiplicative
factor to convert site energy
consumption (at the home or
commercial building) into primary or
source energy consumption (the energy
required to convert and deliver the site
energy). These conversion factors
account for the energy used at power
plants to generate electricity and losses
in transmission and distribution. For
electricity, the conversion factors vary
over time due to projected changes in
generation sources (i.e., the power plant
types projected to provide electricity to
the country). The factors that DOE
developed are marginal values, which
represent the response of the system to
an incremental decrease in consumption
associated with appliance standards.
For the April 2011 NOPR, DOE used
annual site-to-source conversion factors
based on the version of NEMS that
corresponds to AEO2010, which
provides energy forecasts through 2035.
For 2036–2043, DOE used conversion
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factors that remain constant at the 2035
values.
Section 1802 of EPAct 2005 directed
DOE to contract a study with the
National Academy of Science (NAS) to
examine whether the goals of energy
efficiency standards are best served by
measurement of energy consumed, and
efficiency improvements, at the actual
point-of-use or through the use of the
full-fuel-cycle, beginning at the source
of energy production (Pub. L. 109–58
(August 8, 2005)). NAS appointed a
committee on ‘‘Point-of-Use and FullFuel-Cycle Measurement Approaches to
Energy Efficiency Standards’’ to conduct
the study, which was completed in May
2009. The NAS committee defined fullfuel-cycle energy consumption as
including, in addition to site energy use,
the following: Energy consumed in the
extraction, processing, and transport of
primary fuels such as coal, oil, and
natural gas; energy losses in thermal
combustion in power generation plants;
and energy losses in transmission and
distribution to homes and commercial
buildings.51
In evaluating the merits of using
point-of-use and full-fuel-cycle
measures, the NAS committee noted
that DOE uses what the committee
referred to as ‘‘extended site’’ energy
consumption to assess the impact of
energy use on the economy, energy
security, and environmental quality.
The extended site measure of energy
consumption includes the energy
consumed during the generation,
transmission, and distribution of
electricity but, unlike the full-fuel-cycle
measure, does not include the energy
consumed in extracting, processing, and
transporting primary fuels. A majority of
the NAS committee concluded that
extended site energy consumption
understates the total energy consumed
to make an appliance operational at the
site. As a result, the NAS committee
recommended that DOE consider
shifting its analytical approach over
time to use a full-fuel-cycle measure of
energy consumption when assessing
national and environmental impacts,
especially with respect to the
calculation of greenhouse gas emissions.
The NAS committee also recommended
that DOE provide more comprehensive
information to the public through labels
and other means, such as an enhanced
Web site. For those appliances that use
multiple fuels (e.g., water heaters), the
51 The National Academies, Board on Energy and
Environmental Systems, Letter to Dr. John Mizroch,
Acting Assistant Secretary, U.S. DOE, Office of
Energy Efficiency and Renewable Energy from
James W. Dally, Chair, Committee on Point-of-Use
and Full-Fuel-Cycle Measurement Approaches to
Energy Efficiency Standards, May 15, 2009.
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NAS committee indicated that
measuring full-fuel-cycle energy
consumption would provide a more
complete picture of energy consumed
and permit comparisons across many
different appliances, as well as an
improved assessment of impacts.
In response to the NAS
recommendations, DOE issued, on
August 20, 2010, a Notice of Proposed
Policy proposing to incorporate a fullfuel cycle analysis into the methods it
uses to estimate the likely impacts of
energy conservation standards on
energy use and emissions. Specifically,
DOE proposed to use full-fuel-cycle
(FFC) measures of energy and GHG
emissions, rather than the primary
(extended site) energy measures it
currently uses. Additionally, DOE
proposed to work collaboratively with
the FTC to make FFC energy and GHG
emissions data available to the public to
enable consumers to make cross-class
comparisons. On October 7, 2010, DOE
held an informal public meeting to
discuss and receive comments on its
planned approach. The Notice, a
transcript of the public meeting and all
public comments received by DOE are
available at: https://www.regulations.gov/
search/Regs/home.html#docketDetail?
R=EERE-2010-BT-NOA-0028. Following
the close of the public comment period,
DOE issued a final policy statement on
these subjects and will take steps to
begin implementing that policy in
future rulemakings and other activities.
76 FR 51281 (August 18, 2011). The
Statement of Policy is available at:
https://www.gpo.gov/fdsys/pkg/FR-201108-18/pdf/2011-21078.pdf.
G. Consumer Sub-Group Analysis
In analyzing the potential impact of
new or amended standards on
consumers, DOE evaluates the impact
on identifiable sub-groups of consumers
(e.g., low-income households) that a
national standard may
disproportionately affect. DOE received
no comments regarding specific subgroups and, therefore, evaluated the
same sub-groups addressed in the 2009
Lamps Rule, assuming that consumers
using GSFL would share similar
characteristics with ballast consumers.
Specifically, DOE evaluated the
following consumer sub-groups for the
April 2011 NOPR: low-income
households; institutions of religious
worship; and institutions that serve lowincome populations (e.g., small
nonprofits). DOE received no comments
on the April 2011 NOPR regarding its
choice of consumer sub-groups, and
retained this approach for this final rule.
The final rule TSD chapter 12 presents
the consumer subgroup analysis.
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H. Manufacturer Impact Analysis
DOE performed an MIA to estimate
the financial impact of new and
amended energy conservation standards
on manufacturers of ballasts, and to
calculate the impact of such standards
on employment and manufacturing
capacity. The MIA has both quantitative
and qualitative aspects. The quantitative
part of the MIA primarily relies on the
GRIM, an industry cash-flow model
using inputs specific to this rulemaking.
The key GRIM inputs are data on the
industry cost structure, product costs,
shipments, and assumptions about
markups and conversion expenditures.
The key output is the INPV. DOE used
the GRIM to calculate cash flows using
standard accounting principles and to
compare changes in INPV between a
base case and various TSLs (the
standards cases). The difference in INPV
between the base and standards cases
represents the financial impact of the
new and amended standards on
manufacturers. Different sets of
shipment and markup assumptions
(scenarios) will produce different
results. The qualitative part of the MIA
addresses factors such as product
characteristics, characteristics of and
impacts on particular sub-groups of
firms, and important market and
product trends. DOE outlined its
complete methodology for the MIA in
the NOPR. 76 FR 20090, 20134 (April
11, 2011). Chapter 13 of the TSD
outlines the complete MIA.
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1. Product and Capital Conversion Costs
New and amended energy
conservation standards will cause
manufacturers to incur conversion costs
to bring their production facilities and
product designs into compliance. For
the MIA, DOE classified these
conversion costs into two major groups:
(1) product conversion costs and (2)
capital conversion costs. For the final
rule, DOE converted the NOPR product
and capital conversion costs to 2010$
from 2009$ using the producer price
index (PPI) for the relevant industry.
The PPI is disaggregated into each North
American Industry Classification
System (NAICS) code. For fluorescent
lamp ballasts, DOE updated the
conversion costs using the specific PPI
index under NAICS code 335311—
‘‘Electric power and specialty
transformer manufacturing’’ and series
ID PCU3353113353115—‘‘Fluorescent
lamp ballasts.’’ DOE’s estimates of the
product and capital conversion costs for
fluorescent lamp ballasts can be found
in section VII.B.2.a, of today’s final rule
and in chapter 13 of the TSD.
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a. Product Conversion Costs
Product conversion costs are
investments in research, development,
testing, marketing, and other noncapitalized costs necessary to make
product designs comply with the new or
amended energy conservation
standard.DOE based its estimates of the
product conversion costs that would be
required to meet each TSL on
information obtained from manufacturer
interviews, the engineering analysis, the
NIA shipment analysis, and market
information about the number of models
and stock-keeping units (SKUs) each
major manufacturer supports. This
methodology, described in full in the
April 2011 NOPR (76 FR 20090, 20136
(April 11, 2011)), centers on an
assessment of the number of models and
SKUs manufacturers will need to
upgrade to meet new and amended
standards. DOE applied a per-model and
per-SKU cost to every product currently
offered by manufacturers that does not
meet the analyzed standard levels.
Several stakeholders questioned this
methodology, arguing that DOE’s
assumption that manufacturers would
upgrade all models that do not currently
meet existing standards leads to
overstated conversion cost estimates. In
reality, manufacturers would not
upgrade non-compliant models in
product categories where they already
offer similar compliant models. (NEEA
and NPCC, No. 44 at pp. 7–8; CA
Utilities, No. 45 at pp. 7–8) Similarly,
NEEA and NPCC stated that
manufacturers may not upgrade all noncompliant product lines as they shift
resources away from fluorescent lighting
toward emerging technologies such as
solid-state lighting. (NEEA and NPCC,
No. 44 at p. 8)
In contrast, manufacturers argued that
full product line upgrades would be
necessary to compete. GE explained that
manufacturers must upgrade noncompliant models even in categories in
which compliant models currently exist
because today’s high efficiency products
generally bundle additional premium
features at a higher cost. These premium
features, such as Type CC protection,
cold temperature rating, case size, and
lamp striation control, are detailed in
the April 2011 NOPR. 76 FR 20090,
20108–9 (April 11, 2011). To remain
competitive, manufacturers would need
to offer compliant products stripped of
these premium features to the costconscious OEM channels. (GE, Public
Meeting Transcript, No. 43 at p. 217)
Philips emphasized that manufacturers
cannot simply ignore the ballast market
by choosing not to make the necessary
investments to meet today’s standards
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because it represents an important part
of the lighting business. (Philips, Public
Meeting Transcript, No. 43 at pp. 213–
4)
Although DOE’s max tech efficiency
levels do not preclude ballasts with
premium features, DOE agrees that
competition in the OEM channel would
force manufacturers to offer a low-cost
product at the new baseline standard
level. The large fixture manufacturers
that compose the OEM channel are
price-sensitive, and their large orders
afford them substantial buying power.
Their business is valuable to the ballast
industry because the manufacturers rely
on these high-volume orders to improve
plant utilization and lower fixed costs
per unit for all models. As such, DOE
does not predict that large ballast
manufacturers can afford to ignore the
demand for these commoditized 52
products. DOE also finds it
unreasonable to assume that
manufacturers would forego investment
in the ballast market due to a shifting
focus on emerging technologies because
ballast sales currently generate
significant revenue for these companies.
For these reasons, DOE has not adjusted
its methodology for determining the
number of models that would need to be
upgraded in response to standards.
b. Capital Conversion Costs
Capital conversion costs are
investments in property, plant, and
equipment necessary to adapt or change
existing production facilities such that
new product designs can be fabricated
and assembled. Estimates for capital
conversion costs varied greatly from
manufacturer to manufacturer, as
manufacturers anticipated different
paths to compliance based on the
modernity, flexibility, and level of
automation of the equipment already
existing in their factories. However, all
manufacturers DOE interviewed
indicated that capital costs would be
relatively moderate compared to the
required engineering costs. 76 FR 20090,
20136 (April 11, 2011).
2. Markup Scenarios
For the MIA, DOE modeled two
standards-case markup scenarios to
represent the uncertainty regarding the
potential impacts on prices and
profitability for manufacturers following
the implementation of amended energy
conservation standards: (1) A
preservation of operating profit markup
scenario, and (2) a two-tier markup
scenario. These scenarios lead to
52 In this final rule, we define ‘commoditized’ to
mean that a large number of products are produced
by many manufacturers, such that the products are
differentiated only by price.
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different markups values, which, when
applied to the inputted MPCs, result in
varying revenue and cash flow impacts.
The preservation of operating profit
markup scenario assumes that
manufacturers are able to maintain the
base-case total operating profit in
absolute dollars in the standards case,
despite higher product costs and
investment. DOE adjusted the
manufacturer markups in the GRIM at
each TSL to yield approximately the
same earnings before interest and taxes
in the standards case in the year after
the compliance date of the new and
amended standards as in the base case.
The preservation of operating profit
markup scenario represents the upper
bound of industry profitability
following amended energy conservation
standards. Under this scenario, while
manufacturers are not able to yield
additional operating profit from higher
production costs and the investments
required to comply with the new and
amended energy conservation standard,
they are able to maintain the same
operating profit in the standards case as
in the base case.
DOE also modeled a lower bound
profitability scenario with the two-tier
markup scenario. In this scenario, DOE
assumed that the markup on fluorescent
lamp ballasts varies according to two
efficiency tiers in both the base case and
the standards case. DOE used
information from MIA interviews to
estimate markups for fluorescent lamp
ballasts under a two-tier pricing strategy
in the base case. In the standards case,
DOE modeled the situation in which
portfolio reduction squeezes the margin
of higher-efficiency products as they
become the new baseline, presumably
high-volume products. 76 FR 20090,
20137 (April 11, 2011).
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3. Other Key GRIM Inputs
Key inputs to the GRIM characterize
the fluorescent lamp ballast industry
cost structure, investments, shipments,
and markups. For today’s final rule,
DOE made several updates to the GRIM
to reflect changes in these inputs. These
updates do not represent changes in
methodology from the April 2011
NOPR. Specifically, DOE incorporated
changes made in the engineering
analysis and NIA, including updates to
the MPCs, shipment forecasts, and
shipment efficiency distributions. These
updated inputs affected the values
calculated for the conversion costs and
markups described above, as well as the
INPV results presented in section
VII.B.2.
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4. Other Comments From Interested
Parties
The following section discusses a
number of other comments DOE
received on the April 2011 NOPR MIA
methodology.
a. Fixture Redesigns for Ballast Can Size
Changes
Several interested parties commented
that new and amended standards could
drive larger ballast designs, which
would result in product redesign and
tooling costs for fixture manufacturers
because fixtures are built for a particular
ballast can size. NEMA stated that
increasing efficiency by employing
additional circuitry to reduce variation
would drive larger case sizes. (NEMA,
No 47 at p. 9) At the same time, the
market has trended over time toward the
use of smaller can sizes (from the
standard can to the A-can and, most
recently, from the A-can to the N-can).
Larger can sizes would reverse this
trend and cost fixture manufacturers
tens of millions of dollars each,
according to NEMA and Acuity Brands.
Accordingly, these fixture redesign costs
should be included in DOE’s analysis.
(NEMA, Public Meeting Transcript, No.
43 at pp. 33–4, 36–7; Acuity Brands,
Public Meeting Transcript, No. 43 at pp.
171–2)
DOE recognizes that the fluorescent
lamp ballast market has trended over
time toward the use of smaller can sizes.
For today’s final rule, as discussed in
section V.B.5.a, DOE is not analyzing
any efficiency levels that would
eliminate manufacturers’ ability to meet
standard levels with the smaller N-cans.
DOE has accounted for sources of
variation and compliance certification
requirements, as described in section
V.B.4, and does not project that ballasts
will grow in size in response to
standards. As such, fixture
manufacturers will not incur product
redesign and tooling costs to
accommodate larger ballasts.
b. Potential Benefits to Ballast
Manufacturers
ASAP noted that energy conservation
standards for fluorescent lamp ballasts
could accelerate the adoption of
emerging technologies. Because ballast
manufacturers often also offer these
emerging technologies and can typically
command higher margins on these
emerging technology products, ballast
manufacturers could be less affected by
standards than estimated by DOE.
(ASAP, Public Meeting Transcript, No.
43 at pp. 209–11)
As addressed in response to
comments in the April 2011 NOPR (76
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FR 20090, 20138 (April 11, 2011)), the
potential exists for the market to
increasingly migrate from traditional
fixed light output fluorescent lamp
ballasts to alternate technologies such as
LEDs and dimming ballasts. DOE
therefore models the emerging
technologies shipment scenario as
described in section V.F.1.c and in
chapter 10 of the TSD. This market shift
to emerging technologies occurs in the
base case. That is, the shift is not
standards-induced. DOE excludes the
revenue from substitute technologies
earned by manufacturers who produce
ballasts in the GRIM because the
revenue stream would be present in
both the base case and the standards
case, resulting in no impact on the
change in INPV.
c. Opportunity Cost of Investments
NEMA and Philips stated that the TSL
proposed in the April 2011 NOPR (76
FR 20090, 20166–9 (April 11, 2011))
would have a high opportunity cost due
to the limited capital for investment and
R&D. Any investments incurred to meet
amended ballast standards would reflect
foregone investments in emerging
technologies such as solid state lighting
and controls, and reduced wattage lamp
and ballast systems, which the industry
believes offer both better prospects for
market growth and greater potential for
energy savings than traditional fixedlight-output fluorescent lamp ballasts.
(Philips, Public Meeting Transcript, No.
43 at pp. 212–3; NEMA, Public Meeting
Transcript, No. 43 at pp. 40–1; NEMA,
No. 47 at pp. 9, 11) Specifically, NEMA
argued that the investments necessary to
meet new and amended ballast
standards would be better spent
developing new technologies that can
save far more energy than the 2 to 3
percent additional energy savings this
standard would generate. (NEMA, No.
52 at p. 10) NEMA also stated that the
proposed rule provided no clear
incentive for manufacturers to comply
with standards by making already
highly efficient products even more
efficient. (NEMA, No. 47 at p. 9)
DOE recognizes that there is an
opportunity cost associated with any
investment, and agrees that
manufacturers would need to spend
capital to meet today’s standard that
they would not have to spend in the
base case. As a result, manufacturers
must determine the extent to which they
will balance investment in the
traditional ballast market with that in
emerging technologies or other ventures.
DOE includes the product and capital
conversion costs necessary to meet
today’s standard in its analysis.
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d. Component Availability
OSI stated that there are currently
long lead times for many electronic
components. As DOE standards push
the fluorescent lamp ballast industry to
higher efficiency components,
manufacturers will have limited choices
in what components they are able to
receive from suppliers, causing longer
product lead times and decreased
product availability. (OSI, Public
Meeting Transcript, No. 43 at p. 65)
DOE recognized this component
shortage in the April 2011 NOPR (76 FR
20090, 20139 (April 11, 2011)), but DOE
projects limited component availability
to be a relatively short term
phenomenon arising from the capacity
reduction that occurred in the recent
recession and that component suppliers
will ultimately adjust. DOE addresses
this issue again in full in section
VII.B.2.c of today’s notice.
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e. Impact on Competition
NEMA stated that manufacturers may
lose their ability to differentiate their
products because they will need to
remove premium features to meet price
pressure and proposed standard levels.
This would force all manufacturers to
offer the same basic product. NEMA
states that DOE should ensure that
manufacturers are able to offer products
above the standard in order to
differentiate themselves. (NEMA, No. 47
at p. 9) NEEP, while agreeing that high
efficiency ballasts may be commoditized
by this standard, states that
manufacturers will retain opportunities
for differentiation by focusing on
dimming ballasts and controls. (NEEP,
No. 49 at pp. 3–4)
DOE agrees that ballast manufacturers
may not be able to maintain today’s
margins after standards become
effective, particularly in the short run,
as demonstrated by the markup
scenarios described in section V.H.2.
DOE disagrees, however, that
manufacturers will no longer be able to
differentiate themselves. For some
minimally compliant products, DOE
agrees with manufacturers that price
competition will play a large role in the
market, as is currently the case.
Manufacturers may continue to
differentiate in domains other than
price, including premium features such
as Type CC protection, cold temperature
rating, case size, and lamp striation
control. Because of this effort to
differentiate, as discussed in the section
V.H.1, DOE included costs associated
with upgrading non-compliant
products, even when a compliant
product already exists in the category.
Therefore, DOE believes NEMA’s
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concerns are accounted for in DOE’s
analysis.
NEMA stated that manufacturers may
not be able to complete the redesigns
needed to meet the max tech levels
proposed in the April 2011 NOPR (76
FR 20090 (April 11, 2011)). (NEMA, No.
47 at p. 9) NEEP, however, believes that
by setting efficiency levels such that a
select subset of existing NEMA
Premium ballasts qualify at today’s
standard levels, the market would not
be faced with a shortage of qualifying
products and major shift in R&D
resources. (NEEP, No. 49 at p. 2)
At TSL 3A, the level promulgated in
today’s final rule, DOE projects that 38
percent of shipments already meet the
standard. The reconciliation of the DOE
and NEMA test data and the substantial
share of shipments at the proposed level
indicate that the industry will be able to
meet market demand by the compliance
date.
5. Manufacturer Interviews
DOE interviewed manufacturers
representing more than 90 percent of
fluorescent lamp ballast sales. These
interviews were in addition to those
DOE conducted as part of the
engineering analysis. DOE outlined the
key issues for the rulemaking for
manufacturers in the NOPR. 76 FR
20090, 20139–40 (April 11, 2011). DOE
considered the information received
during these interviews in the
development of the NOPR and this final
rule.
6. Sub-Group Impact Analysis
During the NOPR phase, DOE
identified two sub-groups for a separate
impact analysis—small manufacturers
and sign ballast manufacturers. DOE
describes the impacts on small
manufacturers in section VIII.B and the
impacts on sign ballast manufacturers in
section VII.B.2.d.
I. Employment Impact Analysis
DOE considers employment impacts
in the domestic economy as one factor
in selecting a standard. Employment
impacts consist of direct and indirect
impacts. Direct employment impacts are
any changes in the number of
employees working for manufacturers of
the appliance products that are the
subject of this rulemaking, their
suppliers, and related service firms. The
MIA addresses the direct employment
impacts that concern ballast
manufacturers in section VII.B.2.b.
Indirect employment impacts are
changes in employment within the
larger economy that occur due to the
shift in expenditures and capital
investment caused by the purchase and
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operation of more efficient products,
and are addressed in this section.
The indirect employment impacts of
standards consist of the net jobs created
or eliminated in the national economy,
outside of the manufacturing sector
being regulated, due to: (1) Reduced
spending on energy by end users; (2)
reduced spending on new energy
supplies by the utility industry; (3)
increased spending on new products to
which the new standards apply; and (4)
the effects of those three factors
throughout the economy. DOE expects
the net monetary savings from standards
to be redirected to other forms of
economic activity, and expects these
shifts in spending and economic activity
to affect the demand for labor in the
short term.
One method for assessing the possible
effects of such shifts in economic
activity on the demand for labor is to
compare sector employment statistics
developed by the Labor Department’s
Bureau of Labor Statistics (BLS). (Data
on industry employment, hours, labor
compensation, value of production, and
the implicit price deflator for output for
these industries are available upon
request by calling the Division of
Industry Productivity Studies ((202)
691–5618) or by sending a request by
email to dipsweb@bls.gov. These data
are also available at https://www.bls.gov/
news.release/prin1.nr0.htm.) The BLS
regularly publishes its estimates of the
number of jobs per million dollars of
economic activity in different sectors of
the economy, as well as the jobs created
elsewhere in the economy by this same
economic activity. Data from BLS
indicate that expenditures in the utility
sector generally create fewer jobs (both
directly and indirectly) than
expenditures in other sectors of the
economy. There are many reasons for
these differences, including wage
differences and the fact that the utility
sector is more capital intensive and less
labor intensive than other sectors. See
Bureau of Economic Analysis, Regional
Multipliers: A User Handbook for the
Regional Input-Output Modeling System
(RIMS II), Washington, DC, U.S.
Department of Commerce, 1992.
Energy conservation standards have
the effect of reducing consumer utility
bills. Because reduced consumer
expenditures for energy likely lead to
increased expenditures in other sectors
of the economy, the general effect of
efficiency standards is to shift economic
activity from a less labor-intensive
sector (i.e., the utility sector) to more
labor-intensive sectors (e.g., the retail
and manufacturing sectors). Thus, based
on the BLS data alone, DOE’s analysis
shows that net national employment
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will increase due to shifts in economic
activity resulting from new and
amended standards for ballasts.
In developing today’s adopted
standards, DOE estimated indirect
national employment impacts using an
input-output (I–O) model of the U.S.
economy called Impact of Sector Energy
Technologies (ImSET), version 3.1.1.
ImSET is a spreadsheet model of the
U.S. economy that focuses on 187
sectors most relevant to industrial,
commercial, and residential building
energy use. (Roop, J.M., M.J. Scott, and
R.W. Schultz, ImSET 3.1: Impact of
Sector Energy Technologies (PNNL18412 Pacific Northwest National
Laboratory) (2009). Available at https://
www.pnl.gov/main/publications/
external/technical_reports/PNNL18412.pdf.) ImSET is a special purpose
version of the ‘‘U.S. Benchmark
National Input-Output’’ model,
designed to estimate the national
employment and income effects of
energy-saving technologies. The ImSET
software includes a computer-based I–O
model with structural coefficients to
characterize economic flows among the
187 sectors. ImSET’s national economic
I–O structure is based on a 2002 U.S.
benchmark table (Stewart, R.L., J.B.
Stone, and M.L. Streitwieser, ‘‘U.S.
Benchmark Input-Output Accounts,
2002,’’ Survey of Current Business (Oct.
2007)), specially aggregated to the 187
sectors. DOE estimated changes in
expenditures using the NIA spreadsheet.
Using ImSET, DOE estimated the net
national, indirect-employment impacts
on employment by sector of the trial
standard levels for ballasts.
DOE notes that ImSET is not a general
equilibrium forecasting model, and
understands the uncertainties involved
in projecting employment impacts,
especially changes in the later years of
the analysis.4 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. Because
ImSET predicts small job impacts
resulting from this rule, regardless of
these uncertainties, the actual job
impacts are likely to be negligible in the
overall economy. DOE may consider the
use of other modeling approaches for
examining long run employment
impacts.
DOE also notes that the employment
impacts estimated with ImSET for the
entire economy differ from the
employment impacts in the lighting
manufacturing sector estimated in
Chapter 13 using the Government
Regulatory Impact Model (GRIM). The
methodologies used and the sectors
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analyzed in the ImSET and GRIM
models are different.
DOE received two comments on the
April 2011 NOPR, inquiring whether
DOE’s employment analysis accounted
for effects on ballast manufacturer
employment, and if sector-specific
results could be extracted from the
ImSET model output. (Acuity Brands,
Public Meeting Transcript, No. 43 at p.
229; Philips, Public Meeting Transcript,
No. 43 at p. 227.) As discussed
previously in this section, DOE’s
employment analysis models national
effects on indirect employment
(excluding ballast manufacturers) due to
shifts in expenditures and capital
investment caused by the purchase and
operation of more efficient appliances.
As previously noted, the MIA addresses
direct employment impacts on ballast
manufacturers in section VII.B.2.b.
DOE notes that the indirect
employment numbers generated by
ImSET are an estimate of the job
impacts of the projected national energy
and cost savings resulting from new or
amended standards. These calculated
impacts assume that the 187 sectors in
the ImSET model are unchanged from
the time that the I–O parameters were
estimated (last updated in 2008 using
year 2002 Economic Census data). As
noted in the ImSET documentation,
actual job creation will depend on
future labor market supply conditions
and macroeconomic policy.
DOE reviewed current ImSET sectoral
details and identified one economic
sector that corresponds with lighting
product manufacturers, excluding lamp
bulb and related parts (sector S111,
Lighting Fixture Manufacturing). While
this sector could encompass some
ballast manufacturers, DOE notes that it
is not exclusively representative of
ballasts. Further, while ImSET can
produce gross product impacts (in
dollars) by sector, it does not produce
sector-specific employment figures.
Rather, ImSET characterizes economic
flows among and interactions between
187 sectors in the model. Producing
sector-specific employment figures
would require DOE to artificially
constrain its ImSET input data, which
could reduce the meaningfulness of the
results. DOE therefore did not calculate
sector S111 employment figures, and
retained its NOPR employment analysis
approach for this final rule.
For more details on the employment
impact analysis, see chapter 15 of the
final rule TSD.
J. Utility Impact Analysis
The utility impact analysis includes
estimates of the effects of the adopting
new or amended standards on the utility
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industry. For this analysis, DOE used
the NEMS–BT model to generate
forecasts of electricity consumption,
electricity generation by plant type, and
electricity generating capacity by plant
type that would result from each TSL.
The estimated impacts of a standard are
estimated to be the differences between
values forecasted by NEMS–BT and the
values in the AEO2010 reference case.
In response to the April 2011 NOPR,
NEEA, NPCC and NEEP commented that
DOE did not consider the avoided costs
of power plant construction
corresponding to the avoided generation
capacity from new or amended
standards. By NEEA and NPCC’s
estimates, the present value cost of new
generation capacity to supply the
cumulative energy savings at TSL 3
would nearly equal DOE’s cumulative
NPV at TSL 3 (which excludes avoided
power plant and infrastructure
construction). NEEA and NPCC further
suggested that DOE examine the
difference in the value of total
electricity sales between the NEMS–BT
reference case and standards level cases,
which could serve as a proxy for the
economic value of the standard level to
all electricity consumers. (NPCC, Public
Meeting Transcript, No. 43 at p. 223;
NEEA and NPCC, No. 44 at pp. 9–10)
NEEP also commented that decreased
demand is shown to drive energy prices
down, benefiting consumers in general.
(NEEP, No. 49 at p. 4)
DOE acknowledges that the aggregate
economic benefits from avoided
construction of new generating capacity
and infrastructure are potentially large.
However, there may be negative effects
on some of the actors involved in
electricity supply, particularly power
plant providers and fuel suppliers.
There is also uncertainty about the
extent to which the benefits for
electricity users from reduced electricity
prices would be a transfer from actors
involved in electricity supply to
electricity consumers. DOE also takes
under advisement the guidance
provided by the Office of Management
and Budget (OMB) to Federal agencies
on identifying and measuring benefits
and costs in its regulatory analyses
(OMB Circular A–4, section E,
September 17, 2003). Specifically, at
page 38, Circular A–4 instructs that
transfers should be excluded from the
estimates of the benefits and costs of a
regulation. DOE applied this approach
for the utility impact analysis in the
April 2011 NOPR, as well as in this final
rule.
DOE is continuing to investigate the
extent to which projected changes in
electricity prices that result from
standards represent a net economic gain
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to the nation. In response to the
comments discussed in this section,
DOE included the estimated effects of
adopted standards on electricity prices
and the cumulative NPV of resulting
savings in electricity expenditures in
the TSD. DOE also included in the TSD
representative costs of avoided
electricity generation capacity by fuel
type, although these costs are provided
for illustrative purposes only. For more
details on the utility impact analysis,
see chapter 14 of the final rule TSD.
K. Environmental Assessment
Pursuant to the National
Environmental Policy Act of 1969 and
the requirements of DOE Order 451.1B:
NEPA Compliance Program, DOE has
prepared an environmental assessment
(EA) of the impacts of the new and
amended standards for ballasts in this
final rule, which it has included as
chapter 16 of the final rule TSD. DOE
found that the environmental effects
associated with the standards for
ballasts were not significant. Therefore,
DOE is issuing a Finding of No
Significant Impact (FONSI), pursuant to
NEPA, the regulations of the Council on
Environmental Quality (40 CFR parts
1500–1508), and DOE’s regulations for
compliance with NEPA (10 CFR part
1021). The FONSI is available in the
docket for this rulemaking.
In the EA, DOE estimated the
reduction in power sector emissions of
CO2, NOX, and Hg using the NEMS–BT
computer model. In the EA, NEMS–BT
is run similarly to the AEO NEMS,
except that ballast energy use is reduced
by the amount of energy saved (by fuel
type) due to each TSL. The inputs of
national energy savings come from the
NIA spreadsheet model, while the
output is the forecasted physical
emissions. The net benefit of each TSL
in today’s final rule is the difference
between the forecasted emissions
estimated by NEMS–BT at each TSL and
the AEO2010 Reference Case. NEMS–BT
tracks CO2 emissions using a detailed
module that provides results with broad
coverage of all sectors and inclusion of
interactive effects.
Sulfur dioxide (SO2) emissions from
affected electricity generating units
(EGUs) are subject to nationwide and
regional emissions cap-and-trade
programs, and DOE has preliminarily
determined that these programs create
uncertainty about the potential
amended standards’ impact on SO2
emissions. 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).
SO2 emissions from 28 eastern states
and DC are also limited under the Clean
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Air Interstate Rule (CAIR; 70 FR 25162
(May 12, 2005)), which created an
allowance-based trading program.
Although CAIR was remanded to the
Environmental Protection Agency (EPA)
by the U.S. Court of Appeals for the
District of Columbia Circuit (DC Circuit)
(see North Carolina v. EPA, 550 F.3d
1176 (DC Cir. 2008)), it remained in
effect temporarily, consistent with the
DC Circuit’s earlier opinion in North
Carolina v. EPA, 531 F.3d 896 (DC Cir.
2008). On July 6, 2010, EPA issued the
Transport Rule proposal, a replacement
for CAIR (75 FR 45210 (Aug. 2, 2010)),
and on July 6, 2011 EPA issued the final
Transport Rule, entitled the Cross-State
Air Pollution Rule. 76 FR 48208 (August
8, 2011). (https://www.epa.gov/
crossstaterule/). Because the AEO2010
NEMS used for today’s final rule
assumes the implementation of CAIR,
DOE has not been able to take into
account the effects of the Transport Rule
for this rulemaking.53
The attainment of emissions caps is
typically flexible among EGUs and is
enforced through the use of emissions
allowances and tradable permits. Under
existing EPA regulations, any excess
SO2 emissions allowances resulting
from the lower electricity demand
caused by the imposition of an
efficiency standard could be used to
permit offsetting increases in SO2
emissions by any regulated EGU.
However, if the new and amended
standards resulted in a permanent
increase in the quantity of unused
emissions allowances, there would be
an overall reduction in SO2 emissions
from the standards. While there remains
some uncertainty about the ultimate
effects of efficiency standards on SO2
emissions covered by the existing capand-trade system, the NEMS–BT
modeling system that DOE uses to
forecast emissions reductions currently
indicates that no physical reductions in
power sector emissions would occur for
SO2.
As discussed above, the AEO2010
NEMS used for today’s final rule
assumes the implementation of CAIR,
which established a cap on NOX
emissions in 28 eastern states and the
District of Columbia. With CAIR in
effect, the energy conservation
standards for ballasts are expected to
have little or no physical effect on NOX
emissions in those states covered by
CAIR, for the same reasons that they
may have little effect on SO2 emissions.
However, the adopted standards would
be expected to reduce NOX emissions in
53 DOE notes that future iterations of the NEMS–
BT model will ncorporate any changes necessitated
by issuance of the Transport Rule.
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70591
the 22 states not affected by CAIR. For
these 22 states, DOE used the NEMS–BT
to estimate NOX emissions reductions
from the standards considered in
today’s final rule.
Similar to emissions of SO2 and NOX,
future emissions of Hg would have been
subject to emissions caps. In May 2005,
EPA issued the Clean Air Mercury Rule
(CAMR). 70 FR 28606 (May 18, 2005).
CAMR would have permanently capped
emissions of Hg for new and existing
coal-fired power plants in all states by
2010. However, on February 8, 2008, the
DC Circuit issued a decision in New
Jersey v. Environmental Protection
Agency, 517 F.3d 574 (DC Cir. 2008), in
which it vacated CAMR. EPA has
decided to develop emissions standards
for power plants under Section 112 of
the Clean Air Act, consistent with the
DC Circuit’s opinion on CAMR. See
https://www.epa.gov/air/mercuryrule/
pdfs/certpetition_withdrawal.pdf.
Pending EPA’s forthcoming revisions to
the rule, DOE is excluding CAMR from
its environmental assessment. In the
absence of CAMR, a DOE standard
would likely reduce Hg emissions and
DOE used NEMS–BT to estimate these
reductions. However, DOE continues to
review the impact of rules that reduce
energy consumption on Hg emissions,
and may revise its assessment of Hg
emission reductions in future
rulemakings.
L. Monetizing Carbon Dioxide and Other
Emissions Impacts
As part of the development of this
final rule, DOE considered the estimated
monetary benefits likely to result from
the reduced emissions of CO2 and NOX
that are expected to result from each of
the TSLs considered. In order to make
this calculation similar 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
forecast period for each TSL. This
section summarizes the basis for the
monetary values used for each of these
emissions and presents the values
considered in this rulemaking.
For today’s final rule, DOE is relying
on a set of values for the SCC that was
developed by an interagency process. A
summary of the basis for these values is
provided in the following sections, and
a more detailed description of the
methodologies used is provided as an
appendix to chapter 17 of the final rule
TSD.
1. Social Cost of Carbon
Under section 1(b) of Executive Order
12866, agencies must, to the extent
permitted by law, ‘‘assess both the costs
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and the benefits of the intended
regulation and, recognizing that some
costs and benefits are difficult to
quantify, propose or adopt a regulation
only upon a reasoned determination
that the benefits of the intended
regulation justify its costs.’’ The purpose
of the SCC estimates presented here is
to allow agencies to incorporate the
monetized social benefits of reducing
CO2 emissions into cost-benefit analyses
of regulatory actions that have small, or
‘‘marginal,’’ impacts on cumulative
global emissions. The estimates are
presented with an acknowledgement of
the many uncertainties involved and
with a clear understanding that they
should be updated over time to reflect
increasing knowledge of the science and
economics of climate impacts.
As part of the interagency process that
developed these SCC estimates,
technical experts from numerous
agencies met on a regular basis to
consider public comments, explore the
technical literature in relevant fields,
and discuss key model inputs and
assumptions. The main objective of this
process was to develop a range of SCC
values using a defensible set of input
assumptions grounded in the existing
scientific and economic literatures. In
this way, key uncertainties and model
differences transparently and
consistently inform the range of SCC
estimates used in the rulemaking
process.
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a. Monetizing Carbon Dioxide Emissions
The SCC is an estimate of the
monetized damages associated with an
incremental increase in carbon
emissions in a given year. It is intended
to include (but is not limited to) changes
in net agricultural productivity, human
health, property damages from
increased flood risk, and the value of
ecosystem services. Estimates of the
SCC are provided in dollars per metric
ton of CO2.
When attempting to assess the
incremental economic impacts of CO2
emissions, the analyst faces a number of
serious challenges. A recent report from
the National Research Council 54 points
out that any assessment will suffer from
uncertainty, speculation, and lack of
information about (1) Future emissions
of greenhouse gases, (2) the effects of
past and future emissions on the climate
system, (3) the impact of changes in
climate on the physical and biological
environment, and (4) the translation of
these environmental impacts into
54 National
Research Council. Hidden Costs of
Energy: Unpriced Consequences of Energy
Production and Use. National Academies Press:
Washington, DC (2009).
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economic damages. As a result, any
effort to quantify and monetize the
harms associated with climate change
will raise serious questions of science,
economics, and ethics and should be
viewed as provisional.
Despite the serious limits of both
quantification and monetization, SCC
estimates can be useful in estimating the
social benefits of reducing CO2
emissions. Consistent with the directive
in Executive Order 12866 quoted
previously in this section, the purpose
of the SCC estimates presented here is
to make it possible for Federal agencies
to incorporate the social benefits from
reducing CO2 emissions into costbenefit analyses of regulatory actions
that have small, or ‘‘marginal,’’ impacts
on cumulative global emissions. Most
Federal regulatory actions can be
expected to have marginal impacts on
global emissions.
For such policies, the agency can
estimate the benefits from reduced (or
costs from increased) emissions in any
future year by multiplying the change in
emissions in that year by the SCC value
appropriate for that year. The net
present value of the benefits can then be
calculated by multiplying each of these
future benefits by an appropriate
discount factor and summing across all
affected years. This approach assumes
that the marginal damages from
increased emissions are constant for
small departures from the baseline
emissions path, an approximation that
is reasonable for policies that have
effects on emissions that are small
relative to cumulative global CO2
emissions. For policies that have a large
(non-marginal) impact on global
cumulative emissions, there is a
separate question of whether the SCC is
an appropriate tool for calculating the
benefits of reduced emissions. This
concern is not applicable to this notice,
and DOE does not attempt to answer
that question here.
At the time of the preparation of this
notice, the most recent interagency
estimates of the potential global benefits
resulting from reduced CO2 emissions in
2010, expressed in 2010$, were $4.9,
$22.3, $36.5, and $67.6 per metric ton
avoided. For emissions reductions that
occur in later years, these values grow
in real terms over time. Additionally,
the interagency group determined that a
range of values from 7 percent to 23
percent should be used to adjust the
global SCC to calculate domestic
effects,55 although preference is given to
55 It is recognized that this calculation for
domestic values is approximate, provisional, and
highly speculative. There is no a priori reason why
domestic benefits should be a constant fraction of
net global damages over time.
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consideration of the global benefits of
reducing CO2 emissions.
It is important to emphasize that the
interagency process is committed to
updating these estimates as the science
and economic understanding of climate
change and its impacts on society
improves over time. Specifically, the
interagency group has set a preliminary
goal of revisiting the SCC values within
2 years or at such time as substantially
updated models become available, and
to continue to support research in this
area. In the meantime, the interagency
group will continue to explore the
issues raised by this analysis and
consider public comments as part of the
ongoing interagency process.
b. Social Cost of Carbon Values Used in
Past Regulatory Analyses
To date, economic analyses for
Federal regulations have used a wide
range of values to estimate the benefits
associated with reducing CO2 emissions.
In the final model year 2011 CAFE rule,
the U.S. Department of Transportation
(DOT) used both a ‘‘domestic’’ SCC
value of $2 per ton of CO2 and a
‘‘global’’ SCC value of $33 per ton of
CO2 for 2007 emission reductions (in
2007$), increasing both values at 2.4
percent per year.56 DOT also included a
sensitivity analysis at $80 per ton of
CO2. See Average Fuel Economy
Standards Passenger Cars and Light
Trucks Model Year 2011, 74 FR 14196
(March 30, 2009) (Final Rule); Final
Environmental Impact Statement
Corporate Average Fuel Economy
Standards, Passenger Cars and Light
Trucks, Model Years 2011–2015 at 3–90
(Oct. 2008) (Available at: https://
www.nhtsa.gov/fuel-economy). A
domestic SCC value is meant to reflect
the value of damages in the United
States resulting from a unit change in
CO2 emissions, while a global SCC value
is meant to reflect the value of damages
worldwide.
A 2008 regulation proposed by DOT
assumed a domestic SCC value of $7 per
ton of CO2 (in 2006$) for 2011 emission
reductions (with a range of $0–$14 for
sensitivity analysis), also increasing at
2.4 percent per year. See Average Fuel
Economy Standards, Passenger Cars
and Light Trucks, Model Years 2011–
2015, 73 FR 24352 (May 2, 2008)
(Proposed Rule); Draft Environmental
Impact Statement Corporate Average
Fuel Economy Standards, Passenger
Cars and Light Trucks, Model Years
2011–2015 at 3–58 (June 2008)
(Available at: https://www.nhtsa.gov/
fuel-economy). A regulation for
56 Throughout this section, references to tons of
CO2 refer to metric tons.
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packaged terminal air conditioners and
packaged terminal heat pumps finalized
by DOE in October of 2008 used a
domestic SCC range of $0 to $20 per ton
CO2 for 2007 emission reductions (in
2007$). 73 FR 58772, 58814 (Oct. 7,
2008) In addition, EPA’s 2008 Advance
Notice of Proposed Rulemaking on
Regulating Greenhouse Gas Emissions
Under the Clean Air Act identified what
it described as ‘‘very preliminary’’ SCC
estimates subject to revision. 73 FR
44354 (July 30, 2008). EPA’s global
mean values were $68 and $40 per ton
CO2 for discount rates of approximately
2 percent and 3 percent, respectively (in
2006$ for 2007 emissions).
In 2009, an interagency process was
initiated to offer a preliminary
assessment of how best to quantify the
benefits from reducing CO2 emissions.
To ensure consistency in how benefits
are evaluated across agencies, the
Administration sought to develop a
transparent and defensible method,
specifically designed for the rulemaking
process, to quantify avoided climate
change damages from reduced CO2
emissions. The interagency group did
not undertake any original analysis.
Instead, it combined SCC estimates from
the existing literature to use as interim
values until a more comprehensive
analysis could be conducted. The
outcome of the preliminary assessment
by the interagency group was a set of
five interim values: global SCC
estimates for 2007 (in 2006$) of $55,
$33, $19, $10, and $5 per ton of CO2.
These interim values represent the first
sustained interagency effort within the
U.S. government to develop an SCC for
use in regulatory analysis. The results of
this preliminary effort were presented in
several proposed and final rules and
were offered for public comment in
connection with proposed rules,
including the joint EPA–DOT fuel
economy and CO2 tailpipe emission
proposed rules.
c. Current Approach and Key
Assumptions
Since the release of the interim
values, the interagency group
reconvened on a regular basis to
generate improved SCC estimates,
which were considered for this final
rule. Specifically, the group considered
public comments and further explored
the technical literature in relevant
fields. The interagency group relied on
three integrated assessment models
commonly used to estimate the SCC: the
FUND, DICE, and PAGE models.57
These models are frequently cited in the
peer-reviewed literature and were used
in the last assessment of the
Intergovernmental Panel on Climate
Change. Each model was given equal
weight in the SCC values that were
developed.
Each model takes a slightly different
approach to model how changes in
emissions result in changes in economic
70593
damages. A key objective of the
interagency process was to enable a
consistent exploration of the three
models while respecting the different
approaches to quantifying damages
taken by the key modelers in the field.
An extensive review of the literature
was conducted to select three sets of
input parameters for these models:
climate sensitivity, socio-economic and
emissions trajectories, and discount
rates. A probability distribution for
climate sensitivity was specified as an
input into all three models. In addition,
the interagency group used a range of
scenarios for the socio-economic
parameters and a range of values for the
discount rate. All other model features
were left unchanged, relying on the
model developers’ best estimates and
judgments.
The interagency group selected four
SCC values for use in regulatory
analyses. Three values are based on the
average SCC from three integrated
assessment models, at discount rates of
2.5, 3, and 5 percent. The fourth value,
which represents the 95th percentile
SCC estimate across all three models at
a 3-percent discount rate, is included to
represent higher-than-expected impacts
from temperature change further out in
the tails of the SCC distribution. For
emissions (or emission reductions) that
occur in later years, these values grow
in real terms over time, as depicted in
Table V.8.
TABLE V.8—SOCIAL COST OF CO2, 2010–2050
[In 2007 dollars per metric ton]
Discount rate
5% Avg
mstockstill on DSK4VPTVN1PROD with RULES2
2010
2015
2020
2025
2030
2035
2040
2045
2050
.................................................................................................................................................
.................................................................................................................................................
.................................................................................................................................................
.................................................................................................................................................
.................................................................................................................................................
.................................................................................................................................................
.................................................................................................................................................
.................................................................................................................................................
.................................................................................................................................................
It is important to recognize that a
number of key uncertainties remain, and
that current SCC estimates should be
treated as provisional and revisable
since they will evolve with improved
scientific and economic understanding.
The interagency group also recognizes
that the existing models are imperfect
and incomplete. As the National
Research Council report mentioned in
section V.L.1.a points out, there is
tension between the goal of producing
quantified estimates of the economic
damages from an incremental ton of
carbon and the limits of existing efforts
to model these effects. There are a
number of concerns and problems that
should be addressed by the research
community, including research
programs housed in many of the Federal
3% Avg
4.7
5.7
6.8
8.2
9.7
11.2
12.7
14.2
15.7
18:36 Nov 10, 2011
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35.1
38.4
41.7
45.9
50.0
54.2
58.4
61.7
65.0
3% 95th
64.9
72.8
80.7
90.4
100.0
109.7
119.3
127.8
136.2
agencies participating in the interagency
process to estimate the SCC.
DOE recognizes the uncertainties
embedded in the estimates of the SCC
used for cost-benefit analyses. As such,
DOE and others in the U.S. Government
intend to periodically review and
reconsider those estimates to reflect
increasing knowledge of the science and
economics of climate impacts, as well as
57 The models are described in appendix 16–A of
the final rule TSD.
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21.4
23.8
26.3
29.6
32.8
36.0
39.2
42.1
44.9
2.5% Avg
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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
improvements in modeling. In this
context, statements recognizing the
limitations of the analysis and calling
for further research take on exceptional
significance.
In summary, in considering the
potential global benefits resulting from
reduced CO2 emissions, DOE used the
most recent values identified by the
interagency process, adjusted to 2010$
using the GDP price deflator. For each
of the four cases specified, the values
used for emissions 2010 were $4.9,
$22.3, $36.5, and $67.6 per metric ton
avoided (values expressed in 2010$).58
To monetize the CO2 emissions
reductions expected to result from new
and amended standards for ballasts,
DOE used the values identified in Table
A1 of the ‘‘Social Cost of Carbon for
Regulatory Impact Analysis Under
Executive Order 12866,’’ which is
reprinted in appendix 17A of the final
rule TSD, appropriately adjusted to
2010$. To calculate a present value of
the stream of monetary values, DOE
discounted the values in each of the
four cases using the specific discount
rate that had been used to obtain the
SCC values in each case.
2. Valuation of Other Emissions
Reductions
mstockstill on DSK4VPTVN1PROD with RULES2
DOE investigated the potential
monetary benefit of reduced NOX
emissions from the TSLs it considered.
As noted in the previous section, DOE
has taken into account how new or
amended energy conservation standards
would reduce NOX emissions in those
22 states that are not affected by the
CAIR. DOE estimated the monetized
value of NOX emissions reductions
resulting from the standard levels
considered for today’s final rule based
on environmental damage estimates
found in the relevant scientific
literature. Available estimates suggest a
very wide range of monetary values,
ranging from $370 per ton to $3,800 per
ton of NOX from stationary sources,
measured in 2001$ (equivalent to a
range of $450 to $4,623 per ton in
2010$).59 In accordance with guidance
from the U.S. Office of Management and
Budget (OMB), DOE conducted two
calculations of the monetary benefits
derived using each of the economic
values used for NOX, one using a real
58 Table A1 presents SCC values through 2050.
For DOE’s calculation, it derived values after 2050
using the 3-percent per year escalation rate used by
the interagency group.
59 For additional information, refer to U.S. Office
of Management and Budget, Office of Information
and Regulatory Affairs, 2006 Report to Congress on
the Costs and Benefits of Federal Regulations and
Unfunded Mandates on State, Local, and Tribal
Entities, Washington, DC.
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discount rate of 3 percent and another
using a real discount rate of 7 percent.60
DOE is aware of multiple agency
efforts to determine the appropriate
range of values used in evaluating the
potential economic benefits of reduced
Hg emissions. DOE has decided to await
further guidance regarding consistent
valuation and reporting of Hg emissions
before it once again monetizes Hg
emissions in its rulemakings.
VI. Other Issues for Discussion
A. Proposed Standard Levels in April
2011 NOPR
In the April 2011 NOPR, DOE
proposed to adopt the max tech level,
which represented the highest level that
was technologically feasible for a
sufficient diversity of products
(spanning several ballast factors,
numbers of lamps per ballast, and types
of lamps operated). DOE received
several comments supporting the
proposed standard levels. NEEP
commented that assuming the test data
discrepancy between DOE’s and
NEMA’s data is resolved, the proposed
standards would greatly benefit the
Northeast region of the United States
where energy prices are typically higher
than the rest of the country, increasing
the magnitude of life cycle cost savings
for those consumers. They also observed
that locking in strong efficiency levels
for ballasts would complement the
strong fluorescent lamp standards that
are set to take effect on July 14, 2012.
NEEP added that the NOPR proposal
would help the Northeast region meet
its energy savings and emission
reduction goals including those set
forward in Massachusetts’ Global
Warming Solutions Act of 2008. (NEEP,
No. 49 at pp. 2–4)
EEI also supported the proposed
standards and agreed they would be cost
effective for the vast majority of
commercial consumers based on the
analysis and data put forward in the
April 2011 NOPR. (EEI, No. 48 at p. 1)
In addition to the above feedback,
DOE also received several comments
that disagreed with the proposed
standard levels. These comments are
discussed in more detail in the
following paragraphs.
NEMA disagreed with DOE’s proposal
to adopt the max tech efficiency levels.
NEMA stated that, even when using
DOE data, very few products met the
proposed minimum BLE requirements.
For example, only one residential,
T5SO, and T5HO ballast met DOE’s
proposed standard levels. NEMA
commented that the DOE is therefore
60 OMB, Circular A–4: Regulatory Analysis (Sept.
17, 2003).
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Frm 00048
Fmt 4701
Sfmt 4700
using only one product to develop a
rule. (NEMA, Public Meeting Transcript,
No. 43 at p. 29–32) NEMA analyzed its
own dataset and suggested an
alternative level that allowed the
majority of manufacturers’ NEMA
Premium products, which represent
their most efficient product offerings.
NEMA noted that although it is not
shown in the submitted data, several
products they manufacture are not
NEMA Premium products and therefore
would not meet their proposal. At a
minimum, NEMA requested that two
manufacturers’ complete product lines
be able to meet the standard levels.
NEMA also added that they would
support a proposal that does not create
limited availability, disruption in the
market, or extreme R&D redesign costs.
(NEMA, Public Meeting Transcript, No.
43 at p. 41–5; NEMA, No. 47 at p. 6)
ASAP disagreed with NEMA’s
recommendation that all manufacturers’
high efficiency products should meet
the highest level. ASAP noted that
based on the DOE data, there were two
products that were compliant in each
class. ASAP therefore approved of
DOE’s decision to adopt the max tech
level. (ASAP, Public Meeting
Transcript, No. 43 at p. 50–1; ASAP, No.
46 at p. 1) NEEP agreed and supported
the result that only a subset of NEMA
Premium products met the proposed
standard. (NEEP, No. 49 at p. 1–2) CA
Utilities also agreed that all products
with a NEMA Premium designation
should not meet the proposed standard
because NEMA Premium covers a range
of efficiency with some ballasts only
meeting TSL1 or TSL2 as analyzed in
the April 2011 NOPR. They noted that
they reviewed the data and found that
there is at least one product for each
specific utility that meets the standard,
though all manufacturers may not have
an offering for each utility. (CA Utilities,
Public Meeting Transcript, No. 43 at p.
62–3; CA Utilities, No. 45 at p. 4; CA
Utilities, No. 58 at p. 3)
In response to the August 2011
NODA, NEMA recommended adopting
lower efficiency levels for several of the
product classes. NEMA recommended
adopting EL2 instead of EL3 for the IS/
RS and PS product classes because the
incremental cost of product redesign at
EL3 is not outweighed by the
incremental energy savings between EL2
and EL3. NEMA added that at EL2,
manufacturers would focus on retiring
non-compliant products and improving
existing product lines rather than
redesigning a large number of models.
(NEMA, No. 56 at p. 3)
For the same reasons, NEMA
recommended adopting EL2 for the 8foot HO IS/RS product class. They noted
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that the energy savings at EL2 are
similar to those achieved at EL3 (the
level proposed in the April 2011 NOPR),
but EL3 imposes much greater costs on
manufacturers. (NEMA, No. 56 at p. 3)
Finally, NEMA recommended EL1 as
the standard level for residential ballasts
because linear fluorescent technology is
more efficient and cost-effective than
other traditional technologies and
therefore it does not make sense to
increase the cost burden on this pricesensitive market. (NEMA, No. 47 at p. 4;
NEMA, No. 56 at p. 3) EEI also
commented on residential ballasts,
stating that although they generally
agreed with the proposed standard
levels, they were concerned about the
impacts of the standards on some
residential consumers. EEI noted that
according to the NOPR proposal,
relative to the T8 baseline, 100 percent
of consumers have increased life-cycle
costs. 76 FR 20090, 20146 (April 11,
2011). (EEI, No. 48 at p. 2)
DOE determines efficiency levels as
described in section V.B.5, and then
assesses the impacts, including those on
manufacturers and industry
competition. DOE acknowledges that
conversion costs increase at higher
efficiency levels, but also notes that
higher levels result in increased energy
savings and NPV for the nation and
increased LCC savings for consumers.
Although each efficiency level may not
allow a full product line from every
manufacturer, DOE has concluded that,
for the levels it is adopting in this final
rule, the benefits outweigh the burdens.
See section VII.C.2 for more details.
B. Universal Versus Dedicated Input
Voltage
NEMA also expressed concern that
the proposed standards may eliminate
universal voltage ballasts from the
market. NEMA commented that
although dedicated voltage ballasts are
more efficient, consumers demand
universal voltage instead of dedicated
voltage products. NEMA stated that
manufacturers may need to shift back to
the more efficient dedicated voltage
products to meet the proposed
standards. This shift away from
universal voltage would go against
industry and consumer demand.
(NEMA, Public Meeting Transcript, No.
43 at p. 36) NEEA and NPCC
commented that their data assessment
strongly suggested ballast efficiency
does not vary consistently by input
voltage, and that universal voltage
ballasts can be as efficient as, or more
efficient than, fixed input voltage
ballasts in any individual product class
and utility category. (NEEA and NPCC,
No. 44 at p. 3) CA Utilities also stated
that based on experience and review of
DOE’s test data, they found no
indication that universal voltage ballasts
are consistently less efficient than
dedicated voltage ballasts and that
therefore universal and dedicated
voltage ballasts should be held to the
same standard levels. (NEMA, No. 56 at
p. 3; CA Utilities, No. 45 at p. 6)
DOE agrees with the CA Utilities that
test data shows universal voltage
ballasts to be as efficient or more
efficient than dedicated input voltage
ballasts. DOE also recognizes that there
is significant market demand for
universal voltage fluorescent lamp
ballasts. In both the April 2011 NOPR
and this final rule, DOE’s max tech
efficiency levels are met by universal
voltage ballasts. For the IS/RS product
class, 80 percent (37 out of 46) of
ballasts that meet the proposed standard
are universal voltage ballasts; for the PS
product class, over 95 percent (20 out of
21) are universal voltage ballasts.
Therefore, DOE does not believe the
final rule prohibits the manufacture and
sale of universal voltage products.
70595
C. Implementation of Adopted Standard
Levels
In the April 2011 NOPR, DOE
proposed that standards for all covered
ballasts require compliance three years
following publication of the final rule in
the Federal Register. P.R. China noted
that, for several product classes, DOE
proposed increasing efficiency
requirements by a large percentage and
that adapting to the proposed standards
could create a large burden on
manufacturers. P.R. China suggested
that DOE gradually phase in standards,
transitioning from the lowest considered
efficiency level through the higher
efficiency levels to reach the proposed
standard. P.R. China stated that this
approach is internationally accepted
and would ease the initial burden
placed on manufacturers. (P.R. China,
No. 51 at p. 3)
DOE acknowledges that for certain
ballast types the standards adopted
represent a large increase in efficiency
relative to existing standards or the
analyzed baseline. However, as
described in section VII.C.2, DOE
analyzed the burden on manufacturers
pursuant to 42 U.S.C. 6295(o) and
determined that it was outweighed by
the benefits of the rule to consumers
and the nation.
VII. Analytical Results and Conclusions
A. Trial Standard Levels
DOE analyzed the benefits and
burdens of the TSLs developed for
today’s final rule. Table VII.1 presents
the trial standard levels and the
corresponding product class efficiency
levels for all product classes. See the
engineering analysis in section V.B.5 of
this final rule for a more detailed
discussion of the efficiency levels.
TABLE VII.1—TRIAL STANDARD LEVELS
mstockstill on DSK4VPTVN1PROD with RULES2
Product class
TSL 1
IS and RS ballasts (not classified as residential) that operate .......................................................
4-foot MBP lamps
2-foot U-shaped lamps
8-foot slimline lamps
PS ballasts (not classified as residential) that operate ...................................................................
4-foot MBP lamps
2-foot U-shaped lamps
4-foot MiniBP SO lamps
4-foot MiniBP HO lamps
IS and RS ballasts (not classified as sign ballasts) that operate: 8-foot HO lamps .......................
PS ballasts (not classified as sign ballasts) that operate: 8-foot HO lamps ...................................
Sign ballasts that operate: 8-foot HO lamps ...................................................................................
IS and RS residential ballasts that operate .....................................................................................
4-foot MBP lamps
2-foot U-shaped lamps
8-foot slimline lamps
PS residential ballasts that operate .................................................................................................
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TSL 2
TSL 3A
TSL 3B
EL1
EL2
EL3
EL3
EL1
EL2
EL3
EL3
EL1
EL1
EL1
EL1
EL2
EL2
EL1
EL1
EL2
EL2
EL1
EL1
EL3
EL3
EL1
EL2
EL1
EL1
EL1
EL2
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70596
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.1—TRIAL STANDARD LEVELS—Continued
Product class
TSL 1
TSL 2
TSL 3A
TSL 3B
4-foot MBP lamps
2-foot U-shaped lamps
mstockstill on DSK4VPTVN1PROD with RULES2
In this section, DOE presents the
analytical results for the TSLs of the
product classes that DOE analyzed
directly (the ‘‘representative product
classes’’). DOE scaled the standards for
these representative product classes to
create standards for other product
classes that were not directly analyzed
(the 8-foot HO PS and residential PS
product classes), as set forth in chapter
5 of the final rule TSD.
TSL 1, which would set energy
conservation standards at EL1 for all
product classes, would eliminate the
majority of currently available 4-foot
MBP T12 RS (commercial and
residential), low-efficiency 4-foot MBP
T8 PS, magnetic 8-foot HO, and
magnetic sign ballasts. Based on these
impacts, TSL 1 would likely cause a
migration from 4-foot MBP T12 RS
ballasts (both commercial and
residential) to 4-foot MBP T8 IS ballasts.
TSL 1 also prevents inefficient T5
standard output and high output
ballasts from becoming prevalent in
future years. DOE would not anticipate
any impact of TSL 1 on consumers of 8foot slimline ballasts.
TSL 2 would establish energy
conservation standards at EL2 for the IS/
RS, PS, and 8-foot HO IS/RS product
classes. This level would likely
eliminate low efficiency two-lamp 4foot MBP T8 IS commercial ballasts and
the least efficient T12 8-foot slimline
ballasts, causing a migration toward
high efficiency two lamp 4-foot MBP T8
IS ballasts and 8-foot T8 slimline
ballasts. DOE does not anticipate any
impact of TSL 2 on four-lamp 4-foot
MBP T8 IS ballast consumers. For PS
ballasts, high-efficiency 4-foot MBP T8
ballasts and high-efficiency T5 standard
output and high output ballasts are
required at TSL 2. For the 8-foot HO IS/
RS product class, this level would likely
result in the elimination of the majority
of current T12 electronic ballasts, but
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can be met with T8 electronic ballasts.
As with TSL 1, TSL 2 would continue
to use EL1 for the residential IS/RS
product class, eliminating currently
available 4-foot MBP T12 RS ballasts,
but allowing higher efficiency T8
residential ballasts. In addition, the sign
ballast efficiency level remains
unchanged from TSL1.
TSL 3A would establish energy
conservation standards at the maximum
technologically feasible level for all
product classes except for residential
and 8-foot HO IS/RS product classes. As
with TSL 2, the 8-foot HO IS/RS product
class at TSL 3A results in the
elimination of current T12 electronic
ballasts, but can be met with T8
electronic ballasts. Consistent with TSLs
1 and 2, TSL 3A also requires EL1 for
the residential IS/RS product class. This
TSL represents the most stringent
efficiency requirements where a positive
LCC savings for each representative
product class is maintained.
TSL 3B represents the maximum
technologically feasible level for all
product classes. This level would
establish energy conservation standards
at EL1 for sign ballasts, EL2 for
residential IS/RS product classes, and
EL3 for the commercial IS/RS and PS,
and 8-foot HO IS/RS product classes.
TSL 3B represents the highest EL
analyzed in all representative product
classes and is the max tech TSL. Ballasts
that meet TSL 3B represent the most
efficient models tested by DOE in their
respective representative product
classes.
B. Economic Justification and Energy
Savings
1. Economic Impacts on Individual
Consumers
a. Life-Cycle Cost and Payback Period
Consumers affected by new or
amended standards usually experience
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Fmt 4701
Sfmt 4700
higher purchase prices and lower
operating costs. Generally, these effects
on individual consumers are best
summarized by changes in LCCs and by
the payback period. DOE calculated the
LCC and PBP values for the potential
standard levels considered in this
rulemaking to provide key inputs for
each TSL. These values are reported by
product class in Table VII.12 through
Table VII.15. Each table includes the
average total LCC and the average LCC
savings, as well as the fraction of
product consumers for which the LCC
will either decrease (net benefit), or
increase (net cost) relative to the
baseline case. In limited cases, a more
efficient (i.e., higher BLE) ballast will
have a higher total LCC and lower LCC
savings than a less efficient ballast (e.g.,
EL3 versus EL2 in Table VII.9). This is
because the higher-EL ballast has a
higher BF and system input power,
resulting in higher operating costs than
for the lower-EL ballast. The last
column in each table contains the
median PBPs for the consumer
purchasing a design compliant with the
TSL. Negative PBP values indicate a
reduction of both operating costs and
installed costs (i.e., there is no purchase
price increment for the consumer to
recover). Entries of ‘‘N/A’’ indicate
standard levels that do not reduce
operating costs, which prevents the
consumer from recovering the increased
purchase cost. This scenario did not
occur at any of the standard levels
adopted by DOE in today’s final rule.
The results for each TSL are presented
relative to the energy use distribution in
the base case (no amended standards),
based on energy consumption under
conditions of actual product use. The
rebuttable presumption PBP is based on
test values under conditions prescribed
by the DOE test procedure, as required
by EPCA. (42 U.S.C. 6295(o)(2)(B)(iii))
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70597
TABLE VII.2—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (COMMERCIAL, T12
BASELINE): LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median
payback
period *
years
Net cost
Net benefit
....................
0
0
0
....................
100
100
100
....................
¥3.35
¥1.66
¥1.30
....................
0
0
0
....................
100
100
100
....................
¥2.97
¥1.43
¥1.19
Event I: Replacement
1 .............................
2 .............................
3A, 3B ....................
Baseline ...............
1 ...........................
2 ...........................
3 ...........................
64
57
59
60
247
225
218
214
311
282
277
274
....................
29
34
37
Event II: New Construction/Renovation
1 .............................
2 .............................
3A, 3B ....................
Baseline ...............
1 ...........................
2 ...........................
3 ...........................
67
59
62
62
247
222
213
211
314
281
275
273
....................
32
39
40
* Negative PBP values indicate standards that reduce operating costs and installed costs.
TABLE VII.3—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (COMMERCIAL, T8
BASELINE): LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median
payback
period *
years
Net cost
Net benefit
....................
0
0
....................
100
100
....................
3.62
2.86
....................
0
0
....................
100
100
....................
2.76
2.74
Event I: Replacement
1 .............................
2 .............................
3A, 3B ....................
Baseline/1 ............
2 ...........................
3 ...........................
56
59
59
225
218
214
281
277
273
....................
5
8
Event II: New Construction/Renovation
1 .............................
2 .............................
3A, 3B ....................
Baseline/1 ............
2 ...........................
3 ...........................
58
61
62
225
216
214
283
277
275
....................
7
8
TABLE VII.4—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE FOUR 4-FOOT MBP LAMPS: LCC AND PBP
RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median payback period
years
Net cost
Net benefit
....................
0
....................
100
....................
2.65
....................
3
....................
0
....................
100
....................
4.43
E:\FR\FM\14NOR2.SGM
14NOR2
Event I: Replacement
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
78
81
412
403
490
484
....................
7
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Event II: New Construction/Renovation
1, 2 ........................
3A, 3B ...................
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3 ............................
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83
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406
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490
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70598
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.5—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 8-FOOT SLIMLINE LAMPS (T12 BASELINE):
LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median
payback
period *
years
Net cost
Net benefit
....................
0
0
....................
100
100
....................
¥0.12
0.01
....................
0
0
....................
100
100
....................
¥0.17
0.01
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline/1 .............
2 ............................
3 ............................
90
90
90
457
432
425
547
521
514
....................
26
33
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline/1 .............
2 ............................
3 ............................
92
92
92
457
440
435
549
532
527
....................
17
22
* Negative PBP values indicate standards that reduce operating costs and installed costs.
TABLE VII.6—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 8-FOOT SLIMLINE LAMPS (T8 BASELINE):
LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard
level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median payback period
years
Net cost
Net benefit
....................
0
....................
100
....................
0.46
....................
0
....................
100
....................
0.61
Event I: Replacement
1, 2 ......................
3A, 3B .................
Baseline/2 ...............
3 ..............................
90
91
432
425
522
515
....................
7
Event II: New Construction/Renovation
1, 2 ......................
3A, 3B .................
Baseline/2 ...............
3 ..............................
93
93
432
426
524
519
....................
5
TABLE VII.7—PRODUCT CLASS 2—PS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS: LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median
payback
period
years
Net cost
Net benefit
....................
0
0
....................
100
100
....................
1.09
1.25
....................
13
14
....................
0
0
....................
100
100
....................
1.09
1.26
E:\FR\FM\14NOR2.SGM
14NOR2
Event I: Replacement
1, 2 ........................
3A, 3B ...................
Baseline ................
2 ............................
3 ............................
59
60
60
205
191
188
263
251
249
....................
12
15
Event II: New Construction/Renovation
mstockstill on DSK4VPTVN1PROD with RULES2
1, 2 ........................
3A, 3B ...................
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2 ............................
3 ............................
20:32 Nov 10, 2011
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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
70599
TABLE VII.8—PRODUCT CLASS 2—PS BALLASTS THAT OPERATE FOUR 4-FOOT MBP LAMPS: LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median payback period
years
Net cost
Net benefit
....................
100
1
....................
0
99
....................
20.52
6.00
....................
0
0
....................
100
100
....................
1.43
1.76
Event I: Replacement
1 ............................
2, 3A, 3B ...............
Baseline ................
1 ............................
3 ............................
77
81
83
375
373
363
452
454
446
....................
¥2
6
Event II: New Construction/Renovation
1 ............................
2, 3A, 3B ...............
Baseline ................
1 ............................
3 ............................
79
83
85
2375
342
334
454
425
419
....................
29
35
TABLE VII.9—PRODUCT CLASS 2—PS BALLASTS THAT OPERATE TWO 4-FOOT MINIBP SO LAMPS: LCC AND PBP
RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median payback period
years
Net cost
Net benefit
....................
0
0
0
....................
100
100
100
....................
0.05
0.55
3.82
....................
0
0
0
....................
100
100
100
....................
0.05
0.78
2.41
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
64
64
66
70
268
251
240
252
332
315
306
322
....................
18
27
10
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
66
67
68
73
268
251
248
242
335
317
316
315
....................
18
18
19
TABLE VII.10—PRODUCT CLASS 2—PS BALLASTS THAT OPERATE TWO 4-FOOT MINIBP HO LAMPS: LCC AND PBP
RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median
payback
period
years
Net cost
Net benefit
....................
0
0
0
....................
100
100
100
....................
1.05
1.40
2.03
....................
26
26
26
....................
0
0
0
....................
100
100
100
....................
1.05
1.63
2.13
E:\FR\FM\14NOR2.SGM
14NOR2
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
64
68
71
74
357
326
318
319
421
395
389
393
....................
26
32
28
mstockstill on DSK4VPTVN1PROD with RULES2
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
VerDate Mar<15>2010
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1 ............................
2 ............................
3 ............................
20:32 Nov 10, 2011
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326
323
321
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397
397
397
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70600
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.11—PRODUCT CLASS 3—IS AND RS BALLASTS THAT OPERATE TWO 8-FOOT HO LAMPS (T12 BASELINE):
LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median
payback
period *
years
Net cost
Net benefit
....................
0
0
0
....................
100
100
100
....................
¥0.66
¥0.69
¥0.53
....................
0
0
0
....................
100
100
100
....................
¥0.98
¥1.26
¥0.97
Event I: Replacement
1 ............................
2, 3A ......................
3B ..........................
Baseline ................
1 ............................
2 ............................
3 ............................
116
111
97
101
631
571
420
413
747
682
517
514
....................
65
230
233
Event II: New Construction/Renovation
1 ............................
2, 3A ......................
3B ..........................
Baseline ................
1 ............................
2 ............................
3 ............................
119
114
99
103
631
590
517
513
750
704
616
616
....................
46
134
134
* Negative PBP values indicate standards that reduce operating costs and installed costs.
TABLE VII.12—PRODUCT CLASS 3—IS AND RS BALLASTS THAT OPERATE TWO 8-FOOT HO LAMPS (T8 BASELINE): LCC
AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median payback period
years
Net cost
Net benefit
....................
3
....................
97
....................
4.57
....................
84
....................
16
....................
9.50
Event I: Replacement
1, 2, 3A .................
3B ..........................
Baseline/2 .............
3 ............................
94
98
420
413
514
511
....................
3
Event II: New Construction/Renovation
1, 2, 3A .................
3B ..........................
Baseline/2 .............
3 ............................
96
100
420
417
517
517
....................
¥1
TABLE VII.13—PRODUCT CLASS 5—SIGN BALLASTS THAT OPERATE FOUR 8-FOOT HO LAMPS: LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings
Average
savings
2010$
LCC
Percent of consumers that
experience
Median
payback
period *
years
Net cost
Net benefit
....................
0
....................
100
....................
¥0.16
....................
0
....................
100
....................
¥0.26
Event I: Replacement
1, 2, 3A, 3B ...........
Baseline ................
1 ............................
164
157
1,483
1,086
1,646
1,244
....................
403
Event II: New Construction/Renovation
1, 2, 3A, 3B ...........
Baseline ................
1 ............................
166
160
1,483
1,239
1,649
1,398
....................
251
mstockstill on DSK4VPTVN1PROD with RULES2
* Negative PBP values indicate standards that reduce operating costs and installed costs.
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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
70601
TABLE VII.14—PRODUCT CLASS 6—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (RESIDENTIAL, T12
BASELINE): LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings
Average
savings
2010$
LCC *
Percent of consumers that
experience
Median
payback
period *
years
Net cost
Net benefit
....................
0
0
....................
100
100
....................
¥5.46
¥4.92
....................
0
0
....................
100
100
....................
¥9.45
¥6.35
Event I: Replacement
1, 2, 3A .................
3B ..........................
Baseline ................
1 ............................
2 ............................
53
46
47
71
56
58
124
102
105
....................
21
19
Event II: New Construction/Renovation
1, 2, 3A .................
3B ..........................
Baseline ................
1 ............................
2 ............................
55
48
49
71
63
61
126
111
110
....................
15
16
* Negative PBP values indicate standards that reduce operating costs and installed costs.
TABLE VII.15—PRODUCT CLASS 6—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (RESIDENTIAL, T8
BASELINE): LCC AND PBP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings
Average
savings
2010$
LCC *
Percent of consumers that
experience
Median
payback
period *
years
Net cost
Net benefit
....................
100
....................
0
....................
N/A
....................
27
....................
73
....................
8.18
Event I: Replacement
1, 2, 3A .................
3B ..........................
Baseline/1 .............
2 ............................
45
46
56
58
101
104
....................
¥2
Event II: New Construction/Renovation
1, 2, 3A .................
3B ..........................
Baseline/1 .............
2 ............................
47
49
56
55
104
103
....................
1
* Entries of ‘‘N/A’’ indicate standard levels that do not reduce operating costs.
mstockstill on DSK4VPTVN1PROD with RULES2
b. Consumer Sub-Group Analysis
Using the LCC spreadsheet model,
DOE determined the impact of the trial
standard levels on the following
consumer sub-groups: low-income
consumers, institutions of religious
worship, and institutions that serve lowincome populations. Representative
ballast designs used in the industrial
sector (e.g., ballasts operating HO
lamps) are not typically used by the
identified sub-groups, and were not
included in the sub-group analysis.
Similarly, DOE assumed that lowincome consumers use residential
ballasts only, and did not include
commercial ballast designs in the LCC
analysis for this sub-group. DOE
VerDate Mar<15>2010
18:36 Nov 10, 2011
Jkt 226001
assumed that institutions of religious
worship and institutions that serve lowincome populations use commercial
ballasts only, and did not include
residential ballast designs in the subgroup analysis.
DOE adjusted inputs to the LCC
model to reflect conditions faced by the
identified subgroups. For low-income
consumers, DOE adjusted electricity
prices to represent rates typically paid
by consumers living below the poverty
line. DOE assumed that institutions of
religious worship have lower annual
operating hours than the commercial
sector average used in the main LCC
analysis. For institutions serving lowincome populations, DOE assumed that
PO 00000
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Sfmt 4700
the majority of these institutions are
small nonprofits, and used a higher
discount rate of 10.7 percent (versus 6.9
percent for the main commercial sector
analysis).
Table VII.16 through Table VII.25
shows the LCC impacts and payback
periods for identified sub-groups that
purchase ballasts. Negative PBP values
indicate standards that reduce operating
costs and installed costs. Entries of
‘‘N/A’’ indicate standard levels that do
not reduce operating costs. In general,
the average LCC savings for the
identified sub-groups at the considered
efficiency levels exhibited the same
trends and relationships as the averages
for all consumers.
E:\FR\FM\14NOR2.SGM
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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.16—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (COMMERCIAL, T12
BASELINE): LCC AND PBP SUB-GROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings *
Percent of consumers that
experience
Average
savings
2010$
LCC
Median
payback
period **
years
Net cost
Net benefit
....................
0
0
0
....................
100
100
100
....................
¥5.81
¥2.89
¥2.26
....................
0
0
0
....................
100
100
100
....................
¥5.16
¥2.48
¥2.06
....................
0
0
0
....................
100
100
100
....................
¥3.35
¥1.66
¥1.30
....................
0
0
0
....................
100
100
100
....................
¥2.97
¥1.43
¥1.19
Sub-Group: Institutions of Religious Worship
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
64
57
59
60
195
178
173
170
260
235
232
230
....................
25
28
30
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
67
59
62
62
195
176
169
167
262
235
231
229
....................
27
32
33
Sub-Group: Institutions Serving Low-Income Populations
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
64
57
59
60
209
191
185
181
273
247
244
241
....................
26
29
32
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
67
59
62
62
209
188
180
179
276
247
242
241
....................
28
34
35
* See Table VII.2 for average LCC savings for all consumers.
** Negative PBP values indicate standards that reduce operating costs and installed costs.
TABLE VII.17—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (COMMERCIAL, T8
BASELINE): LCC AND PBP SUB-GROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings*
Percent of consumers that
experience
Average
savings
2010$
LCC
Median
payback
period
years
Net cost
Net benefit
....................
1
0
....................
99
100
....................
6.28
4.96
....................
0
0
....................
100
100
....................
4.79
4.75
....................
99
100
....................
3.62
2.86
Sub-Group: Institutions of Religious Worship
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline/1 .............
2 ............................
3 ............................
56
59
59
178
173
170
234
231
229
....................
3
6
Event II: New Construction/Renovation
mstockstill on DSK4VPTVN1PROD with RULES2
1 ............................
2 ............................
3A, 3B ...................
Baseline/1 .............
2 ............................
3 ............................
58
61
62
178
171
169
237
232
231
....................
5
6
Sub-Group: Institutions Serving Low-Income Populations
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
VerDate Mar<15>2010
Baseline/1 .............
2 ............................
3 ............................
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56
59
59
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191
185
181
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246
243
240
Sfmt 4700
....................
3
6
....................
1
0
E:\FR\FM\14NOR2.SGM
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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
70603
TABLE VII.17—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (COMMERCIAL, T8
BASELINE): LCC AND PBP SUB-GROUP RESULTS—Continued
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings*
Percent of consumers that
experience
Average
savings
2010$
LCC
Net cost
Net benefit
....................
0
0
....................
100
100
Median
payback
period
years
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline/1 .............
2 ............................
3 ............................
58
61
62
191
183
181
249
244
242
....................
5
7
....................
2.76
2.74
* See Table VII.3 for average LCC savings for all consumers.
TABLE VII.18—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE FOUR 4-FOOT MBP LAMPS: LCC AND PBP
RESULTS: LCC AND PBP SUB-GROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings*
Percent of consumers that
experience
Average
savings
2010$
LCC
Median
payback
period
years
Net cost
Net benefit
....................
0
....................
100
....................
4.61
....................
10
....................
90
....................
7.69
....................
0
....................
100
....................
2.65
....................
4
....................
96
....................
4.43
Sub-Group: Institutions of Religious Worship
Event I: Replacement
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
78
81
326
319
405
400
....................
5
Event II: New Construction/Renovation
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
81
83
326
322
407
405
....................
2
Sub-Group: Institutions Serving Low-Income Populations
Event I: Replacement
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
78
81
349
341
427
422
....................
5
Event II: New Construction/Renovation
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
81
83
349
344
429
427
....................
2
* See Table VII.4 for average LCC savings for all consumers.
TABLE VII.19—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 8-FOOT SLIMLINE LAMPS (T12
BASELINE): LCC AND PBP SUB-GROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings *
Average
savings
2010$
LCC
Percent of consumers that
experience
Net cost
Net benefit
....................
20
26
....................
0
0
....................
100
100
E:\FR\FM\14NOR2.SGM
14NOR2
Median
payback
period * *
years
mstockstill on DSK4VPTVN1PROD with RULES2
Sub-Group: Institutions of Religious Worship
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
VerDate Mar<15>2010
Baseline/1 .............
2 ............................
3 ............................
20:32 Nov 10, 2011
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90
90
90
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362
342
336
Fmt 4701
452
431
426
Sfmt 4700
....................
¥0.20
¥0.01
70604
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.19—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 8-FOOT SLIMLINE LAMPS (T12
BASELINE): LCC AND PBP SUB-GROUP RESULTS—Continued
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings *
Percent of consumers that
experience
Average
savings
2010$
LCC
Median
payback
period * *
years
Net cost
Net benefit
....................
0
0
....................
100
100
....................
¥0.30
¥0.02
....................
0
0
....................
100
100
....................
¥0.12
0.01
....................
0
0
....................
100
100
....................
¥0.17
0.01
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline/1 .............
2 ............................
3 ............................
92
92
92
362
348
344
454
441
436
....................
14
18
Sub-Group: Institutions Serving Low-Income Populations
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline/1 .............
2 ............................
3 ............................
90
90
90
387
365
359
477
455
449
....................
22
28
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline/1 .............
2 ............................
3 ............................
92
92
92
387
372
368
479
465
460
....................
15
19
* See Table VII.5 for average LCC savings for all consumers.
* * Negative PBP values indicate standards that reduce operating costs and installed costs.
TABLE VII.20—PRODUCT CLASS 1—IS AND RS BALLASTS THAT OPERATE TWO 8-FOOT SLIMLINE LAMPS (T12
BASELINE): LCC AND PBP SUB-GROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings *
Percent of consumers that
experience
Average
savings
2010$
LCC
Median
payback
period
years
Net cost
Net benefit
....................
0
....................
100
....................
0.80
....................
0
....................
100
....................
1.05
....................
0
....................
100
....................
0.46
....................
4
....................
0
....................
100
....................
0.61
E:\FR\FM\14NOR2.SGM
14NOR2
Sub-Group: Institutions of Religious Worship
Event I: Replacement
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
90
91
342
336
432
427
....................
5
Event II: New Construction/Renovation
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
93
93
342
337
434
430
....................
4
Sub-Group: Institutions Serving Low-Income Populations
Event I: Replacement
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
90
91
365
359
456
450
....................
6
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Event II: New Construction/Renovation
1, 2 ........................
3A, 3B ...................
Baseline/2 .............
3 ............................
93
93
365
361
458
454
* See Table VII.6 for average LCC savings for all consumers.
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TABLE VII.21—PRODUCT CLASS 2—PS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS: LCC AND PBP SUBGROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings *
Percent of consumers that
experience
Average
savings
2010$
LCC
Median
payback
period
years
Net cost
Net benefit
....................
0
0
....................
100
100
....................
1.90
2.16
....................
0
0
....................
100
100
....................
1.89
2.19
....................
0
0
....................
100
100
....................
1.09
1.25
....................
0
0
....................
100
100
....................
1.09
1.26
Sub-Group: Institutions of Religious Worship
Event I: Replacement
1, 2 ........................
3A, 3B ...................
Baseline ................
2 ............................
3 ............................
59
60
60
149
139
137
208
199
198
....................
9
10
Event II: New Construction/Renovation
1, 2 ........................
3A, 3B ...................
Baseline ................
2 ............................
3 ............................
61
62
63
149
139
137
210
201
200
....................
9
10
Sub-Group: Institutions Serving Low-Income Populations
Event I: Replacement
1, 2 ........................
3A, 3B ...................
Baseline ................
2 ............................
3 ............................
59
60
60
163
152
150
222
212
211
....................
10
11
Event II: New Construction/Renovation
1, 2 ........................
3A, 3B ...................
Baseline ................
2 ............................
3 ............................
61
62
63
163
152
151
225
215
213
....................
10
11
* See Table VII.7 for average LCC savings for all consumers.
TABLE VII.22—PRODUCT CLASS 2—PS BALLASTS THAT OPERATE FOUR 4-FOOT MBP LAMPS: LCC AND PBP SUBGROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings *
Percent of consumers that
experience
Average
savings
2010$
LCC
Median
payback
period
years
Net cost
Net benefit
....................
100
80
....................
0
20
....................
35.63
10.41
....................
0
0
....................
100
100
....................
2.48
3.06
....................
100
19
....................
0
81
....................
20.52
6.00
....................
22
....................
0
....................
100
....................
1.43
E:\FR\FM\14NOR2.SGM
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Sub-Group: Institutions of Religious Worship
Event I: Replacement
1 ............................
2, 3A, 3B ...............
Baseline ................
1 ............................
3 ............................
77
81
83
273
272
265
350
352
347
....................
¥2
3
Event II: New Construction/Renovation
1 ............................
2, 3A, 3B ...............
Baseline ................
1 ............................
3 ............................
79
83
85
273
249
243
353
332
329
....................
20
24
Sub-Group: Institutions Serving Low-Income Populations
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Event I: Replacement
1 ............................
2, 3A, 3B ...............
Baseline ................
1 ............................
3 ............................
77
81
83
299
298
290
376
378
373
....................
¥2
4
Event II: New Construction/Renovation
1 ............................
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1 ............................
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TABLE VII.22—PRODUCT CLASS 2—PS BALLASTS THAT OPERATE FOUR 4-FOOT MBP LAMPS: LCC AND PBP SUBGROUP RESULTS—Continued
Life-cycle cost 2010$
Trial standard level
2, 3A, 3B ...............
Efficiency level
Discounted
operating
cost
Installed
cost
3 ............................
85
Life-cycle cost savings *
LCC
267
Percent of consumers that
experience
Average
savings
2010$
352
Net cost
27
Median
payback
period
years
Net benefit
0
100
1.76
* See Table VII.8 for average LCC savings for all consumers.
TABLE VII.23—PRODUCT CLASS 2—PS BALLASTS THAT OPERATE TWO 4-FOOT MINIBP SO LAMPS: LCC AND PBP SUBGROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings *
Percent of consumers that
experience
Average
savings
2010$
LCC
Median
payback
period
years
Net cost
Net benefit
....................
0
0
1
....................
100
100
99
....................
0.09
0.95
6.63
....................
0
0
0
....................
100
100
100
....................
0.09
1.35
4.19
....................
0
0
2
....................
100
100
98
....................
0.05
0.55
3.82
....................
0
0
0
....................
100
100
100
....................
0.05
0.78
2.41
Sub-Group: Institutions of Religious Worship
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
64
64
66
70
212
198
190
199
276
263
256
270
....................
14
21
7
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
66
67
68
73
212
198
197
192
279
265
265
265
....................
14
14
14
Sub-Group: Institutions Serving Low-Income Populations
Event I: Replacement
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
64
64
66
70
227
212
203
213
291
276
269
284
....................
15
22
7
Event II: New Construction/Renovation
1 ............................
2 ............................
3A, 3B ...................
Baseline ................
1 ............................
2 ............................
3 ............................
66
67
68
73
227
212
210
205
294
279
278
278
....................
15
15
15
* See Table VII.9 for average LCC savings for all consumers.
TABLE VII.24—PRODUCT CLASS 6—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (RESIDENTIAL, T12
BASELINE): LCC AND PBP SUB-GROUP RESULTS
Life-cycle cost 2010$
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Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings *
Average
savings
2010$
LCC
Percent of consumers that
experience
Net cost
Net benefit
....................
21
19
....................
0
0
....................
100
100
E:\FR\FM\14NOR2.SGM
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Median
payback
period **
years
Sub-Group: Low-Income Consumers
Event I: Replacement
1, 2, 3A .................
3B ..........................
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1 ............................
2 ............................
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46
47
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57
58
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102
105
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....................
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¥4.92
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70607
TABLE VII.24—PRODUCT CLASS 6—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (RESIDENTIAL, T12
BASELINE): LCC AND PBP SUB-GROUP RESULTS—Continued
Life-cycle cost 2010$
Trial standard level
Efficiency level
Discounted
operating
cost
Installed
cost
Life-cycle cost savings *
Average
savings
2010$
LCC
Percent of consumers that
experience
Net cost
Net benefit
....................
0
0
....................
100
100
Median
payback
period **
years
Event II: New Construction/Renovation
1, 2, 3A .................
3B ..........................
Baseline ................
1 ............................
2 ............................
55
48
49
71
63
61
126
111
110
....................
15
16
....................
¥9.45
¥6.35
* See Table VII.14 for average LCC savings for all consumers.
** Negative PBP values indicate standards that reduce operating costs and installed costs.
TABLE VII.25—PRODUCT CLASS 6—IS AND RS BALLASTS THAT OPERATE TWO 4-FOOT MBP LAMPS (RESIDENTIAL, T8
BASELINE): LCC AND PBP SUB-GROUP RESULTS
Life-cycle cost 2010$
Trial standard level
Efficiency level
Installed
cost
Discounted
operating
cost
Life-cycle cost savings *
Average
savings
2010$
LCC
Percent of consumers that
experience
Median
payback
period **
years
Net cost
Net benefit
....................
100
....................
0
....................
N/A
....................
27
....................
73
....................
8.18
Sub-Group: Low-Income Consumers
Event I: Replacement
1, 2, 3A .................
3B ..........................
Baseline/1 .............
2 ............................
45
46
57
58
101
104
....................
¥2
Event II: New Construction/Renovation
1, 2, 3A .................
3B ..........................
Baseline/1 .............
2 ............................
47
49
57
55
104
103
....................
1
* See Table VII.15 for average LCC savings for all consumers.
** Entries of ‘‘N/A’’ indicate standard levels that do not reduce operating costs.
mstockstill on DSK4VPTVN1PROD with RULES2
c. Rebuttable Presumption Payback
As discussed in section IV.D.2, EPCA
provides a rebuttable presumption that
an energy conservation standard is
economically justified if the increased
purchase cost for a product that meets
the standard is less than three times the
value of the first-year energy savings
resulting from the standard. DOE’s LCC
and PBP analyses generate values for
calculating the payback period for
consumers affected by potential energy
conservation standards. This includes,
but is not limited to, the 3-year payback
period contemplated under the
rebuttable presumption test discussed in
section IV.D.2. DOE, however, routinely
conducts an economic analysis that
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considers the full range of impacts—
including those on consumers,
manufacturers, the Nation, and the
environment—as required under 42
U.S.C. 6295(o)(2)(B)(i).
For this final rule, DOE calculated a
rebuttable presumption payback period
for each TSL. DOE used discrete values
rather than distributions for inputs and,
as required by EPCA, made the
calculations using the applicable DOE
test procedures for ballasts. DOE then
calculated a single rebuttable
presumption payback value, rather than
a distribution of payback periods, for
each TSL. Table VII.26 shows the
rebuttable presumption payback periods
that are less than 3 years. Negative PBP
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values indicate standards that reduce
operating costs and installed costs.
While DOE examined the rebuttablepresumption criterion, it also
considered a more comprehensive
analysis of the economic impacts of
these levels to determine whether the
standard levels considered for today’s
rule are economically justified pursuant
to 42 U.S.C. 6295(o)(2)(B)(i). The results
of this analysis serve as the basis for
DOE to 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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2. Economic Impacts on Manufacturers
For the MIA in the April 2011 NOPR,
DOE used changes in INPV to compare
the direct financial impacts of different
TSLs on manufacturers. 76 FR 20090,
20156–61 (April 11, 2011). DOE used
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the GRIM to compare the INPV of the
base case (no new or amended energy
conservation standards) to that of each
TSL. The INPV is the sum of all net cash
flows discounted by the industry’s cost
of capital (discount rate) to the base
year. The difference in INPV between
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the base case and the standards case is
an estimate of the economic impacts
that implementing that standard level
would have on the entire fluorescent
ballast industry. For today’s final rule,
DOE continues to use the methodology
presented in the NOPR (76 FR 20090,
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20134–5 (April 11, 2011)) and in section
V.H.
a. Industry Cash-Flow Analysis Results
Table VII.27 and Table VII.28 depict
the financial impacts on manufacturers
(represented by changes in INPV) and
the conversion costs DOE estimates
manufacturers would incur at each TSL.
The two tables show two sets of INPV
impacts: Table VII.27 reflects the lower
(less severe) bound of impacts and Table
VII.28 represents the upper bound. To
evaluate this range of cash-flow impacts
on the fluorescent lamp ballast industry,
DOE modeled two different scenarios
using different markup assumptions.
These assumptions correspond to the
bounds of a range of market responses
that DOE anticipates could occur in the
70609
standards case (i.e., where new and
amended energy conservation standards
apply). Each of the two scenarios results
in a unique set of cash flows and
corresponding industry value at each
TSL. The April 2011 NOPR (76 FR
20090, 20156 (April 11, 2011)) discusses
each of these scenarios in full, and they
are also presented in chapter 13 of the
TSD.
TABLE VII.27—MANUFACTURER IMPACT ANALYSIS FOR FLUORESCENT LAMP BALLASTS—PRESERVATION OF OPERATING
PROFIT MARKUP, EXISTING TECHNOLOGIES, AND SHIFT SHIPMENT SCENARIO
Trial standard level
Units
Base case
1
INPV ......................
Change in INPV ....
Product Conversion
Costs.
Capital Conversion
Costs.
Total Conversion Costs.
2
3A
3B
(2010$ millions) ................
(2010$ millions) ................
(%) ....................................
(2010$ millions) ................
1,219
................................
................................
................................
1,199
(19.6)
¥1.6%
5
1,176
(42.4)
¥3.5%
18
1,144
(74.5)
¥6.1%
46
1,141
(77.6)
¥6.4%
48
(2010$ millions) ................
................................
11
20
28
29
(2010$ millions) ................
................................
17
38
74
78
TABLE VII.28—MANUFACTURER IMPACT ANALYSIS FOR FLUORESCENT LAMP BALLASTS—TWO-TIER MARKUP, EMERGING
TECHNOLOGIES, AND ROLL-UP SHIPMENT SCENARIO
Trial standard level
Units
Base case
1
INPV ............................
Change in INPV ..........
Product Conversion
Costs.
Capital Conversion
Costs.
mstockstill on DSK4VPTVN1PROD with RULES2
Total Conversion
Costs.
3A
3B
(2010$ millions) ................
(2010$ millions) ................
(%) ....................................
(2010$ millions) ................
733
..........................
..........................
..........................
616
(116.4)
¥15.9%
5
545
(188.0)
¥25.7%
18
464
(268.6)
¥36.7%
46
431
(301.2)
¥41.1%
48
(2010$ millions) ................
..........................
11
20
28
29
(2010$ millions) ................
..........................
17
38
74
78
TSL 1 represents EL1 for all five
representative product classes. At TSL
1, DOE estimates impacts on INPV to
range from ¥$19.6 million to ¥$116.4
million, or a change in INPV of ¥1.6
percent to ¥15.9 percent. At this level,
industry free cash flow 61 is estimated to
decrease by approximately 12 percent to
$43.4 million, compared to the basecase value of $49.3 million in the year
leading up to the energy conservation
standards.
The INPV impacts at TSL 1 are
relatively minor, in part because the
vast majority of shipments already meet
EL1. DOE estimates that in 2014, the
year in which compliance with the new
and amended standards will be
required, over 99 percent of the IS/RS
product class shipments, 73 percent of
61 Industry free cash flow is the operating cash
flow minus capital expenditures.
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the PS product class shipments, 98
percent of the 8-foot HO IS/RS product
class shipments, 64 percent of the sign
ballast product class shipments, and 96
percent of the residential IS/RS product
class shipments would meet EL1 or
higher in the base case. The majority of
shipments at baseline efficiency levels
that would need to be converted at TSL
1 are 2-lamp and 4-lamp 4ft MBP PS
ballasts, 4-lamp sign ballasts, and 2lamp 4-foot MBP IS/RS residential
ballasts.
Because most fluorescent lamp ballast
shipments already meet the efficiency
levels analyzed at TSL 1, DOE expects
conversion costs to be small compared
to the industry value. DOE estimates
product conversion costs of $5 million
due to the research, development,
testing, and certification costs needed to
upgrade product lines that do not meet
TSL 1. For capital conversion costs,
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DOE estimates $11 million for the
industry, largely driven by the cost of
converting all magnetic sign ballast
production lines to electronic sign
ballast production lines.
Under the preservation of operating
profit markup scenario, impacts on
manufacturers are marginally negative
because, while manufacturers earn the
same operating profit as is earned in the
base case for 2015 (the year following
the compliance date of amended
standards), they face $17 million in
conversion costs. INPV impacts on
manufacturers are not as significant
under this scenario as in other scenarios
because most shipments already meet
TSL 1 and the shift shipment scenario
moves products beyond the eliminated
baseline to higher-price (and higher
gross profit) levels. This results in a
shipment-weighted average MPC
increase of 6 percent applied to a
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growing market over the analysis
period.
Shipments under the existing
technologies scenario are nearly three
and a half times greater than shipments
under the emerging technologies
scenario by the end of the analysis
period. At TSL 1, the moderate price
increase applied to a large quantity of
shipments lessens the impact of the
minor conversion costs estimated at TSL
1, resulting in slightly negative impacts
at TSL 1 under the preservation of
operating profit markup scenario.
Under the two-tier markup scenario,
manufacturers are not able to fully pass
on additional costs to consumers and
are not guaranteed base-case operating
profit levels. Rather, products that once
earned a higher-than-average markup at
EL1 become commoditized once
baseline products are eliminated at TSL
1. Thus, the average markup drops
below the base-case average markup
(which is equal to the flat manufacturer
markup of 1.4). Because shipments
above the baseline do not shift to higher
efficiencies with greater costs under the
roll-up scenario, the shipment-weighted
average MPC does not significantly
increase. A lower average markup of
1.38 and $17 million in conversion costs
results in more negative impacts at TSL
1 under the two-tier markup scenario.
These impacts increase on a percentage
basis under the emerging technologies
scenario relative to the existing
technologies scenario because the basecase INPV against which changes are
compared is nearly 40 percent lower.
TSL 2 represents EL1 for the sign
ballast and residential IS/RS product
classes. For the IS/RS, PS, and 8-foot
HO IS/RS product classes, TSL 2
represents EL2. At TSL 2, DOE estimates
impacts on INPV to range from ¥$42.4
million to ¥$188.0 million, or a change
in INPV of ¥3.5 percent to ¥25.7
percent. At this level, industry free cash
flow is estimated to decrease by
approximately 26 percent to $36.6
million, compared to the base-case
value of $49.3 million in the year
leading up to the energy conservation
standards.
Because the sign ballast and
residential IS/RS product classes remain
at EL1 at TSL 2, the additional impacts
at TSL 2 relative to TSL 1 result only
from increasing the IS/RS, PS, and 8foot HO IS/RS product classes to EL2.
At TSL 2, DOE estimates that 63 percent
of the IS/RS product class shipments, 19
percent of the PS product class
shipments, and 89 percent of the 8-foot
HO IS/RS product class shipments
would meet EL2 or higher in the base
case. Since the 8-foot HO IS/RS product
class represents only 0.1 percent of the
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fluorescent lamp ballast market, the vast
majority of impacts at TSL 2 relative to
TSL 1 result from changes in the IS/RS
and PS product classes.
At TSL 2, conversion costs remain
small compared to the industry value.
Product conversion costs increase to $18
million due to the increase in the
number of product lines within the IS/
RS and PS product classes that would
need to be redesigned at TSL 2. Capital
conversion costs grow to $20 million at
TSL 2 because manufacturers would
need to invest in additional testing
equipment and convert some
production lines.
Under the preservation of operating
profit markup scenario, INPV impacts
are negative because manufacturers are
not able to fully pass on higher product
costs to consumers. The shipmentweighted average MPC increases by 9
percent compared to the baseline MPC,
but this increase does not generate
enough cash flow to outweigh the $38
million in conversion costs at TSL 2,
resulting in a ¥3.5 percent change in
INPV at TSL 2 compared to the base
case.
Under the two-tier markup scenario,
more products are commoditized to a
lower markup at TSL 2. The impact of
this lower average markup of 1.36
outweighs the impact of a 6 percent
increase in shipment-weighted average
MPC, resulting in a negative change in
INPV at TSL 2. The $38 million in
conversion costs further erodes
profitability, and the lower base case
INPV against which the change in INPV
is compared under the emerging
technologies scenario increases INPV
impacts on a percentage basis.
TSL 3A represents EL1 for the sign
ballasts and residential IS/RS product
classes, EL2 for the 8-foot HO IS/RS
product class, and EL3 for the IS/RS and
PS product classes. At TSL 3A, DOE
estimates impacts on INPV to range
from ¥$74.5 million to ¥$268.6
million, or a change in INPV of ¥6.1
percent to ¥36.7 percent. At this level,
industry free cash flow is estimated to
decrease by approximately 48 percent to
$25.8 million, compared to the basecase value of $49.3 million in the year
leading up to the energy conservation
standards.
Because the sign ballast and
residential IS/RS product classes remain
at EL1 and the 8-foot HO IS/RS product
class remains at EL2 for TSL 3A, the
additional impacts at TSL 3A relative to
TSL 2 result only from increasing the
IS/RS and PS product classes to EL3. At
TSL 3A, DOE estimates that 21 percent
of the IS/RS product class shipments
and 7 percent of the PS product class
shipments would meet the efficiency
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levels contained in TSL 3A or higher in
the base case.
At TSL 3A, product conversion costs
increase to $46 million because far more
product lines within the IS/RS, and PS
product classes would need to be
redesigned at TSL 3A than TSL 2.
Capital conversion costs rise to $28
million at TSL 3A because
manufacturers would need to invest in
equipment such as surface-mount
device placement machinery and solder
machines to convert production lines
for the manufacturing of more efficient
ballasts.
Under the preservation of operating
profit markup scenario, INPV decreases
by 6.1 percent at TSL 3A compared to
the base case. The shipment-weighted
average MPC increases by 17 percent,
but manufacturers are not able to pass
on the full amount of these higher costs
to consumers. This MPC increase is
outweighed by the $74 million in
conversion costs at TSL 3A.
Under the two-tier markup scenario,
at TSL 3A, products are commoditized
to a lower markup to an even greater
extent than under the preservation of
operating profit markup scenario. The
impact of this lower average markup of
1.33 outweighs the impact of a 15
percent increase in shipment-weighted
average MPC, resulting in a negative
change in INPV at TSL 3A compared to
TSL 2. Profitability is further reduced by
the $74 million in conversion costs and
the lower base-case INPV over which
change in INPV is compared under the
emerging technologies scenario.
TSL 3B represents EL1 for the sign
ballast product class, EL2 for the
residential IS/RS product class, and EL3
for the IS/RS, PS, and 8-foot HO IS/RS
product classes. At TSL 3B, DOE
estimates impacts on INPV to range
from ¥$77.6 million to ¥$301.2
million, or a change in INPV of ¥6.4
percent to ¥41.1 percent. At this level,
industry free cash flow is estimated to
decrease by approximately 50 percent to
$24.7 million, compared to the basecase value of $49.3 million in the year
leading up to the energy conservation
standards.
Because the sign ballast product class
remains at EL1 and the IS/RS and PS
product classes remain at EL3 for TSL
3B, the additional impacts at TSL 3B
relative to TSL 3A result only from
increasing the 8-foot HO IS/RS product
class to EL3 and the residential IS/RS
product class to EL2. At TSL 3B, DOE
estimates that 2 percent of the 8-foot HO
IS/RS product class shipments and 23
percent of the residential IS/RS product
class shipments would meet the
efficiency levels contained in TSL 3B in
the base case.
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At TSL 3B, conversion costs are
slightly greater compared to TSL 3A.
Product and capital conversion costs
increase to $48 million and $29 million,
respectively, because more product
lines would need to be redesigned and
upgraded at TSL 3B.
Under the preservation of operating
profit markup scenario, INPV decreases
by 6.4 percent at TSL 3B compared to
the base case, which is slightly greater
than the percentage impact at TSL 3A.
The shipment-weighted average MPC
increases by over 17 percent, but
manufacturers are not able to pass on
the full amount of these higher costs to
consumers. This slight MPC increase is
outweighed by the $78 million in
conversion costs at TSL 3B.
Under the two-tier markup scenario,
at TSL 3B, products are commoditized
to a lower markup to the greatest extent
of any TSL analyzed. The impact of this
lower average markup of 1.33 outweighs
the impact of a 17 percent increase in
shipment-weighted average MPC,
resulting in a negative change in INPV
at TSL 3B compared to TSL 3A.
Profitability is further reduced by the
$78 million in conversion costs and the
lower base-case INPV over which
change in INPV is compared under the
emerging technologies scenario.
b. Impacts on Employment
DOE typically presents modeled
quantitative estimates of the potential
changes in production employment that
could result from new and amended
energy conservation standards.
However, for this rulemaking, DOE
determined that none of the major
manufacturers, which comprise more
than 90 percent of the market, have
domestic fluorescent lamp ballast
production. Although a few niche
manufacturers have relatively limited
domestic production, based on
interviews, DOE has identified very few
domestic production employees in the
United States. Because many niche
manufacturers did not respond to
interview requests or submit comments
on domestic employment impacts, DOE
is unable to fully quantify domestic
production employment impacts.
Therefore, while DOE qualitatively
discusses potential employment impacts
below, DOE did not model direct
employment impacts explicitly because
the results would not be meaningful
given the very low number of domestic
production employees.
Based on interviews, DOE projects
that significant direct employment
impacts would occur only in the event
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that one or more businesses exit the
market due to new standards.
Discussions with manufacturers
indicated that, at the highest efficiency
levels (TSL 3A and TSL 3B), some small
manufacturers will be faced with the
decision of whether or not to make the
investments necessary to remain in the
market based on their current technical
capabilities. In general, however, DOE
projects that TSL 3A, the level adopted
in today’s final rule, will not have
significant adverse impacts on domestic
employment because achieving these
levels is within the expertise of most
manufacturers, including small
manufacturers, due to the lack of
intellectual property restrictions and
similarity of products among
manufacturers.
In summary, given the low number of
production employees and the low
likelihood that manufacturers would
exit the market at the efficiency levels
adopted in today’s final rule, DOE does
not expect a significant impact on direct
employment following new and
amended energy conservation
standards.
DOE notes that the direct employment
impacts discussed here are independent
of the indirect employment impacts
from the broader U.S. economy, which
are documented in chapter 15,
Employment Impact Analysis, of the
TSD.
c. Impacts on Manufacturing Capacity
Manufacturers stated that new and
amended energy conservation standards
could harm manufacturing capacity due
to the current component shortage
discussed in the April 2011 NOPR (76
FR 20090, 20139 (April 11, 2011)). At
present, manufacturers are struggling to
produce enough fluorescent lamp
ballasts to meet demand because of a
worldwide shortage of electrical
components. The components most
affected by this shortage are premium
high-efficiency parts, for which demand
would increase even more following
new and amended energy conservation
standards. In the near term this
increased demand might exacerbate the
component shortage, thereby impacting
manufacturing capacity. While DOE
recognizes that the component shortage
is currently a significant issue for
manufacturers, DOE projects it to be a
relatively short-term phenomenon to
which component suppliers will
ultimately adjust. According to
manufacturers, suppliers have the
ability to ramp up production to meet
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70611
ballast component demand by the
compliance date of new and amended
standards, but those suppliers have
hesitated to invest in additional
capacity due to economic uncertainty
and skepticism about the sustainability
of demand. The state of the
macroeconomic environment through
2014 will likely affect the duration of
the component shortage. Mandatory
standards, however, could create more
certainty for suppliers about the
eventual demand for these components.
Additionally, the components at issue
are not new technologies; rather, they
have simply not historically been
demanded in large quantities by ballast
manufacturers. DOE received no
comments or additional information
indicating that its conclusions related to
the component shortage issue were
incorrect and therefore reiterates these
conclusions for today’s final rule.
d. Impacts on Sub-Groups of
Manufacturers
As discussed in the April 2011 NOPR
(76 FR 20090, 20135 (April 11, 2011)),
using average cost assumptions to
develop an industry cash-flow estimate
may be inadequate to assess differential
impacts among manufacturer subgroups. DOE used the results of the
industry characterization to group
ballast manufacturers exhibiting similar
characteristics. DOE identified two subgroups that would experience
differential impacts: Small
manufacturers and sign ballast
manufacturers, many of whom are also
small manufacturers. For a discussion of
the impacts on the small manufacturer
sub-group, see the Regulatory Flexibility
Analysis in section VIII.B and chapter
13 of the TSD.
DOE is not presenting results under
the two-tier markup scenario for sign
ballasts because it did not observe a
two-tier effect in the sign ballast market.
Electronic ballasts at EL1 command
neither a higher price nor a higher
markup in the base case. Additionally,
roll-up and shift scenarios do not have
separate impacts for sign ballasts
because there are no higher ELs above
the new baseline to which products
could potentially shift in the standards
case. As such, Table VII.29 and Table
VII.30 present the cash-flow analysis
results under the preservation of
operating profit markup and roll-up
shipment scenarios with existing or
emerging technologies for sign ballast
manufacturers.
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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.29—MANUFACTURER IMPACT ANALYSIS FOR SIGN BALLASTS—PRESERVATION OF OPERATING PROFIT MARKUP,
EXISTING TECHNOLOGIES, AND ROLL-UP SHIPMENT SCENARIO
Trial standard level
Units
Base case
1
INPV ......................................
Change in INPV ....................
Product Conversion Costs ....
Capital Conversion Costs .....
Total Conversion Costs
2
3A
3B
(2010$ millions) ................
(2010$ millions) ................
(%) ....................................
(2010$ millions) ................
(2010$ millions) ................
142
........................
........................
........................
........................
138
(4.2)
¥2.9%
2
6
138
(4.2)
¥2.9%
2
6
138
(4.2)
¥2.9%
2
6
138
(4.2)
¥2.9%
2
6
(2010$ millions) ................
........................
8
8
8
8
TABLE VII.30—MANUFACTURER IMPACT ANALYSIS FOR SIGN BALLASTS—PRESERVATION OF OPERATING PROFIT MARKUP,
EMERGING TECHNOLOGIES, AND ROLL-UP SHIPMENT SCENARIO
Trial standard level
Units
Base case
1
INPV ......................................
Change in INPV ....................
Product Conversion Costs ....
Capital Conversion Costs .....
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Total Conversion Costs
18:36 Nov 10, 2011
3A
3B
(2010$ millions) ................
(2010$ millions) ................
(%) ....................................
(2010$ millions) ................
(2010$ millions) ................
116
........................
........................
........................
........................
111
(5.1)
¥4.4%
2
6
111
(5.1)
¥4.4%
2
6
111
(5.1)
¥4.4%
2
6
111
(5.1)
¥4.4%
2
6
(2010$ millions) ................
........................
8
8
8
8
For the sign ballast product class,
DOE analyzed only one efficiency level;
thus, the results are the same at each
TSL. TSLs 1 through 3B represent EL1
for the sign ballast product class. At
TSLs 1 through 3B, DOE estimates
impacts on INPV to range from ¥$4.2
million to ¥$5.1 million, or a change in
INPV of ¥2.9 percent to ¥4.4 percent.
At these levels, industry free cash flow
is estimated to decrease by
approximately 38 percent to $4.9
million, compared to the base-case
value of $7.9 million in the year leading
up to the energy conservation standards.
As shown by the results, DOE expects
sign ballast manufacturers overall to
face small negative impacts under TSLs
1 through 3B. DOE estimates that 64
percent of the sign ballast product class
shipments would meet EL1 in the base
case. Many manufacturers already
produce electronic sign ballasts, which
is the design option represented by EL1.
Many other manufacturers, however,
produce only magnetic T12 sign ballasts
and therefore would face significant
capital exposure in moving from
magnetic to electronic ballasts to meet
TSLs 1 through 3B. For that reason, DOE
estimates relatively high capital
conversion costs of $6 million for sign
ballast manufacturers. Product redesign
and testing costs are expected to total $2
million for sign ballasts. DOE notes that
small sign ballast manufacturers,
particularly those who would be
required to move from magnetic to
electronic sign ballasts as a result of
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2
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today’s standards, may apply to DOE for
an exemption from the standard
pursuant to 42 U.S.C. 6295(t). The
process applicants must follow to
request an exemption and DOE’s
process for making a decision on a
particular request are set forth in DOE’s
regulations at 10 CFR 430 Subpart E.
Unlike most product classes, sign
ballasts are expected to decrease rather
than increase in price moving from
baseline to EL1 by a shipment-weighted
average decrease in MPC of over 4
percent. This is because electronic
ballasts are a cheaper alternative to
magnetic ballasts, even though the
industry has not yet fully moved toward
electronic production. During
interviews, manufacturers stated that
consumers were reluctant to convert to
electronic ballasts even though there
were no technical barriers to doing so.
Under the preservation of operating
profit markup scenario, however,
manufacturers are able to maintain the
base-case operating profit for the year
following the compliance date of new
and amended standards despite lower
production costs, so the average markup
increases slightly to 1.41 to account for
the decrease in MPC. Despite this
markup increase, revenue is lower at
TSLs 1 through 3B than in the base case
because of the lower average unit price
and the $8 million in conversion costs.
When the preservation of operating
profit markup is combined with the
existing technologies scenario rather
than the emerging technologies
PO 00000
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scenario, the impact of this maximized
revenue per unit is greatest because it is
applied to a larger total quantity of
shipments.
e. Cumulative Regulatory Burden
While any one regulation may not
impose a significant burden on
manufacturers, the combined effects of
recent or impending regulations may
have serious consequences for some
manufacturers, groups of manufacturers,
or an entire industry. Assessing the
impact of a single regulation may
overlook this cumulative regulatory
burden. In addition to energy
conservation standards, other
regulations can significantly affect
manufacturers’ financial operations.
Multiple regulations affecting the same
manufacturer can strain profits and lead
companies to abandon product lines or
markets with lower expected future
returns than competing products. For
these reasons, DOE conducts an analysis
of cumulative regulatory burden as part
of its rulemakings pertaining to
appliance efficiency.
During previous stages of this
rulemaking, DOE identified a number of
requirements, in addition to new and
amended energy conservation standards
for ballasts, that manufacturers of these
products will face for products and
equipment they manufacture within
approximately 3 years prior to and 3
years after the anticipated compliance
date of the new and amended standards.
DOE discusses these and other
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requirements, including the energy
conservation standards for lamps that
take effect beginning in 2012 (74 FR
34080 (July 14, 2009) and U.S.C. 6295
(i)(1)(A)), in its full cumulative
regulatory burden analysis in chapter 13
of the TSD.
In written comments on the NOPR,
NEMA expressed concern that DOE has
not accounted for other legislation that
would increase costs. (NEMA, No. 47 at
p. 9) While it is not clear to which other
legislation NEMA is referring, DOE does
take into account the cost of compliance
with other published Federal energy
conservation standards, such as the
2009 lamps rule. DOE does not include
the impacts of standards that have not
yet been finalized, however, because
any impacts of such standards would be
speculative. The cumulative regulatory
impact analysis is discussed in more
detail in chapter 13 of the TSD. In
response to the September 2011 NODA,
NEMA also noted that President Obama
stated an objective in a September 8,
2011 speech of reducing regulatory
burden on manufacturers. (NEMA, No.
56 at p. 3) DOE acknowledges the
President’s objective of reducing
regulatory burden and, as required by
EPCA, ensures that each of its energy
conservation standards is economically
justified. DOE has analyzed the various
TSLs considered in this rulemaking and
believes that the burdens of today’s
rulemaking are outweighed and justified
by the benefits of the rule, as described
in section VII.C.2.
70613
3. National Impact Analysis
a. Significance of Energy Savings
To estimate the energy savings
through 2043 attributable to potential
energy conservation standards for
ballasts, DOE compared the energy
consumption of these products under
the base case to their anticipated energy
use under each TSL. Table VII.31
presents DOE’s forecasts of the national
energy savings for each TSL, for the
existing and emerging technologies
shipment scenarios that represent the
maximum and minimum energy savings
resulting from all the scenarios
analyzed. Chapter 11 of the final rule
TSD describes these estimates in more
detail.
TABLE VII.31—SUMMARY OF CUMULATIVE NATIONAL ENERGY SAVINGS FOR BALLASTS
[2014–2043]
National energy savings quads
Trial
standard
level
1 ..................
Product class
Existing
technologies,
shift
IS and RS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...................................................................................................
Four 4-foot MBP lamps ...................................................................................................
Two 8-foot slimline lamps ...............................................................................................
PS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...................................................................................................
Four 4-foot MBP lamps ...................................................................................................
Two 4-foot MiniBP SO lamps .........................................................................................
Two 4-foot MiniBP HO lamps .........................................................................................
IS and RS ballasts (not classified as sign ballasts) that operate:
Two 8-foot HO lamps ......................................................................................................
Sign ballasts that operate:
Four 8-foot HO lamps .....................................................................................................
IS and RS residential ballasts that operate:
Two 4-foot MBP lamps ...................................................................................................
1.19
0
0
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3A ................
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E:\FR\FM\14NOR2.SGM
0.01
3.50
1.36
1.19
0
0.02
0.42
0
0.001
0.27
0.33
0.78
0.43
0.13
0.13
0.25
0.39
0.04
0.04
0.92
0.69
0.13
0.01
4.10
2.05
1.44
0.31
0.02
0.55
0.12
0.02
0.30
0.33
1.51
0.56
14NOR2
0.69
0.13
IS and RS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...................................................................................................
Four 4-foot MBP lamps ...................................................................................................
Two 8-foot slimline lamps ...............................................................................................
PS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...................................................................................................
Four 4-foot MBP lamps ...................................................................................................
Two 4-foot MiniBP SO lamps .........................................................................................
Two 4-foot MiniBP HO lamps .........................................................................................
0.04
0.92
Total (TSL2) .............................................................................................................
0.13
0.10
0.16
0.23
0.04
IS and RS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...................................................................................................
Four 4-foot MBP lamps ...................................................................................................
Two 8-foot slimline lamps ...............................................................................................
PS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...................................................................................................
Four 4-foot MBP lamps ...................................................................................................
Two 4-foot MiniBP SO lamps .........................................................................................
Two 4-foot MiniBP HO lamps .........................................................................................
IS and RS ballasts (not classified as sign ballasts) that operate:
Two 8-foot HO lamps ......................................................................................................
Sign ballasts that operate:
Four 8-foot HO lamps .....................................................................................................
IS and RS residential ballasts that operate:
Two 4-foot MBP lamps ...................................................................................................
0.001
0
0
0.27
0.27
0.43
0.25
Total (TSL1) .............................................................................................................
2 ..................
Emerging
technologies,
roll-up
0.14
0.13
0.51
0.52
70614
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.31—SUMMARY OF CUMULATIVE NATIONAL ENERGY SAVINGS FOR BALLASTS—Continued
[2014–2043]
National energy savings quads
Trial
standard
level
Product class
Existing
technologies,
shift
IS and RS ballasts (not classified as sign ballasts) that operate:
Two 8-foot HO lamps ......................................................................................................
Sign ballasts that operate:
Four 8-foot HO lamps .....................................................................................................
IS and RS residential ballasts that operate:
Two 4-foot MBP lamps ...................................................................................................
0.04
b. Net Present Value of Consumer Costs
and Benefits
DOE estimated the cumulative NPV to
the nation of the total costs and savings
for consumers that would result from
particular standard levels for ballasts. In
accordance with the OMB’s guidelines
on regulatory analysis (OMB Circular
A–4, section E, September 17, 2003),
DOE calculated NPV using both a 7percent and a 3-percent real discount
rate. The 7-percent rate is an estimate of
the average before-tax rate of return to
private capital in the U.S. economy, and
reflects the returns to real estate and
small business capital as well as
corporate capital. DOE used this
discount rate to approximate the
opportunity cost of capital in the private
sector, because recent OMB analysis has
found the average rate of return to
capital to be near this rate. In addition,
DOE used the 3-percent rate to capture
the potential effects of standards on
private consumption (e.g., through
higher prices for products and the
purchase of reduced amounts of energy).
This rate represents the rate at which
society discounts future consumption
flows to their present value. This rate
can be approximated by the real rate of
return on long-term government debt
(i.e., yield on Treasury notes minus
annual rate of change in the Consumer
0.01
5.55
2.74
1.44
0.31
0.02
0.55
0.12
0.02
0.30
0.33
1.51
0.56
0.14
0.13
0.51
0.52
0.04
0.04
0.92
0.69
0.13
0.12
5.56
Total (TSL3B) ..........................................................................................................
0.69
0.13
IS and RS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...................................................................................................
Four 4-foot MBP lamps ...................................................................................................
Two 8-foot slimline lamps ...............................................................................................
PS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...................................................................................................
Four 4-foot MBP lamps ...................................................................................................
Two 4-foot MiniBP SO lamps .........................................................................................
Two 4-foot MiniBP HO lamps .........................................................................................
IS and RS ballasts (not classified as sign ballasts) that operate:
Two 8-foot HO lamps ......................................................................................................
Sign ballasts that operate:
Four 8-foot HO lamps .....................................................................................................
IS and RS residential ballasts that operate:
Two 4-foot MBP lamps ...................................................................................................
0.04
0.92
Total (TSL3A) ..........................................................................................................
3B ................
Emerging
technologies,
roll-up
2.86
Price Index), which has averaged about
3 percent on a pre-tax basis for the last
30 years.
Table VII.32 shows the consumer NPV
results for each TSL DOE considered for
ballasts, using both a 7-percent and a 3percent discount rate. This table
presents the results of the two shipment
scenarios that represent the maximum
and minimum NPV resulting from all
the scenarios analyzed. Zero values
indicate product types with zero energy
savings at a particular TSL, i.e., the
corresponding efficiency level is a
baseline design. See chapter 11 of the
final rule TSD for more detailed NPV
results.
TABLE VII.32—SUMMARY OF CUMULATIVE NET PRESENT VALUE FOR BALLASTS (2014–2043)
Net present value
billion 2010$
Trial standard
level
Product class
Existing technologies, shift
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7 Percent
discount rate
1 ...................
VerDate Mar<15>2010
IS and RS ballasts (not classified as residential) that
operate:
Two 4-foot MBP lamps ...........................................
Four 4-foot MBP lamps ..........................................
Two 8-foot slimline lamps .......................................
PS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...........................................
Four 4-foot MBP lamps ..........................................
18:36 Nov 10, 2011
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Emerging technologies, roll-up
3 Percent
discount rate
7 Percent
discount rate
3 Percent
discount rate
2.33
0
0
0.01
0
0
0.01
0
0
0.77
0.61
Sfmt 4700
5.20
0
0
1.40
1.35
0.51
0.30
0.78
0.58
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70615
TABLE VII.32—SUMMARY OF CUMULATIVE NET PRESENT VALUE FOR BALLASTS (2014–2043)—Continued
Net present value
billion 2010$
Trial standard
level
Product class
Existing technologies, shift
7 Percent
discount rate
Two 4-foot MiniBP SO lamps .................................
Two 4-foot MiniBP HO lamps .................................
IS and RS ballasts (not classified as sign ballasts) that
operate two 8-foot HO lamps.
Sign ballasts that operate four 8-foot HO lamps ...........
IS and RS residential ballasts that operate two 4-foot
MBP lamps.
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18:36 Nov 10, 2011
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5.55
0.49
2.52
0.16
4.62
0.27
17.43
4.59
8.28
5.20
0
0.10
1.08
0
0.01
2.15
0
0.01
1.40
1.61
3.09
0.94
0.13
0.51
0.37
0.68
0.43
0.11
0.78
0.72
1.31
0.94
0.13
5.55
0.49
2.52
0.16
4.62
0.27
8.91
18.50
5.85
10.92
2.83
0.46
0.05
6.31
1.06
0.10
1.44
0.25
0.05
2.86
0.52
0.10
0.84
0.73
1.52
0.36
0.11
1.54
1.61
3.89
0.87
0.13
0.56
0.37
0.85
0.36
0.11
0.87
0.72
1.87
0.87
0.13
2.94
0.22
5.55
0.49
2.52
0.16
4.62
0.27
10.06
21.55
6.67
12.84
2.83
0.46
0.05
6.31
1.06
0.10
1.44
0.25
0.05
2.86
0.52
0.10
0.84
0.73
1.52
0.36
0.11
1.54
1.61
3.89
0.87
0.13
0.56
0.37
0.85
0.36
0.11
0.87
0.72
1.87
0.87
0.13
2.94
0.23
5.55
0.50
2.52
0.23
4.62
0.50
10.06
Sfmt 4700
1.02
0.88
0.12
2.94
0.22
IS and RS ballasts (not classified as residential) that
operate:
Two 4-foot MBP lamps ...........................................
Four 4-foot MBP lamps ..........................................
Two 8-foot slimline lamps .......................................
PS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...........................................
Four 4-foot MBP lamps ..........................................
Two 4-foot MiniBP SO lamps .................................
Two 4-foot MiniBP HO lamps .................................
IS and RS ballasts (not classified as sign ballasts) that
operate two 8-foot HO lamps.
Sign ballasts that operate four 8-foot HO lamps ...........
IS and RS residential ballasts that operate two 4-foot
MBP lamps.
0.57
0.42
0.10
0.77
0.73
1.33
0.42
0.11
IS and RS ballasts (not classified as residential) that
operate:
Two 4-foot MBP lamps ...........................................
Four 4-foot MBP lamps ..........................................
Two 8-foot slimline lamps .......................................
PS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...........................................
Four 4-foot MBP lamps ..........................................
Two 4-foot MiniBP SO lamps .................................
Two 4-foot MiniBP HO lamps .................................
IS and RS ballasts (not classified as sign ballasts) that
operate two 8-foot HO lamps.
Sign ballasts that operate four 8-foot HO lamps ...........
IS and RS residential ballasts that operate two 4-foot
MBP lamps.
2.45
0.88
0.12
2.33
0
0.05
IS and RS ballasts (not classified as residential) that
operate:
Two 4-foot MBP lamps ...........................................
Four 4-foot MBP lamps ..........................................
Two 8-foot slimline lamps .......................................
PS ballasts (not classified as residential) that operate:
Two 4-foot MBP lamps ...........................................
Four 4-foot MBP lamps ..........................................
Two 4-foot MiniBP SO lamps .................................
Two 4-foot MiniBP HO lamps .................................
IS and RS ballasts (not classified as sign ballasts) that
operate two 8-foot HO lamps.
Sign ballasts that operate four 8-foot HO lamps ...........
IS and RS residential ballasts that operate two 4-foot
MBP lamps.
Total (TSL3B) .........................................................
VerDate Mar<15>2010
3 Percent
discount rate
8.52
Total (TSL3A) ..................................................
3B ................
7 Percent
discount rate
2.94
0.22
Total (TSL2) .....................................................
3A ................
3 Percent
discount rate
1.11
0.42
0.11
Total (TSL1) .....................................................
2 ...................
Emerging technologies, roll-up
21.56
6.73
13.07
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c. Impacts on Employment
DOE estimated the indirect
employment impacts of potential
standards on the economy in general,
assuming that energy conservation
standards for ballasts would reduce
energy bills for ballast users and the
resulting net savings would be
redirected to other forms of economic
activity. DOE used an I–O model of the
U.S. economy to estimate these effects
including the demand for labor as
described in section V.I .
The I–O model results suggest that
today’s adopted standards are likely to
increase the net labor demand. The
gains, however, would most likely be
small relative to total national
employment, and neither the BLS data
nor the input/output model DOE uses
includes the quality or wage level of the
jobs. As discussed in section VII.B.2.b,
the major manufacturers interviewed for
this rulemaking indicate they have no
domestic ballast production. New and
amended standards for ballasts therefore
will not have a significant impact on the
limited number of production workers
directly employed by ballast
manufacturers in the U.S.
Table VII.33—presents the estimated
net indirect employment impacts from
the TSLs that DOE considered in this
rulemaking. See chapter 15 of the final
rule TSD for more detailed results.
TABLE VII.33–NET CHANGE IN JOBS FROM INDIRECT EMPLOYMENT EFFECTS UNDER BALLAST TSLS
Net national change in jobs
(thousands)
Analysis period year
Trial standard level
Existing technologies, shift
2020 ..........................................................................
2043 ..........................................................................
4. Impact on Utility or Performance of
Products
As presented in section IV.D.1.d of
this final rule, DOE concluded that none
of the TSLs considered in this final rule
would reduce the utility or performance
of the products under consideration in
this rulemaking. Furthermore,
manufacturers of these products
currently offer ballasts that meet or
exceed the adopted standards. (42
U.S.C. 6295(o)(2)(B)(i)(IV))
5. Impact of Any Lessening of
Competition
As discussed in the April 2011 NOPR,
and in section IV.D.1.e of this final rule,
DOE considers any lessening of
competition likely to result from
standards; the Attorney General
1 ................................................................................
2 ................................................................................
3A .............................................................................
3B .............................................................................
1 ................................................................................
2 ................................................................................
3A .............................................................................
3B .............................................................................
determines the impact, if any, of any
such lessening of competition.
DOJ concluded that the standards
contained in the proposed rule could
possibly impact competition. Depending
on the investment required and the
opportunity for business expansion, DOJ
found it is not clear how quickly current
manufacturers could comply with new
standards. DOE considered these
comments and notes that TSL 3A, the
level adopted in today’s rule, would
impact manufacturers to a lesser extent
than the TSL 3 proposed in the April
2011 NOPR. Specifically, TSL 3A
contains lower standards for residential
and 8-foot HO product classes than the
previously proposed TSL 3. Therefore,
DOE does not expect that TSL 3A will
raise competitive issues. For all product
Emerging technologies, roll-up
2.5
2.3
2.2
2.2
52.2
57.1
73.8
73.9
1.9
2.1
2.1
2.2
17.2
24.2
30.7
34.3
classes analyzed, DOE found that
multiple manufacturers offered products
at TSL 3A and any product
modifications needed to reach TSL 3A
do not require proprietary technology.
6. Need of the Nation To Conserve
Energy
An improvement in the energy
efficiency of the products subject to this
final rule is likely to improve the
security of the nation’s energy system by
reducing overall demand for energy.
Reduced electricity demand may also
improve the reliability of the electricity
system. As a measure of this reduced
demand, Table VII.34 presents the
estimated reduction in generating
capacity in 2043 for the TSLs that DOE
considered in this rulemaking.
TABLE VII.34—ESTIMATED REDUCTION IN ELECTRICITY GENERATING CAPACITY IN 2043 UNDER BALLAST TSLS
Reduction in electric generating
capacity
Gigawatts
Trial standard level
mstockstill on DSK4VPTVN1PROD with RULES2
Existing technologies, shift
1 .......................................................................................................................................................................
2 .......................................................................................................................................................................
3A .....................................................................................................................................................................
3B .....................................................................................................................................................................
Energy savings from new and
amended standards for ballasts could
also produce environmental benefits in
the form of reduced emissions of air
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pollutants and GHGs associated with
electricity production. Table VII.35
provides DOE’s estimate of cumulative
CO2, NOX, and Hg emissions reductions
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3.8
4.6
6.4
6.4
projected to result from the TSLs
considered in this rulemaking. DOE
reports annual CO2, NOX, and Hg
emissions reductions for each TSL in
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2.2
3.0
3.1
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
70617
the environmental assessment of in
chapter 16 the final rule TSD.
TABLE VII.35—SUMMARY OF EMISSIONS REDUCTION ESTIMATED FOR BALLAST TSLS (CUMULATIVE FOR 2014 THROUGH
2043)
Cumulative reduction in emissions (2014 through 2043)
Existing technologies, shift
Trial standard level
NOX
kt
CO2
Mt
1 .......................................
2 .......................................
3A .....................................
3B .....................................
64
76
106
106
As discussed in section V.K, DOE did
not report SO2 emissions reductions
from power plants because there is
uncertainty about the effect of energy
conservation standards on the overall
level of SO2 emissions in the United
States due to SO2 emissions caps. DOE
also did not include NOX emissions
reduction from power plants in States
subject to CAIR because an energy
conservation standard would not affect
the overall level of NOX emissions in
those States due to the emissions caps
mandated by CAIR.
As part of the analysis for this final
rule, DOE estimated monetary benefits
likely to result from the reduced
emissions of CO2 and NOX that DOE
estimated for each of the TSLs
considered. As discussed in section
V.L.1, DOE used values for the SCC
developed by an interagency process.
The four values for CO2 emissions
reductions resulting from that process
(for emissions in 2010, expressed in
2010$) are $4.9/ton (the average value
from a distribution that uses a 5-percent
discount rate), $22.3/ton (the average
value from a distribution that uses a 3percent discount rate), $36.5/ton (the
average value from a distribution that
uses a 2.5-percent discount rate), and
Emerging technologies, roll-up
Hg
t
23
28
39
39
CO2
Mt
0.88
1.05
1.47
1.47
$67.6/ton (the 95th-percentile value
from a distribution that uses a 3-percent
discount rate). These values correspond
to the value of emission reductions in
2010; the values for later years are
higher due to increasing damages as the
magnitude of climate change increases.
For each TSL, DOE calculated the global
present values of CO2 emissions
reductions, using the same discount rate
as was used in the studies upon which
the dollar-per-ton values are based. DOE
calculated domestic values as a range
from 7 percent to 23 percent of the
global values.
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 world economy
continues to evolve rapidly. Thus, any
value placed in this rulemaking on
reducing CO2 emissions is subject to
change. DOE, together with other
Federal agencies, will continue to
review various methodologies for
estimating the monetary value of
reductions in CO2 and other GHG
emissions. This ongoing review will
consider the comments on this subject
that are part of the public record for this
NOX
kt
13
20
27
29
Hg
t
10
16
22
23
0.18
0.29
0.40
0.42
and other rulemakings, as well as other
methodological assumptions and issues.
However, consistent with DOE’s legal
obligations, and taking into account the
uncertainty involved with this
particular issue, DOE has included in
this final rule the most recent values
and analyses resulting from the ongoing
interagency review process.
DOE also estimated a range for the
cumulative monetary value of the
economic benefits associated with NOX
and Hg emissions reductions
anticipated to result from amended
ballast standards. Estimated monetary
benefits for CO2, NOX and Hg emission
reductions are detailed in chapter 17 of
the final rule TSD.
The NPV of the monetized benefits
associated with emissions reductions
can be viewed as a complement to the
NPV of the consumer savings calculated
for each TSL considered in this
rulemaking. Table VII.36 shows an
example of the calculation of the
combined NPV including benefits from
emissions reductions for the case of TSL
3A for ballasts. The CO2 values used in
the table correspond to the four
scenarios for the valuation of CO2
emission reductions presented in
section V.L.1.
TABLE VII.36—ADDING NET PRESENT VALUE OF CONSUMER SAVINGS TO PRESENT VALUE OF MONETIZED BENEFITS
FROM CO2 AND NOX EMISSIONS REDUCTIONS AT TSL 3A FOR BALLASTS
[Existing Technologies, Shift]
Present value
billion 2010$
Category
Discount rate %
Benefits
mstockstill on DSK4VPTVN1PROD with RULES2
Operating Cost Savings ...............................................................................................................................
15.1
31.5
0.40
2.01
3.38
6.12
0.03
0.06
17.1
CO2 Reduction Monetized Value (at $4.9/Metric Ton)* ..............................................................................
CO2 Reduction Monetized Value (at $22.3/Metric Ton)* ............................................................................
CO2 Reduction Monetized Value (at $36.5/Metric Ton)* ............................................................................
CO2 Reduction Monetized Value (at $67.6/Metric Ton)* ............................................................................
NOX Reduction Monetized Value (at $2,537/Ton)* .....................................................................................
Total Monetary Benefits
VerDate Mar<15>2010
**
...........................................................................................................................
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3
5
3
2.5
3
7
3
7
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TABLE VII.36—ADDING NET PRESENT VALUE OF CONSUMER SAVINGS TO PRESENT VALUE OF MONETIZED BENEFITS
FROM CO2 AND NOX EMISSIONS REDUCTIONS AT TSL 3A FOR BALLASTS—Continued
[Existing Technologies, Shift]
Present value
billion 2010$
Category
Discount rate %
33.5
3
Costs
Total Incremental Installed Costs ................................................................................................................
5.05
9.91
7
3
Net Benefits/Costs
Including CO2 and NOX** ............................................................................................................................
12.1
23.6
7
3
* The CO values represent global monetized values (in 2010$) of the social cost of CO emissions in 2010 under several scenarios. The val2
2
ues of $4.9, $22.3, and $36.5 per metric ton are the averages of SCC distributions calculated using 5-percent, 3-percent, and 2.5-percent discount rates, respectively. The value of $67.6/t represents the 95th percentile of the SCC distribution calculated using a 3-percent discount rate.
The value for NOX (in 2010$) is the average of the low and high values used in DOE’s analysis. See section V.L.2 for details.
** Total Benefits for both the 3-percent and 7-percent cases are derived using the SCC value calculated at a 3-percent discount rate, which is
$22.3/t in 2010 (in 2010$).
Although adding the value of
consumer savings to the values of
emission reductions would provide a
valuable perspective, the following
should be considered: (1) the national
consumer savings are domestic U.S.
consumer monetary savings found in
market transactions, while the values of
emissions reductions are based on
estimates of marginal social costs,
which, in the case of CO2, are based on
a global value; and (2) the assessments
of consumer savings and emissionrelated benefits are performed with
different computer models, leading to
different timeframes for analysis. For
ballasts, the present value of national
consumer savings is measured for the
period in which units shipped (2014–
2043) continue to operate. However, the
time frames of the benefits associated
with the emission reductions differ. For
example, the value of CO2 emissions
reductions reflects the present value of
all future climate-related impacts due to
emitting a ton of CO2 in that year, out
to 2300. Chapter 17 of the final rule TSD
presents calculations of the combined
NPV including benefits from emissions
reductions for each TSL.
C. Conclusions
EPCA requires that any new or
amended energy conservation standard
for any type (or class) of covered
product 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 after considering, to the greatest
extent practicable, the seven statutory
factors discussed previously. (42 U.S.C.
6295(o)(2)(B)(i)) The new or amended
standard must also result in a significant
conservation of energy. (42 U.S.C.
6295(o)(3)(B))
DOE considered the impacts of
standards at each trial standard level,
beginning with the maximum
technologically feasible level, to
determine whether that level met the
evaluation criteria. If 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.
DOE discusses the benefits and/or
burdens of each trial standard level in
the following sections. DOE bases its
discussion on quantitative analytical
results for each trial standard level
(presented in section VII.A) such as
national energy savings, net present
value (discounted at 7 and 3 percent),
emissions reductions, industry net
present value, life-cycle cost, and
consumers’ installed price increases.
Beyond the quantitative results, DOE
also considers other burdens and
benefits that affect economic
justification, including how
technological feasibility, manufacturer
costs, and impacts on competition may
affect the economic results presented.
To aid the reader as DOE discusses
the benefits and burdens of each trial
standard level, DOE has included the
following tables that present a summary
of the results of DOE’s quantitative
analysis for each TSL. These include the
impacts on identifiable subgroups of
consumers, specifically low-income
households, institutions of religious
worship, and institutions that serve lowincome populations, who may be
disproportionately affected by an
amended national standard. Section
VII.B.1 presents the estimated impacts
of each TSL for these subgroups.
TABLE VII.37—SUMMARY OF RESULTS FOR BALLASTS
mstockstill on DSK4VPTVN1PROD with RULES2
[Existing Technologies, Shift]
Category
TSL 1
TSL 2
TSL 3A
TSL 3B
National Energy Savings (quads) ........................................................
3.50 ..................
4.10 ..................
5.55 ..................
5.56
21.55 ................
21.56
NPV of Consumer Benefits (2010$ billion)
3% discount rate ..................................................................................
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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.37—SUMMARY OF RESULTS FOR BALLASTS—Continued
[Existing Technologies, Shift]
Category
TSL 1
TSL 2
TSL 3A
TSL 3B
7% discount rate ..................................................................................
8.52 ..................
8.91 ..................
10.06 ................
10.06
1,176 ................
¥3.5% ..............
1,144 ................
¥6.1% ..............
1,141
¥6.4%
106 ...................
39 .....................
1.47 ..................
106
39
1.47
0.40 to 6.12 ......
58 .....................
31 .....................
0.40 to 6.13
58
31
Industry Impacts
Industry NPV (2010$ million) ...............................................................
Industry NPV (% change) ....................................................................
1,199 ................
¥1.6% ..............
Cumulative Emissions Reduction
CO2 (Mt) ...............................................................................................
NOX (kt) ...............................................................................................
Hg (t) ....................................................................................................
64 .....................
23 .....................
0.88 ..................
76 .....................
28 .....................
1.05 ..................
Value of Cumulative Emissions Reduction
CO2 (2010$ billion)* .............................................................................
NOX—3% discount rate (2010$ million) ..............................................
NOX—7% discount rate (2010$ million) ..............................................
0.24 to 3.68 ......
35 .....................
18 .....................
0.29 to 4.40 ......
41 .....................
22 .....................
Mean LCC Savings (replacement event, per ballast)** (2010$)
IS and RS ballasts (not classified as residential) that operate: ..........
Two 4-foot MBP lamps.
Four 4-foot MBP lamps.
Two 8-foot slimline lamps.
PS ballasts (not classified as residential) that operate: ......................
Two 4-foot MBP lamps.
Four 4-foot MBP lamps.
Two 4-foot MiniBP SO lamps.
Two 4-foot MiniBP HO lamps.
IS and RS ballasts (not classified as sign ballasts) that operate two
8-foot HO lamps
Sign ballasts that operate four 8-foot HO lamps
IS and RS residential ballasts that operate two 4-foot MBP lamps ....
29 .....................
5 to 34 ..............
7 to 37 ..............
7 to 37
¥2 to 26: ..........
6 to 32 ..............
6 to 28 ..............
6 to 28
65 .....................
230 ...................
230 ...................
3 to 233
403 ...................
21 .....................
403 ...................
21 .....................
403 ...................
21 .....................
403
¥2 to 19
Median PBP (replacement event)*** (years)
IS and RS ballasts (not classified as residential) that operate: ..........
Two 4-foot MBP lamps.
Four 4-foot MBP lamps.
Two 8-foot slimline lamps.
PS ballasts (not classified as residential) that operate: ......................
Two 4-foot MBP lamps.
Four 4-foot MBP lamps.
Two 4-foot MiniBP SO lamps.
Two 4-foot MiniBP HO lamps.
IS and RS ballasts (not classified as sign ballasts) that operate two
8-foot HO lamps.
Sign ballasts that operate four 8-foot HO lamps .................................
IS and RS residential ballasts that operate two 4-foot MBP lamps ....
¥3.35 ...............
¥1.66 to 3.62 ..
¥1.30 to 2.86 ...
¥1.30 to 2.86
0.05 to 20.52 ....
0.55 to 6.00 ......
1.25 to 6.00 ......
1.25 to 6.00
¥0.66 ...............
¥0.69 ...............
¥0.69 ...............
¥0.53 to 4.57
¥0.16 ...............
¥5.46 ...............
¥0.16 ...............
¥5.46 ...............
¥0.16 ...............
¥5.46 ...............
¥0.16
¥4.92
Distribution of Consumer LCC Impacts (see Table VII.16 through Table VII.23)
Generation Capacity Reduction (GW)† ...............................................
3.82 ..................
4.56 ..................
6.35 ..................
6.35
57 .....................
74 .....................
74
Employment Impacts
Indirect Domestic Jobs (thousands) † ..................................................
52 .....................
mstockstill on DSK4VPTVN1PROD with RULES2
* Range of the economic value of CO2 reductions is based on estimates of the global benefit of reduced CO2 emissions.
** For LCCs, a negative value means an increase in LCC by the amount indicated.
*** For PBPs, negative values indicate standards that reduce operating costs and installed costs; ‘‘N/A’’ indicates standard levels that do not
reduce operating costs.
† Changes in 2043.
TABLE VII.38—SUMMARY OF RESULTS FOR BALLASTS
[Emerging Technologies, Roll-up]
Category
TSL 1
TSL 2
TSL 3A
National Energy Savings (quads) ........................................................
1.36 ..................
2.05 ..................
2.74 ..................
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2.86
70620
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
TABLE VII.38—SUMMARY OF RESULTS FOR BALLASTS—Continued
[Emerging Technologies, Roll-up]
Category
TSL 1
TSL 2
TSL 3A
TSL 3B
10.92 ................
5.85 ..................
12.84 ................
6.67 ..................
13.07
6.73
545 ...................
¥25.7% ............
464 ...................
¥36.7% ............
431
¥41.1%
27 .....................
22 .....................
0.40 ..................
29
23
0.42
0.12 to 1.75 ......
29 .....................
13 .....................
0.13 to 1.84
30
14
NPV of Consumer Benefits (2010$ billion)
3% discount rate ..................................................................................
7% discount rate ..................................................................................
8.28 ..................
4.59 ..................
Industry Impacts
Industry NPV (2010$ million) ...............................................................
Industry NPV (% change) ....................................................................
616 ...................
¥15.9% ............
Cumulative Emissions Reduction
CO2 (Mt) ...............................................................................................
NOX (kt) ...............................................................................................
Hg (t) ....................................................................................................
13 .....................
10 .....................
0.18 ..................
20 .....................
16 .....................
0.29 ..................
Value of Cumulative Emissions Reduction
CO2 (2010$ billion) * ............................................................................
NOX–3% discount rate (2010$ million) ................................................
NOX–7% discount rate (2010$ million) ................................................
0.06 to 0.80 ......
13 .....................
6 .......................
0.09 to 1.27 ......
21 .....................
10 .....................
Mean LCC Savings (replacement event, per ballast) ** (2010$)
IS and RS ballasts (not classified as residential) that operate ...........
Two 4-foot MBP lamps.
Four 4-foot MBP lamps.
Two 8-foot slimline lamps.
PS ballasts (not classified as residential) that operate .......................
Two 4-foot MBP lamps.
Four 4-foot MBP lamps.
Two 4-foot MiniBP SO lamps.
Two 4-foot MiniBP HO lamps.
IS and RS ballasts (not classified as sign ballasts) that operate Two
8-foot HO lamps.
Sign ballasts that operate Four 8-foot HO lamps ................................
IS and RS residential ballasts that operate Two 4-foot MBP lamps ...
29 .....................
5 to 34 ..............
7 to 37 ..............
7 to 37
¥2 to 26 ...........
6 to 32 ..............
6 to 28 ..............
6 to 28
65 .....................
230 ...................
230 ...................
3 to 233
403 ...................
21 .....................
403 ...................
21 .....................
403 ...................
21 .....................
403
¥2 to 19
Median PBP (replacement event)*** (years)
IS and RS ballasts (not classified as residential) that operate ...........
Two 4-foot MBP lamps.
Four 4-foot MBP lamps.
Two 8-foot slimline lamps.
PS ballasts (not classified as residential) that operate .......................
Two 4-foot MBP lamps.
Four 4-foot MBP lamps.
Two 4-foot MiniBP SO lamps.
Two 4-foot MiniBP HO lamps.
IS and RS ballasts (not classified as sign ballasts) that operate Two
8-foot HO lamps.
Sign ballasts that operate Four 8-foot HO lamps ................................
IS and RS residential ballasts that operate Two 4-foot MBP lamps ...
¥3.35 ...............
¥1.66 to 3.62 ...
¥1.30 to 2.86 ..
¥1.30 to 2.86
0.05 to 20.52 ....
0.55 to 6.00 ......
1.25 to 6.00 ......
1.25 to 6.00
¥0.66 ...............
¥0.69 ...............
¥0.69 ...............
¥0.53 to 4.57
¥0.16 ...............
¥5.46 ...............
¥0.16 ...............
¥5.46 ...............
¥0.16 ...............
¥5.46 ...............
¥0.16
¥4.92
Distribution of Consumer LCC Impacts (see Table VII.16 through Table VII.23)
Generation Capacity Reduction (GW) † ..............................................
1.37 ..................
2.18 ..................
2.99 ..................
3.14
24 .....................
31 .....................
34
Employment Impacts
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Indirect Domestic Jobs (thousands)† ..................................................
17 .....................
* Range of the economic value of CO2 reductions is based on estimates of the global benefit of reduced CO2 emissions.
** For LCCs, a negative value means an increase in LCC by the amount indicated.
*** For PBPs, negative values indicate standards that reduce operating costs and installed costs; ‘‘N/A’’ indicates standard levels that do not
reduce operating costs.
† Changes in 2043.
DOE also notes that the economics
literature provides a wide-ranging
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discussion of how consumers trade off
upfront costs and energy savings in the
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absence of government intervention.
Much of this literature attempts to
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explain why consumers undervalue
energy efficiency improvements. This
undervaluation suggests that regulation
that promotes energy efficiency can
produce significant net private gains (as
well as producing social gains by, for
example, reducing pollution). There is
evidence that consumers undervalue
future energy savings as a result of: (1)
A lack of information, (2) a lack of
sufficient salience of the long-term or
aggregate benefits, (3) a lack of sufficient
savings to warrant delaying or altering
purchases (e.g., an inefficient
ventilation fan in a new building or the
delayed replacement of a water pump),
(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 (e.g., renter versus owner;
builder versus purchaser). Other
literature indicates that with less than
perfect foresight and a high degree of
uncertainty about the future, consumers
may trade off investments in efficiency
at a higher than expected rate between
current consumption and uncertain
future energy cost savings.
In its current regulatory analysis, DOE
includes potential changes in the
benefits and costs of a regulation due to
changes in consumer purchase
decisions in two ways. First, if
consumers forego a purchase of a
product in the standards case, it
decreases sales for product
manufacturers and the cost to
manufacturers is included in the MIA.
Second, DOE accounts for energy
savings attributable only to products
used by consumers in the standards
case; if a regulatory option decreases the
number of products used by consumers,
this decreases the potential energy
savings from an energy conservation
standard. DOE provides detailed
estimates of shipments and changes in
the volume of product purchases under
standards in chapter 10 of the TSD.
However, DOE’s current analysis does
not explicitly control for differences in
consumer preferences, preferences
across subcategories of products or
specific features, or consumer price
sensitivity varying with household
income (Reiss and White 2004).
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 has posted
a paper that discusses the issue of
consumer welfare impacts of appliance
energy efficiency standards, and
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70621
potential enhancements to the
methodology by which these impacts
are defined and estimated in the
regulatory process.62 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 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.
TSL 3B, the benefits of energy savings,
emissions reductions (both in physical
reductions and the monetized value of
those reductions), and the positive net
economic savings to the nation would
be outweighed by the economic burden
on consumers (of residential T8 ballasts
and 8-foot HO T8 ballasts) and the large
product and capital conversion costs
that could result in a large reduction in
INPV for manufacturers. Consequently,
the Secretary has concluded that trial
standard level 3B is not economically
justified.
1. Trial Standard Level 3B
DOE first considered the most
efficient level, TSL 3B, which would
save an estimated 2.9 to 5.6 quads of
energy through 2043. For the nation as
a whole, TSL 3B would have a net
savings of $6.7 billion–$10.1 billion at
a 7-percent discount rate, and $13.1
billion–$21.6 billion at a 3-percent
discount rate. The emissions reductions
at TSL 3B are estimated at 29–106
million metric tons (Mt) of CO2, 23–39
kilotons (kt) of NOX, and 0.42–1.47 tons
of Hg. Total generating capacity in 2043
is estimated to decrease compared to the
reference case by 3.14–6.35 gigawatts
under TSL 3B. As seen in section
VII.B.1, while consumers of most
representative ballast types have
available ballast designs which result in
positive LCC savings, ranging from
$2.77–$402.86, some consumers
experience negative LCC savings at TSL
3B. Consumers that experience negative
LCC savings, ranging from ¥$1 to ¥$2,
are those that currently have a 2-lamp
8-foot HO T8 ballast (for the new
construction/renovation event) or a 2lamp 4-foot MBP T8 ballast in the
residential sector (for the replacement
event). The projected change in industry
value would range from a decrease of
$77.6 million to a decrease of $301.2
million, or a net loss of 6.4 percent to
a net loss of 41.1 percent in INPV.
DOE based TSL 3B on the most
efficient commercially available
products for each representative ballast
type analyzed. This TSL represents the
highest efficiency level that is
technologically feasible for a diversity of
products (spanning several ballast
factors, number of lamps per ballast,
and types of lamps operated) within
each product class.
After carefully considering the
analysis and weighing the benefits and
burdens of TSL 3B, the Secretary has
reached the following conclusion: At
2. Trial Standard Level 3A
DOE next considered TSL 3A, which
would save an estimated 2.7 to 5.6
quads of energy through 2043—a
significant amount of energy. For the
nation as a whole, TSL 3A would have
a net savings of $6.7 billion–$10.1
billion at a 7-percent discount rate, and
$12.8 billion–$21.6 billion at a 3percent discount rate. The emissions
reductions at TSL 3A are estimated at
27–106 Mt of CO2, 22–39 kt of NOX, and
0.40–1.47 tons of Hg. Total generating
capacity in 2043 is estimated to
decrease compared to the reference case
by 2.99–6.35 gigawatts under TSL 3A.
As seen in section VII.B.1, TSL 3A
results in positive LCC savings for all
representative ballast types, ranging
from $6–$403. The projected change in
industry value would range from a
decrease of $74.5 million to a decrease
of $268.6 million, or a net loss of 6.1
percent to a net loss of 36.7 percent in
INPV.
DOE based TSL 3A on the most
efficient commercially available
products for each representative ballast
type analyzed except for IS/RS ballasts
in the residential sector and 8-foot HO
ballasts. This TSL represents the highest
efficiency level for a diversity of
products (spanning several ballast
factors, number of lamps per ballast,
and types of lamps operated) at which
consumers of all ballasts types,
including those consumers with T8
residential or 8-foot HO systems,
experience positive LCC savings.
After considering the analysis,
comments on the analysis, and the
benefits and burdens of TSL 3A, the
Secretary has reached the following
conclusion: TSL 3A offers the maximum
improvement in efficiency that is
technologically feasible and
economically justified, and will result
in significant conservation of energy.
The Secretary has reached the
conclusion that the benefits of energy
savings, emissions reductions (both in
physical reductions and the monetized
value of those reductions), the positive
net economic savings to the nation, and
62 Alan Sanstad, Notes on the Economics of
Household Energy Consumption and Technology
Choice. Lawrence Berkeley National Laboratory.
2010. https://www1.eere.energy.gov/buildings/
appliance_standards/pdfs/consumer_ee_theory.pdf.
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positive life-cycle cost savings would
outweigh the reduction in INPV for
manufacturers. Therefore, DOE adopts
the energy conservation standards for
ballasts at TSL 3A.
D. Backsliding
As discussed in section II.A, EPCA
contains what is commonly known as
an ‘‘anti-backsliding’’ provision, which
mandates that the Secretary not
prescribe 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)) Because
DOE is evaluating amended standards in
terms of ballast luminous efficiency,
DOE converted the existing BEF
standards to BLE to verify that the
adopted standards did not constitute
backsliding. The following describes
how DOE completed this comparison.
Ballast efficacy factor is defined as
ballast factor divided by input power
times 100. Ballast factor, in turn, is
currently defined as the test system light
output divided by a reference system
light output. As mentioned in section
IV.A, the active mode test procedure
SNOPR proposed a new method for
calculating ballast factor. 75 FR 71570,
71577–8 (November 24, 2010). The new
methodology entails measuring the
lamp arc power of the test system and
dividing it by the lamp arc power of the
reference system. Because this new
method calculates a ballast factor
equivalent to the existing method, DOE
finds that this definition can be
incorporated into the equation for BEF.
After this substitution, BEF can be
converted to BLE by dividing by 100
and multiplying by the appropriate
reference arc power. Table VII.39
contains the existing standard in terms
of BEF, the existing standard in terms of
BLE, and the adopted standard in terms
of BLE.
TABLE VII.39—EXISTING FEDERAL BEF STANDARDS AND THE CORRESPONDING BLE
Equivalent BLE
Application for operation of
Low freq
One
Two
Two
Two
One
Two
Two
Two
Adopted BLE
BEF Standard
F40T12 lamp ............................................................................................
F40T12 lamps ..........................................................................................
F96T12 lamps ..........................................................................................
F96T12/HO lamps ...................................................................................
F34T12 lamp ............................................................................................
F34T12 lamps ..........................................................................................
F96T12/ES lamps ....................................................................................
F96T12/HO/ES lamps ..............................................................................
2.29
1.17
0.63
0.39
2.61
1.35
0.77
0.42
0.831
0.849
0.888
0.777
0.777
0.804
0.876
0.711
High freq
0.832
0.850
0.897
0.780
0.778
0.805
0.884
0.713
Standard*
0.875
0.899
0.918
0.886
0.809
0.841
0.913
0.881
* For ballast types that could be in more than one product class, this table presents the lowest standard the ballast would be required to meet.
For example, 8-foot HO ballasts can have a PS starting method in addition to IS or RS. Therefore, DOE presents the standard for the PS product class as it is the lowest.
As seen in Table VII.39, the standards
adopted in this final rule are higher than
the existing standards, regardless of low
or high frequency operation. As such,
the adopted standards do not decrease
the minimum required energy efficiency
of the covered products and therefore do
not violate the anti-backsliding
provision in EPCA.
VIII. Procedural Issues and Regulatory
Review
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A. Review Under Executive Orders
12866 and 13563
Section 1(b)(1) of Executive Order
12866, ‘‘Regulatory Planning and
Review,’’ 58 FR 51735 (Oct. 4, 1993),
requires each agency to identify the
problem that it intends to address,
including, where applicable, the failures
of private markets or public institutions
that warrant new agency action, as well
as to assess the significance of that
problem. The problems that today’s
standards address are as follows:
(1) There is a lack of consumer
information and/or information
processing capability about energy
efficiency opportunities in lighting
market.
(2) There is asymmetric information
(one party to a transaction has more and
better information than the other) and/
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or high transactions costs (costs of
gathering information and effecting
exchanges of goods and services).
(3) There are external benefits
resulting from improved energy
efficiency of fluorescent lamp ballasts
that are not captured by the users of
such equipment. These benefits include
externalities related to environmental
protection and energy security that are
not reflected in energy prices, such as
reduced emissions of greenhouse gases.
In addition, DOE has determined that
today’s regulatory action is an
‘‘economically significant regulatory
action’’ under section 3(f)(1) of
Executive Order 12866. Accordingly,
section 6(a)(3) of the Executive Order
requires that DOE prepare a regulatory
impact analysis (RIA) on today’s rule
and that the Office of Information and
Regulatory Affairs (OIRA) in the OMB
review this rule. DOE presented to OIRA
for review the draft rule and other
documents prepared for this
rulemaking, including the RIA, and has
included these documents in the
rulemaking record. The assessments
prepared pursuant to Executive Order
12866 can be found in the technical
support document for this rulemaking.
DOE has also reviewed this regulation
pursuant to Executive Order 13563,
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issued on January 18, 2011 (76 FR 3281,
Jan. 21, 2011). EO 13563 is
supplemental to and explicitly reaffirms
the principles, structures, and
definitions governing regulatory review
established in Executive Order 12866.
To the extent permitted by law, agencies
are required by Executive Order 13563
to: (1) Propose or adopt a regulation
only upon a reasoned determination
that its benefits justify its costs
(recognizing that some benefits and
costs are difficult to quantify); (2) tailor
regulations to impose the least burden
on society, consistent with obtaining
regulatory objectives, taking into
account, among other things, and to the
extent practicable, the costs of
cumulative regulations; (3) select, in
choosing among alternative regulatory
approaches, those approaches that
maximize net benefits (including
potential economic, environmental,
public health and safety, and other
advantages; distributive impacts; and
equity); (4) to the extent feasible, specify
performance objectives, rather than
specifying the behavior or manner of
compliance that regulated entities must
adopt; and (5) identify and assess
available alternatives to direct
regulation, including providing
economic incentives to encourage the
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desired behavior, such as user fees or
marketable permits, or providing
information upon which choices can be
made by the public.
DOE emphasizes as well that
Executive Order 13563 requires agencies
‘‘to use the best available techniques to
quantify anticipated present and future
benefits and costs as accurately as
possible.’’ In its guidance, the Office of
Information and Regulatory Affairs has
emphasized that such techniques may
include ‘‘identifying changing future
compliance costs that might result from
technological innovation or anticipated
behavioral changes.’’ For the reasons
stated in the preamble, DOE finds that
today’s final rule is consistent with
these principles, including the
requirement that, to the extent
permitted by law, agencies adopt a
regulation only upon a reasoned
determination that its benefits justify its
costs and select, in choosing among
alternative regulatory approaches, those
approaches that maximize net benefits.
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B. Review Under the Regulatory
Flexibility Act
The Regulatory Flexibility Act (5
U.S.C. 601 et seq.) requires preparation
of an initial regulatory flexibility
analysis (IRFA) for any rule that by law
must be proposed for public comment,
and a final regulatory flexibility analysis
(FRFA) for any such rule that an agency
adopts as a final rule, unless the agency
certifies that the rule, if promulgated,
will not have a significant economic
impact on a substantial number of small
entities. As required by Executive Order
13272, ‘‘Proper Consideration of Small
Entities in Agency Rulemaking,’’ 67 FR
53461 (August 16, 2002), DOE
published procedures and policies on
February 19, 2003, to ensure that the
potential impacts of its rules on small
entities are properly considered during
the rulemaking process. 68 FR 7990.
DOE has made its procedures and
policies available on the Office of the
General Counsel’s Web site (https://
www.gc.doe.gov). DOE reviewed the
April 2011 NOPR and today’s final rule
under the provisions of the Regulatory
Flexibility Act and the procedures and
policies published on February 19,
2003.
As presented and discussed in the
following sections, the FRFA describes
potential impacts on small
manufacturers associated with the
required product and capital conversion
costs at each TSL and discusses
alternatives that could minimize these
impacts. Chapter 13 of the TSD contains
more information about the impact of
this rulemaking on manufacturers.
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1. Statement of the Need for, and
Objectives of, the Rule
The reasons why DOE is establishing
the standards in today’s final rule and
the objectives of these standards are
provided elsewhere in the preamble and
not repeated here.
2. Summary of and Responses to the
Significant Issues Raised by the Public
Comments, and a Statement of Any
Changes Made as a Result of Such
Comments
This FRFA incorporates the IRFA and
public comments received on the IRFA
and the economic impacts of the rule.
DOE provides responses to these
comments in the discussion below on
the compliance impacts of the rule and
elsewhere in the preamble. DOE
modified the standards adopted in
today’s final rule in response to
comments received, including those
from small businesses, as described in
the preamble.
3. Description and Estimated Number of
Small Entities Regulated
a. Methodology for Estimating the
Number of Small Entities
For manufacturers of fluorescent lamp
ballasts, the Small Business
Administration (SBA) has set a size
threshold, which defines those entities
classified as ‘‘small businesses’’ for the
purposes of the statute. DOE used the
SBA’s small business size standards to
determine whether any small entities
would be subject to the requirements of
the rule. 65 FR 30836, 30848 (May 15,
2000), as amended at 65 FR 53533,
53544 (Sept. 5, 2000) and codified at
13 CFR part 121. The size standards are
listed by NAICS code and industry
description and are available at https://
www.sba.gov/idc/groups/public/
documents/sba_homepage/serv_sstd_
tablepdf.pdf. Fluorescent lamp ballast
manufacturing is classified under
NAICS 335311, ‘‘Power, Distribution
and Specialty Transformer
Manufacturing.’’ The SBA sets a
threshold of 750 employees or less for
an entity to be considered as a small
business for this category.
In the April 2011 NOPR, DOE
identified approximately 10 small
businesses that produce covered
products and can be considered small
business manufacturers. 76 FR 20090,
20171 (April 11, 2011). Radionic
disagreed with this estimate, stating that
they are the only domestic ballast
manufacturer, and noted that they were
not contacted by DOE. (Radionic, No. 36
at p. 1) During its analysis for the NOPR,
DOE identified Radionic as a small
business manufacturer that could
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potentially be affected by new or
amended standards. Radionic was
included in DOE’s estimate of ten small
manufacturers, which also includes U.S.
manufacturers with foreign production.
DOE contacted Radionic and received a
survey response during the NOPR
analysis period. Two other small
businesses consented to being
interviewed during the MIA interviews.
DOE also obtained information about
small business impacts while
interviewing large manufacturers.
b. Fluorescent Lamp Ballast Industry
Structure
Four major manufacturers with nondomestic production supply the vast
majority of the marketplace. None of the
four major manufacturers is considered
a small business. The remaining market
share is held by foreign manufacturers
and several smaller domestic companies
with very small market shares. Even for
these U.S.-operated firms, most
production is outsourced to overseas
vendors or captive overseas
manufacturing facilities. Some very
limited production takes place in the
United States—mostly magnetic ballasts
for specialty applications. DOE is
unaware of any fluorescent lamp ballast
companies, small or large, that produce
only domestically. See chapter 3 of the
final rule TSD for further details on the
fluorescent lamp ballast market.
c. Comparison Between Large and Small
Entities
The four large manufacturers typically
offer a much wider range of designs of
covered ballasts than small
manufacturers. Ballasts can be designed,
or optimized, to operate different lamp
lengths and numbers of lamps under
various start methods, often in
combination with various additional
features. Large manufacturers typically
offer many SKUs per product line to
meet this wide range of potential
specifications. Generally, one product
family shares some fundamental
characteristic (i.e., lamp diameter,
number of lamps, etc.) and hosts a large
number of SKUs that are manufactured
with minor variations on the same
product line. Some product lines, such
as the 4-foot MBP IS ballast, are
manufactured in high volumes, while
other products may be produced in
much lower volumes but can help
manufacturers meet their customers’
specific needs and provide higher
margin opportunities. For their part,
small manufacturers generally do not
have the volume to support as wide a
range of products.
Beyond variations in ballast types and
features, the large manufacturers also
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offer multiple tiers of efficiency,
typically including a baseline efficiency
product and a high-efficiency product
within the same family. On the other
hand, some small manufacturers
frequently only offer one efficiency level
in a given product class to reduce the
number of SKUs and parts they must
maintain. This strategy is important to
small-scale manufacturers because
many product development costs (e.g.,
testing, certification, and marketing) are
relatively fixed per product line.
Small manufacturers are able to
compete in the fluorescent lamp ballast
industry despite the dominance of the
four major manufacturers due, in large
part, to the fragmented nature of the
fixture industry. The largest four fixture
manufacturers comprise about 60
percent of the industry, while as many
as 200 smaller fixture manufacturers
have the remaining share. Many small
ballast manufacturers have developed
relationships with these small fixture
manufacturers, whose production
volumes may not be attractive to the
larger players. The same structure
applies to the electrical distributor
market—while small ballast
manufacturers often cannot compete for
the business of the largest distributors,
they are able to successfully target small
distributors, often on a regional basis.
Lastly, like the major manufacturers,
small manufacturers usually offer
products in addition to those
fluorescent lamp ballasts covered by
this rulemaking, such as dimming
ballasts, LED drivers, and compact
fluorescent ballasts.
4. Description and Estimate of
Compliance Requirements
Several manufacturers commented on
the potential impacts of energy
conservation standards on small
fluorescent lamp ballast manufacturers.
Radionic noted that small
manufacturers would be burdened
because they have fewer engineering
resources and less capital to deploy
toward redesign and UL testing
compared to large manufacturers and
suggested that consideration for
exemption be given to small
manufacturers. (Radionic, No. 36 at p. 1)
In contrast, Lutron stated that they
believe that the impacts of new and
amended standards for fluorescent lamp
ballasts would be negligible for small
manufacturers because small
manufacturers would concentrate in
areas such as emerging technologies—
where there is potential for growth and
high margins—rather than try to
compete with large manufacturers in a
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high-volume, traditional ballast market.
(Lutron, Public Meeting Transcript, No.
43 at p. 207) Philips agreed that small
manufacturers do not have a significant
presence in the traditional ballast
market. Philips noted, however, that
many sign ballast manufacturers, who
are also small manufacturers, may be
adversely affected by the switch from
magnetic to electronic sign ballasts
driven by proposed standards, which
may force sign ballast manufacturers to
source their ballasts. (Philips, Public
Meeting Transcript, No. 43 at pp. 208–
9)
Small manufacturers have the
potential to be significantly affected by
this rule for the reasons suggested by
Radionic. Most small ballast
manufacturers, however, would be able
to remain viable by focusing on niche
markets or emerging technologies. DOE
details its conclusions on the impacts
on and expected responses of small
manufacturers below.
Additionally, because sign ballast
manufacturers may be differentially
impacted by today’s standards, DOE
analyzed sign ballasts as a manufacturer
subgroup in section VII.B.2.d. DOE
made several attempts to contact sign
ballast manufacturers for interviews but
was unable to speak directly to any of
the manufacturers who specialize in
sign ballasts. As such, DOE’s subgroup
analysis was developed based on
information obtained from interviews
with large manufacturers and from
manufacturer Web sites.
At TSL3A, the level adopted in
today’s final rule, DOE estimates capital
conversion costs of $0.3 million and
product conversion costs of $1.0 million
for a typical small manufacturer,
compared to capital and product
conversion costs of $6.3 million and
$9.7 million, respectively, for a typical
large manufacturer. These costs and
their impacts are described in detail in
the following sections.
a. Capital Conversion Costs
Those small manufacturers DOE
interviewed did not expect increased
capital conversion costs to be a major
concern because most of them source all
or the majority of their products from
Asia. Those that source their products
would likely not make the direct capital
investments themselves. Small
manufacturers experience the impact of
sourcing their products through a higher
cost of goods sold, and thus a lower
operating margin, as compared to large
manufacturers. The capital costs
estimated are largely associated with
those small manufacturers producing
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magnetic ballasts. DOE estimates capital
costs of approximately $0.3 million for
a typical small manufacturer at TSL 3A,
based on the cost of converting magnetic
production lines, such as sign ballasts,
to electronic production lines.
Another challenge facing the industry
is the component shortage discussed in
the section V.H.4.d. As with large
manufacturers, the component shortage
is a significant issue for small
manufacturers, but some small
manufacturers stated that the shortage
does not differentially impact them. At
times, they actually can obtain
components more easily than large
manufacturers. Because their volumes
are lower, they generally pay higher
prices for parts than their larger
competitors, which incentivizes
suppliers to fill small manufacturers’
orders relatively quickly. The lowervolume orders also allow small
manufacturers to piggyback off the
orders for certain components that are
used throughout the consumer
electronics industry.
b. Product Conversion Costs
While capital conversion costs were
not a large concern to the small
manufacturers DOE interviewed,
product conversion costs could
adversely impact small manufacturers at
TSL 3A, the level adopted in today’s
final rule. To estimate the differential
impacts of the adopted standard on
small manufacturers, DOE compared
their cost of compliance with that of the
major manufacturers. First, DOE
examined the number of basic models
and SKUs available from each
manufacturer to determine an estimate
for overall compliance costs. The
number of basic models and SKUs
attributed to each manufacturer is based
on information obtained during
manufacturer interviews and an
examination of the different models
advertised by each on company Web
sites. DOE assumed that the product
conversion costs required to redesign
basic models and test and certify all
SKUs to meet the standard levels
presented in today’s final rule would be
lower per model and per SKU for small
manufacturers, as detailed below. (A
full description of DOE’s methodology
for developing product conversion costs
is found in section V.H.1.a and in
chapter 13 of the final rule TSD.) Table
VIII.1 compares the estimated product
conversion costs of a typical small
manufacturer as a percentage of their
annual R&D expense to those of a
typical large manufacturer.
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TABLE VIII.1—COMPARISON OF A TYPICAL SMALL AND LARGE MANUFACTURER’S PRODUCT CONVERSION COSTS TO
ANNUAL R&D EXPENSE
Large manufacturer
Small manufacturer
Product conversion
costs for a typical
large manufacturer
(2010$ millions)
Product conversion
costs as a percentage of annual R&D
expense
Product Conversion
costs for a typical
small manufacturer
(2010$ millions)
Product Conversion
costs as a percentage of annual R&D
expense
$0.00
1.41
6.15
9.68
12.53
0
16
71
111
144
$0.00
0.14
0.63
0.99
1.28
0
38
163
257
333
Baseline ...........................................................................
TSL 1 ...............................................................................
TSL 2 ...............................................................................
TSL 3A .............................................................................
TSL 3B .............................................................................
Based on discussions with
manufacturers, DOE estimated that the
cost to fully redesign every ballast
model for large manufacturers is
approximately $120,000 per model and
the cost to test and certify every SKU is
approximately $20,000 per SKU. A
typical major manufacturer offers
approximately 80 basic covered models
and 300 SKUs. Based on DOE’s GRIM
analysis, a typical major manufacturer
has an annual R&D expense of $8.7
million. Because not all products would
need to be redesigned at TSL 3A, DOE
estimates $9.7 million in product
conversion costs for a typical major
manufacturer at TSL 3A (compared to
$15.6 million if all products had to be
fully redesigned), which represents 111
percent of its annual R&D expense. This
means that a typical major manufacturer
could redesign its products in just over
a year if it were to devote its entire R&D
budget for fluorescent lamp ballasts to
product redesign and could retain the
engineering resources.
DOE’s research indicated that a
typical small manufacturer offers
approximately 50 basic covered models
and 100 SKUs. However, based on
manufacturer interviews, DOE does not
believe that small manufacturers would
incur the same level of costs per model
and SKU as large manufacturers. Small
manufacturers would not be as likely to
redesign models in-house as large
manufacturers. Instead, they would
source and rebrand products from
overseas manufacturers who supply
their ballasts. As a result, DOE assumed
a lower R&D investment, in absolute
dollars, per model. Because their
products are effectively sourced, DOE
projects smaller manufacturers would
face a higher level of cost of goods sold
(i.e., a higher MPC). Therefore, in a
competitive environment, small
manufacturers would earn a lower
markup than their larger peers and
consequently operate at lower margins.
Small manufacturers would also have to
test and certify every SKU they offer,
but they would not conduct the same
extent of pilot runs and internal testing
as large manufacturers because less
production takes place in internal
factories. As such, DOE estimates that
small manufacturers’ testing and
certification costs are expected to be
$10,000 per SKU for UL and other
certifications. Thus, the product
conversion costs for a typical small
manufacturer could total $1.6 million.
Because not all products would need to
be fully redesigned at TSL 3A, however,
DOE estimates product conversion costs
of $1.0 million at TSL 3A. Based on
scaling GRIM results to an average
small-manufacturer market share of 1.0
percent, DOE assumed that a small
manufacturer has an annual R&D
expense of $0.4 million, so the
estimated product conversion costs at
TSL 3A would represent 257 percent of
its annual R&D expense. This means
that a typical small manufacturer could
redesign its products within the three
year compliance period if it were to
devote its entire R&D budget for
fluorescent lamp ballasts to product
redesign and could retain the
engineering resources.
c. Summary of Compliance Impacts
Although the conversion costs
required can be considered substantial
for all companies, the impacts could be
relatively greater for a typical small
manufacturer because of much lower
production volumes and the relatively
fixed nature of the R&D resources
required per model. Table VIII.2
compares the total conversion costs of a
typical small manufacturer as a
percentage of annual revenue and
earnings before interest and taxes (EBIT)
to those of a typical large manufacturer.
TABLE VIII.2—COMPARISON OF A TYPICAL SMALL AND LARGE MANUFACTURER’S TOTAL CONVERSION COSTS TO ANNUAL
REVENUE AND EBIT
Large Manufacturer
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Total conversion
costs for a typical
large mfr.
(2010$ millions)
Baseline ...
TSL 1 .......
TSL 2 .......
TSL 3A .....
TSL 3B .....
Total conversion
costs as a
percentage of
annual revenue
$0.00
3.99
10.68
16.02
19.14
As seen in Table VIII.2, the impacts
for a typical small manufacturer are
relatively greater than for a large
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Small Manufacturer
Total conversion
costs as a
percentage of
annual EBIT
0
2
5
7
8
Total conversion
costs for a typical
small mfr.
(2010$ millions)
0
21
55
82
99
$0.00
0.26
0.83
1.27
1.58
manufacturer at TSL 3A. Total
conversion costs represent 182 percent
of annual EBIT for a typical small
PO 00000
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Fmt 4701
Sfmt 4700
Total conversion
costs as a
percentage of
annual revenue
0
2
8
12
15
Total conversion
costs as a
percentage of
annual EBIT
0
37
119
182
226
manufacturer compared to 82 percent of
annual EBIT for a typical large
manufacturer. DOE believes these
E:\FR\FM\14NOR2.SGM
14NOR2
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estimates reflect a worst-case scenario
because they assume small
manufacturers would redesign all
proprietary models immediately, and
not take advantage of the industry’s
supply chain dynamics or take other
steps to mitigate the impacts. DOE
anticipates, however, that small
manufacturers would take several steps
to mitigate the costs required to meet
new and amended energy conservation
standards.
At TSL 3A, it is more likely that
ballast manufacturers would
temporarily reduce the number of SKUs
they offer as in-house designs to keep
their product conversion costs at
manageable levels in the years
preceding the compliance date. As
noted previously, the typical small
manufacturer business model is not
predicated on the supply of a wide
range of models and specifications.
Small manufacturers frequently either
focus on a few niche markets or on
customers seeking only basic, low-cost
solutions. They therefore can satisfy the
needs of their customers with a smaller
product portfolio than large
manufacturers who often compete on
brand reputation and the ability to offer
a full product offering. As such, DOE
believes that under the adopted
standards small businesses would likely
selectively upgrade existing product
lines to offer products that are in high
demand or offer strategic advantage.
Small manufacturers could then spread
out further investments over a longer
time period by upgrading some product
lines prior to the compliance date while
sourcing others until resources allow—
and the market supports—in-house
design. Furthermore, while the initial
redesign costs are relatively large, the
estimates assume small manufacturers
would bring compliant ballasts to
market in concert with large
manufacturers. There is a possibility
some small manufacturers would
conserve resources by waiting to
upgrade certain products until new
compliant baseline designs become
available or their in-house development
is less resource-intensive. The
commonality of many consumer
electronics components, designs, and
products fosters considerable sharing of
experience throughout the electronics
supply chain, particularly when
unrestricted by proprietary
technologies. DOE did not find any
intellectual property restrictions that
would prevent small manufacturers
from making the technologies necessary
to meet today’s adopted levels.
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5. Steps Taken to Minimize Impacts on
Small Entities and Reasons Why Other
Significant Alternatives to Today’s Final
Rule Were Rejected
DOE modified the standards
established in today’s final rule from
those proposed in the April 2011 NOPR
as discussed previously and based on
comments and additional test data
received from interested parties. These
modifications include a separate
product class for residential ballasts,
which establishes less stringent
standards for these ballasts than the
NOPR, and new standard equations for
all product classes.
The previous discussion also analyzes
impacts on small businesses that would
result from the other TSLs DOE
considered. Though TSLs lower than
the adopted TSL are expected to reduce
the impacts on small entities, DOE is
required by EPCA to establish standards
that achieve the maximum improvement
in energy efficiency that are technically
feasible and economically justified, and
result in a significant conservation of
energy. Thus DOE rejected the lower
TSLs.
In addition to the other TSLs being
considered, the TSD includes a
regulatory impact analysis in chapter
18. For fluorescent lamp ballasts, this
report discusses the following policy
alternatives: (1) No standard, (2)
consumer rebates, (3) consumer tax
credits, (4) manufacturer tax credits, and
(5) early replacement. DOE does not
intend to consider these alternatives
further because they are either not
feasible to implement, or not expected
to result in energy savings as large as
those that would be achieved by the
standard levels under consideration.
Thus, DOE rejected these alternatives
and is adopting the standards set forth
in this rulemaking.
DOE notes that small manufacturers,
particularly those small sign ballast
manufacturers who would be required
to move from magnetic to electronic
sign ballasts as a result of today’s
standards, may apply to DOE for an
exemption from the standard pursuant
to 42 U.S.C. 6295(t). The process
applicants must follow to request an
exemption and DOE’s process for
making a decision on a particular
request are set forth in DOE’s
regulations at 10 CFR 430 Subpart E.
C. Review Under the Paperwork
Reduction Act
Manufacturers of fluorescent lamp
ballasts must certify to DOE that their
products comply with any applicable
energy conservation standards. In
certifying compliance, manufacturers
PO 00000
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Fmt 4701
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must test their products according to the
DOE test procedures for fluorescent
lamp ballasts, 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
fluorescent lamp ballasts. (76 FR 12422
(March 7, 2011). The collection-ofinformation 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 20 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
DOE prepared an EA of the impacts of
the new and amended rule pursuant to
the National Environmental Policy Act
of 1969 (42 U.S.C. 4321 et seq.), the
regulations of the Council on
Environmental Quality (40 CFR parts
1500–1508), and DOE’s regulations for
compliance with the National
Environmental Policy Act of 1969 (10
CFR part 1021). This assessment
includes an examination of the potential
effects of emission reductions likely to
result from the rule in the context of
global climate change, as well as other
types of environmental impacts. The EA
has been incorporated into the final rule
TSD as chapter 16. Before issuing this
final rule for fluorescent lamp ballasts,
DOE considered public comments and
issued a FONSI as part of a final EA.
E. Review Under Executive Order 13132
Executive Order 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 would limit
the policymaking discretion of the
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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. EPCA
governs and prescribes Federal
preemption of State regulations as to
energy conservation for the products
that are the subject of today’s final rule.
States can petition DOE for exemption
from such preemption to the extent, and
based on criteria, set forth in EPCA. (42
U.S.C. 6297) No further action is
required by Executive Order 13132.
F. Review Under Executive Order 12988
With respect to the review of existing
regulations and the promulgation of
new regulations, section 3(a) of
Executive Order 12988, ‘‘Civil Justice
Reform,’’ imposes on Federal agencies
the general duty to adhere to the
following requirements: (1) Eliminate
drafting errors and ambiguity; (2) write
regulations to minimize litigation; and
(3) provide a clear legal standard for
affected conduct rather than a general
standard and promote simplification
and burden reduction. 61 FR 4729 (Feb.
7, 1996). Section 3(b) of Executive Order
12988 specifically requires that
Executive agencies make every
reasonable effort to ensure that the
regulation: (1) Clearly specifies the
preemptive effect, if any; (2) clearly
specifies any effect on existing Federal
law or regulation; (3) provides a clear
legal standard for affected conduct
while promoting simplification and
burden reduction; (4) specifies the
retroactive effect, if any; (5) adequately
defines key terms; and (6) addresses
other important issues affecting clarity
and general draftsmanship under any
guidelines issued by the Attorney
General. Section 3(c) of Executive Order
12988 requires Executive agencies to
review regulations in light of applicable
standards in section 3(a) and section
3(b) to determine whether they are met
or it is unreasonable to meet one or
more of them. DOE has completed the
required review and determined that, to
the extent permitted by law, this final
rule meets the relevant standards of
Executive Order 12988.
G. Review Under the Unfunded
Mandates Reform Act of 1995
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA) requires
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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
new or amended 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 small governments. On March 18,
1997, DOE published a statement of
policy on its process for
intergovernmental consultation under
UMRA. 62 FR 12820. DOE’s policy
statement is also available at https://
www.gc.doe.gov.
DOE has concluded that this final rule
would likely require expenditures of
$100 million or more on the private
sector. Such expenditures may include:
(1) Investment in research and
development and in capital
expenditures by fluorescent lamp
ballasts 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 fluorescent lamp
ballasts, starting at the compliance date
for the applicable standard.
Section 202 of UMRA authorizes a
Federal agency to respond to the content
requirements of UMRA in any other
statement or analysis that accompanies
the final rule. 2 U.S.C. 1532(c). The
content requirements of section 202(b)
of UMRA relevant to a private sector
mandate substantially overlap the
economic analysis requirements that
apply under section 325(o) of EPCA and
Executive Order 12866. The
SUPPLEMENTARY INFORMATION section of
the notice of final rulemaking and the
‘‘Regulatory Impact Analysis’’ section of
the TSD for this final rule respond to
those requirements.
Under section 205 of UMRA, DOE is
obligated to identify and consider a
reasonable number of regulatory
alternatives before promulgating a rule
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Fmt 4701
Sfmt 4700
70627
for which a written statement under
section 202 is required. 2 U.S.C. 1535(a).
DOE is required to select from those
alternatives the most cost-effective and
least burdensome alternative that
achieves the objectives of the rule
unless DOE publishes an explanation
for doing otherwise, or the selection of
such an alternative is inconsistent with
law. As required by 42 U.S.C. 6295(g),
today’s final rule would establish energy
conservation standards for fluorescent
lamp ballasts that are designed to
achieve the maximum improvement in
energy efficiency that DOE has
determined to be both technologically
feasible and economically justified. A
full discussion of the alternatives
considered by DOE is presented in the
‘‘Regulatory Impact Analysis’’ section of
the TSD for today’s 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
DOE has determined, under Executive
Order 12630, ‘‘Governmental Actions
and Interference with Constitutionally
Protected Property Rights’’ 53 FR 8859
(March 18, 1988), that this regulation
would not result in any takings that
might require compensation under the
Fifth Amendment to the U.S.
Constitution.
J. Review Under the Treasury and
General Government Appropriations
Act, 2001
Section 515 of the Treasury and
General Government Appropriations
Act, 2001 (44 U.S.C. 3516, note)
provides for Federal agencies to review
most disseminations of information to
the public under guidelines established
by each agency pursuant to general
guidelines issued by OMB. OMB’s
guidelines were published at 67 FR
8452 (Feb. 22, 2002), and DOE’s
guidelines were published at 67 FR
62446 (Oct. 7, 2002). DOE has reviewed
today’s 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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Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
K. Review Under Executive Order 13211
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ 66 FR 28355 (May
22, 2001), requires Federal agencies to
prepare and submit to OIRA at OMB, a
Statement of Energy Effects for any
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 today’s
regulatory action, which sets forth
energy conservation standards for
fluorescent lamp ballasts, is not a
significant energy action because the
new and amended standards are not
likely to have a significant adverse effect
on the supply, distribution, or use of
energy, nor has it been designated as
such by the Administrator at OIRA.
Accordingly, DOE has not prepared a
Statement of Energy Effects on the final
rule.
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L. Review Under the Information
Quality Bulletin for Peer Review
On December 16, 2004, OMB, in
consultation with the Office of Science
and Technology Policy, 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 2667.
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In response to OMB’s Bulletin, DOE
conducted formal in-progress peer
reviews of the energy conservation
standards development process and
analyses and has prepared a Peer
Review Report pertaining to the energy
conservation standards rulemaking
analyses. Generation of this report
involved a rigorous, formal, and
documented evaluation using objective
criteria and qualified and independent
reviewers to make a judgment as to the
technical/scientific/business merit, the
actual or anticipated results, and the
productivity and management
effectiveness of programs and/or
projects. The ‘‘Energy Conservation
Standards Rulemaking Peer Review
Report’’ dated February 2007 has been
disseminated and is available at the
following Web site: https://
www1.eere.energy.gov/buildings/
appliance_standards/peer_review.html.
§ 430.2
M. Congressional Notification
As required by 5 U.S.C. 801, DOE will
report to Congress on the promulgation
of this rule prior to its effective date.
The report will state that it has been
determined that the rule is a ‘‘major
rule’’ as defined by 5 U.S.C. 804(2).
■
IX. Approval of the Office of the
Secretary
The Secretary of Energy has approved
publication of today’s final rule.
Comply with Appendix Q1 beginning
November 14, 2014. Prior to this date, all
fluorescent lamp ballasts shall be tested
using the provisions of Appendix Q.
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.
■
■
Issued in Washington, DC, on October 20,
2011.
Henry Kelly,
Acting Assistant Secretary of Energy, Energy
Efficiency and Renewable 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, to read
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 430.2 is amended by adding
the definition of ‘‘ballast luminous
efficiency’’ in alphabetical order to read
as follows:
■
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Fmt 4701
Sfmt 4700
Definitions.
*
*
*
*
*
Ballast luminous efficiency means the
total fluorescent lamp arc power
divided by the fluorescent lamp ballast
input power multiplied by the
appropriate frequency adjustment
factor, as defined in Appendix Q1 of
subpart B of this part.
*
*
*
*
*
■ 3. Appendix Q to subpart B of part
430 is amended by adding introductory
text after the heading to read as follows:
Appendix Q to Subpart B of Part 430—
Uniform Test Method for Measuring the
Energy Consumption of Fluorescent
Lamp Ballasts
Comply with Appendix Q until November
14, 2014. After this date, all fluorescent lamp
ballasts shall be tested using the provisions
of Appendix Q1.
*
*
*
*
*
4. Appendix Q1 to subpart B of part
430 is amended by adding introductory
text after the heading to read as follows:
Appendix Q1 to Subpart B of Part 430—
Uniform Test Method for Measuring the
Energy Consumption of Fluorescent
Lamp Ballasts
*
*
*
*
*
5. Section 430.32 is amended by:
a. Revising paragraph (m)(1)
introductory text.
■ b. Adding paragraphs (m)(8), (m)(9),
and m(10).
The revision and additions read as
follows:
§ 430.32 Energy and water conservation
standards and their effective dates.
*
*
*
*
*
(m)(1) Fluorescent lamp ballasts
(other than specialty application
mercury vapor lamp ballasts). Except as
provided in paragraphs (m)(2), (m)(3),
(m)(4), (m)(5), (m)(6), (m)(7), (m)(8),
(m)(9), and (m)(10) of this section, each
fluorescent lamp ballast—
*
*
*
*
*
(8) Except as provided in paragraph
(m)(9) of this section, each fluorescent
lamp ballast—
(i) Manufactured on or after
November 14, 2014;
(ii) Designed—
(A) To operate at nominal input
voltages at or between 120 and 277
volts;
(B) To operate with an input current
frequency of 60 Hertz; and
(C) For use in connection with
fluorescent lamps (as defined in § 430.2)
E:\FR\FM\14NOR2.SGM
14NOR2
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 / Rules and Regulations
(iii) Shall have—
(A) A power factor of 0.9 or greater
except for those ballasts defined in
paragraph (m)(8)(iii)(B) of this section;
(B) A power factor of 0.5 or greater for
residential ballasts, which are defined
in (m)(8)(vi) of this section;
70629
(C) A ballast luminous efficiency not
less than the following:
BLE = A/(1+B*average total lamp arc power ∧ ¥C) Where A, B, and C are as follows:
Description
A
Instant start and rapid start ballasts (not classified as residential) that are designed to operate ...................................................................................................................................
4-foot medium bipin lamps.
2-foot U-shaped lamps.
8-foot slimline lamps.
Programmed start ballasts (not classified as residential) that are designed to operate ......
4-foot medium bipin lamps.
2-foot U-shaped lamps.
4-foot miniature bipin standard output lamps.
4-foot miniature bipin high output lamps.
Instant start and rapid start ballasts (not classified as sign ballasts) that are designed to
operate 8-foot high output lamps. ......................................................................................
Programmed start ballasts (not classified as sign ballasts) that are designed to operate 8foot high output lamps. ......................................................................................................
Sign ballasts that operate 8-foot high output lamps .............................................................
Instant start and rapid start residential ballasts that operate ................................................
4-foot medium bipin lamps.
2-foot U-shaped lamps.
8-foot slimline lamps.
Programmed start residential ballasts that are designed to operate ....................................
4-foot medium bipin lamps.
2-foot U-shaped lamps.
(iv) Instant start, rapid start, and
programmed start are defined in
Appendix Q1 of subpart B of this part.
Average total lamp arc power is as
defined and measured in accordance
with Appendix Q1 of subpart B of this
part.
(v) Sign ballasts have an Underwriters
Laboratories Inc. Type 2 rating and are
designed, labeled, and marketed for use
in outdoor signs.
(vi) Residential ballasts meet FCC
consumer limits as set forth in 47 CFR
part 18 and are designed and labeled for
use in residential applications.
(9) The standards described in
paragraph (m)(8) of this section do not
apply to:
(i) A ballast that is designed for
dimming to 50 percent or less of the
B
C
0.993
0.25
0.993
0.51
0.37
0.993
0.38
0.25
0.973
0.993
0.993
0.70
0.47
0.41
0.37
0.25
0.25
0.973
maximum output of the ballast except
for those specified in m(10); and
(ii) A low frequency ballast (as
defined in Appendix Q1 to subpart of
this part) that:
(A) Is designed to operate T8 diameter
lamps;
(B) Is designed, labeled, and marketed
for use in EMI-sensitive environments
only;
(C) Is shipped by the manufacturer in
packages containing 10 or fewer
ballasts; and
(iii) A programmed start ballast that
operates 4-foot medium bipin T8 lamps
and delivers on average less than 140
milliamperes to each lamp.
(10) Each fluorescent lamp ballast—
(i) Manufactured on or after
November 14, 2014;
(ii) Designed—
0.27
0.71
0.37
(A) To operate at nominal input
voltages of 120 or 277 volts;
(B) To operate with an input current
frequency of 60 Hertz; and
(C) For use in connection with
fluorescent lamps (as defined in
§ 430.2);
(D) For dimming to 50 percent or less
of the maximum output of the ballast
(iii) Shall have—
(A) A power factor of 0.9 or greater
except for those ballasts defined in
paragraph (m)(8)(iii)(B) of this section;
(B) A power factor of 0.5 or greater for
residential ballasts, which meet FCC
Part B consumer limits and are designed
and labeled for use only in residential
applications;
(C) A ballast luminous efficiency of
not less than the following:
Ballast luminous efficiency
Ballast input
voltage
Designed for the operation of
mstockstill on DSK4VPTVN1PROD with RULES2
One
Two
Two
Two
*
F34T12 lamp ............................................................................
F34T12 lamps ..........................................................................
F96T12/ES lamps ....................................................................
F96T12HO/ES lamps ...............................................................
*
*
*
Total nominal
lamp watts
120/277
120/277
120/277
120/277
Low frequency
ballasts
34
68
120
190
0.777
0.804
0.876
0.711
*
[FR Doc. 2011–28451 Filed 11–10–11; 8:45 am]
BILLING CODE 6450–01–P
VerDate Mar<15>2010
18:36 Nov 10, 2011
Jkt 226001
PO 00000
Frm 00083
Fmt 4701
Sfmt 9990
E:\FR\FM\14NOR2.SGM
14NOR2
High frequency
ballasts
0.778
0.805
0.884
0.713
Agencies
[Federal Register Volume 76, Number 219 (Monday, November 14, 2011)]
[Rules and Regulations]
[Pages 70548-70629]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-28451]
[[Page 70547]]
Vol. 76
Monday,
No. 219
November 14, 2011
Part II
Department of Energy
-----------------------------------------------------------------------
10 CFR Part 430
Energy Conservation Program: Energy Conservation Standards for
Fluorescent Lamp Ballasts; Final Rule
Federal Register / Vol. 76, No. 219 / Monday, November 14, 2011 /
Rules and Regulations
[[Page 70548]]
-----------------------------------------------------------------------
DEPARTMENT OF ENERGY
10 CFR Part 430
[Docket Number EE-2007-BT-STD-0016]
RIN 1904-AB50
Energy Conservation Program: Energy Conservation Standards for
Fluorescent Lamp Ballasts
AGENCY: Office of Energy Efficiency and Renewable Energy, Department of
Energy.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Energy Policy and Conservation Act of 1975 (EPCA), as
amended, prescribes energy conservation standards for various consumer
products and certain commercial and industrial equipment, including
fluorescent lamp ballasts. EPCA also requires the U.S. Department of
Energy (DOE) to determine whether any new or amended standards would be
technologically feasible and economically justified, and would save a
significant amount of energy. In this final rule, DOE adopts new and
amended federal energy conservation standards for fluorescent lamp
ballasts. It has determined that the new and 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 January 13, 2012. Compliance
with the new and amended standards established for fluorescent lamp
ballasts in today's final rule is required as of November 14, 2014.
ADDRESSES: The docket for this rulemaking is available for review at
https://www.regulations.gov, including Federal Register notices,
framework documents, public meeting attendee lists and transcripts,
comments, and other supporting documents/materials. All documents in
the docket are listed in the https://www.regulations.gov index. However,
not all documents listed in the index may be publicly available, such
as information that is exempt from public disclosure.
A link to the docket Web page can be found at: https://www1.eere.energy.gov/buildings/appliance_standards/residential/fluorescent_lamp_ballasts.html. The regulations.gov 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 Ms.
Brenda Edwards at (202) 586-2945 or by email:
Brenda.Edwards@ee.doe.gov.
FOR FURTHER INFORMATION CONTACT:
Dr. Tina Kaarsberg, U.S. Department of Energy, Office of Energy
Efficiency and Renewable Energy, Building Technologies Program, EE-2J,
1000 Independence Avenue SW., Washington, DC 20585-0121. Telephone:
(202) 287-1393. Email: Tina.Kaarsberg@ee.doe.gov.
Ms. Elizabeth Kohl, U.S. Department of Energy, Office of the General
Counsel, GC-71, 1000 Independence Avenue SW., Washington, DC 20585-
0121. Telephone: (202) 586-7796. Email: Elizabeth.Kohl@hq.doe.gov.
SUPPLEMENTARY INFORMATION:
I. Summary of the Final Rule
A. Benefits and Costs to Consumers
B. Impact on Manufacturers
C. National Benefits
D. Conclusion
II. Introduction
A. Authority
B. Background
1. Ballast Efficacy Factor Standards
2. History of Standards Rulemaking for Fluorescent Lamp Ballasts
III. Issues Affecting the Scope of This Rulemaking
A. Additional Fluorescent Lamp Ballasts for Which DOE Is
Adopting Standards
1. Scope of EPCA Requirement That DOE Consider Standards for
Additional Ballasts
2. Identification of the Additional Ballasts for Which DOE
Establishes Standards
3. Summary of Fluorescent Lamp Ballasts to Which DOE Extends
Coverage
B. Off Mode and Standby Mode Energy Consumption Standards
IV. General Discussion
A. Test Procedures
1. Background
2. Transfer Function
3. Reference Lamp
4. Total Lamp Arc Power
B. Technological Feasibility
1. General
2. Maximum Technologically Feasible Levels
C. Energy Savings
1. Determination of Savings
2. Significance of Savings
D. Economic Justification
1. Specific Criteria
2. Rebuttable Presumption
V. Methodology and Discussion
A. Product Classes
1. Residential Ballasts
2. Sign Ballasts
3. Starting Method
4. 8-Foot HO
5. Summary
B. Engineering Analysis
1. NOPR Approach
2. Available Test Data
3. NEMA-Provided and DOE BLE Data Comparison
4. Accounting for Variation and Compliance Certification
Requirements
5. Efficiency Levels
6. Representative Units
7. Scaling to Product Classes Not Analyzed
8. Manufacturer Selling Prices
9. Results
C. Markups To Determine Product Price
1. Distribution Channels
2. Estimation of Markups
3. Summary of Markups
D. Energy Use Analysis
E. Life-Cycle Cost and Payback Period Analyses
1. Product Cost
2. Installation Cost
3. Annual Energy Use
4. Energy Prices
5. Energy Price Projections
6. Replacement and Disposal Costs
7. Product Lifetime
8. Discount Rates
9. Compliance Date of Standards
10. Ballast Purchasing Events
F. National Impact Analysis-National Energy Savings and Net
Present Value Analysis
1. Shipments
2. Site-to-Source Energy Conversion
G. Consumer Sub-Group Analysis
H. Manufacturer Impact Analysis
1. Product and Capital Conversion Costs
2. Markup Scenarios
3. Other Key GRIM Inputs
4. Other Comments From Interested Parties
5. Manufacturer Interviews
6. Sub-Group Impact Analysis
I. Employment Impact Analysis
J. Utility Impact Analysis
K. Environmental Assessment
L. Monetizing Carbon Dioxide and Other Emissions Impacts
1. Social Cost of Carbon
2. Valuation of Other Emissions Reductions
VI. Other Issues for Discussion
A. Proposed Standard Levels in April 2011 NOPR
B. Universal Versus Dedicated Input Voltage
C. Implementation of Adopted Standard Levels
VII. Analytical Results and Conclusions
A. Trial Standard Levels
B. Economic Justification and Energy Savings
1. Economic Impacts on Individual Consumers
2. Economic Impacts on Manufacturers
3. National Impact Analysis
4. Impact on Utility or Performance of Products
5. Impact of Any Lessening of Competition
6. Need of the Nation To Conserve Energy
C. Conclusions
1. Trial Standard Level 3B
2. Trial Standard Level 3A
D. Backsliding
VIII. Procedural Issues and Regulatory Review
A. Review Under Executive Orders 12866 and 13563
B. Review Under the Regulatory Flexibility Act
1. Statement of the Need for, and Objectives of, the Rule
2. Summary of and Responses to the Significant Issues Raised by
the Public Comments, and a Statement of Any Changes Made as a Result
of Such Comments
[[Page 70549]]
3. Description and Estimated Number of Small Entities Regulated
4. Description and Estimate of Compliance Requirements
5. Steps Taken To Minimize Impacts on Small Entities and Reasons
Why Other Significant Alternatives to Today's Final Rule Were
Rejected.
C. Review Under the Paperwork Reduction Act
D. Review Under the National Environmental Policy Act of 1969
E. Review Under Executive Order 13132
F. Review Under Executive Order 12988
G. Review Under the Unfunded Mandates Reform Act of 1995
H. Review Under the Treasury and General Government
Appropriations Act, 1999
I. Review Under Executive Order 12630
J. Review Under the Treasury and General Government
Appropriations Act, 2001
K. Review Under Executive Order 13211
L. Review Under the Information Quality Bulletin for Peer Review
M. Congressional Notification
IX. Approval of the Office of the Secretary
I. Summary of the Final Rule
Title III, Part B\1\ of the Energy Policy and Conservation Act of
1975 (EPCA or the Act), Public Law 94-163 (42 U.S.C. 6291-6309, as
codified), established the Energy Conservation Program for Consumer
Products Other Than Automobiles. Pursuant to EPCA, any new or amended
energy conservation standard that DOE prescribes for certain products,
such as fluorescent lamp ballasts (ballasts), shall be designed to
achieve the maximum improvement in energy efficiency that is
technologically feasible and economically justified. (42 U.S.C.
6295(o)(2)(A)) Furthermore, the new or amended standard must result in
a significant conservation of energy. (42 U.S.C. 6295(o)(3)(B)) In
accordance with these and other statutory provisions discussed in this
notice, DOE adopts new and amended energy conservation standards for
ballasts. The new and amended standards, which are based on ballast
luminous efficiency (BLE), the ratio of total lamp arc power to ballast
input power as defined in Appendix Q1 of title 10 of the Code of
Federal Regulations (CFR), part 430, are shown in Table I.1. These new
and amended standards apply to all products listed in Table I.1 and
manufactured in, or imported into, the United States on or after the
compliance date specified in the DATES section.
---------------------------------------------------------------------------
\1\ For editorial reasons, upon codification in the U.S. Code,
Part B was redesignated Part A.
Table I.1--New and Amended Energy Conservation Standards for Fluorescent Lamp Ballasts
----------------------------------------------------------------------------------------------------------------
Fluorescent lamp ballasts * shall have a ballast luminous efficiency no less than A/(1 + B * Percent
total lamp arc power[caret]-C) where A, B, and C are as follow: improvement
------------------------------------------------------------------------------------------------ over current
standard or
Product Class A B C baseline **
----------------------------------------------------------------------------------------------------------------
Instant start and rapid start ballasts (not 0.993 0.27 0.25 5.7
classified as residential) that are
designed to operate........................
4-foot medium bipin lamps
2-foot U-shaped lamps
8-foot slimline lamps
Programmed start ballasts (not classified as 0.993 0.51 0.37 10.8
residential) that are designed to operate..
4-foot medium bipin lamps
2-foot U-shaped lamps
4-foot miniature bipin standard output
lamps
4-foot miniature bipin high output lamps
Instant start and rapid start ballasts (not 0.993 0.38 0.25 26.5
classified as sign ballasts) that are
designed to operate 8-foot high output
lamps......................................
Programmed start ballasts (not classified as 0.973 0.70 0.37 26.2
sign ballasts) that are designed to operate
8-foot high output lamps...................
Sign ballasts that operate 8-foot high 0.993 0.47 0.25 15.1
output lamps...............................
Instant start and rapid start residential 0.993 0.41 0.25 7.2
ballasts that operate......................
4-foot medium bipin lamps
2-foot U-shaped lamps
8-foot slimline lamps
Programmed start residential ballasts that 0.973 0.71 0.37 5.8
are designed to operate....................
4-foot medium bipin lamps
2-foot U-shaped lamps
----------------------------------------------------------------------------------------------------------------
* Fluorescent ballasts that are exempt from these standards are listed in section III.A.3.
** Percent improvement is applicable to the average of ballasts directly analyzed.
A. Benefits and Costs to Consumers
Table I.2 presents DOE's evaluation of the economic impacts of
today's standards on consumers of ballasts for the product classes
analyzed as representative (see section V.B.6), as measured by the
average life-cycle cost (LCC) savings and the median payback period
(PBP). The average LCC savings are positive for all product classes.
For example, the estimated average LCC savings are $37-$40 for 2-lamp
instant start (IS) and rapid start (RS) ballasts that operate 4-foot T8
\2\ lamps in the commercial sector. When there was more than one
baseline for a representative ballast type, DOE performed separate LCC
analyses comparing replacement lamp-and-ballast systems to each
baseline. Because T8 systems are generally more efficient and have
lower overall LCCs than T12 systems, the LCC savings relative to the T8
baseline are lower than when comparing the same efficiency levels to a
T12 baseline. At the adopted standard levels, however, LCC savings are
positive for all replacement events and baselines analyzed.
---------------------------------------------------------------------------
\2\ A lamp description in the form ``T8'' refers to a lamp that
(1) is tubular (linear) and (2) has a diameter of 8 eighths of an
inch (1 inch).
[[Page 70550]]
Table I.2--Impacts of Today's Standards on Consumers of Ballasts
----------------------------------------------------------------------------------------------------------------
Product Class * Average LCC savings (2010$) Median payback period (years) *
----------------------------------------------------------------------------------------------------------------
IS and RS ballasts (not classified as
residential) that operate:
4-foot MBP lamps (T12 baseline)... $37 to $40......................... -1.2 to -1.3.
4-foot MBP lamps (T8 baseline).... $3 to $8........................... 2.7 to 4.4.
8-foot slimline lamps (T12 $22 to $33......................... 0.1.
baseline).
8-foot slimline lamps (T8 $5 to $7........................... 0.5 to 0.6.
baseline).
PS ballasts (not classified as
residential) that operate:
4-foot MBP lamps.................. $6 to $35.......................... 1.3 to 6.0.
4-foot MiniBP SO lamps............ $10 to $19......................... 2.4 to 3.8.
4-foot MiniBP HO lamps............ $26 to $28......................... 2.0 to 2.1.
IS and RS ballasts (not classified as
sign ballasts) that operate:
8-foot HO lamps (T12 baseline).... $134 to $230....................... -0.7 to -1.3.
Sign ballasts that operate:
8-foot HO lamps................... $251 to $403....................... -0.2 to -0.3.
IS and RS residential ballasts that
operate:
4-foot MBP lamps.................. $15 to $21......................... -5.5 to -9.5.
----------------------------------------------------------------------------------------------------------------
*IS = instant start; RS = rapid start; MBP = medium bipin; MiniBP = miniature bipin; PS = programmed start;
SO = standard output; HO = high output.
**Negative PBP values indicate standards that reduce operating costs and installed costs.
B. Impact on Manufacturers
The industry net present value (INPV) is the sum of the discounted
cash flows to the industry from the base year through the end of the
analysis period (2014 to 2043). Using a real discount rate of 7.4 \3\
percent, DOE estimates that the INPV for manufacturers of ballasts in
the base case ranges from $733 million to $1.22 billion in 2010 dollars
(2010$). Under today's standards, DOE expects that ballast
manufacturers may lose up to 36.7 percent of their INPV, which is
approximately $268.6 million. Based on DOE's interviews with the
manufacturers of ballasts, however, DOE does not expect any plant
closings or significant employment loss. See section VII.B.2.b and
VIII.B.3.b for additional discussion on this topic.
---------------------------------------------------------------------------
\3\ For ballasts, DOE uses a real discount rate of 7.4 percent.
DOE's discount rate estimate was derived from industry financials
then modified according to feedback during manufacturer interviews.
---------------------------------------------------------------------------
C. National Benefits
DOE's analyses indicate that today's ballast standards would save a
significant amount of energy over 30 years (2014-2043)--an estimated
2.7-5.6 quadrillion British thermal units (quads) of cumulative energy.
This amount is equivalent to the annual energy use of 14 million to 28
million U.S. homes.\4\
---------------------------------------------------------------------------
\4\ This estimate is based on the energy use of homes in 2008,
which is the most recent data available. See Rosenfeld, Arthur H.
and Satish Kumar. Tables to Convert Energy or CO2 (saved or used) to
Familiar Equivalents--Cars, Homes, or Power Plants (US Average Data
for 2005). May 2008. https://www.energy.ca.gov/commissioners/rosenfeld_docs/EquivalenceMatrix2008.doc
---------------------------------------------------------------------------
The cumulative national net present value (NPV) of total consumer
costs and savings of today's ballast standards in 2010$ ranges from
$6.7 billion (at a 7-percent discount rate) to $21.6 billion (at a 3-
percent discount rate). This NPV expresses the estimated total value of
future operating-cost savings less the estimated increased product
costs for products purchased in 2014-2043, discounted to 2011.
In addition, today's ballast standards would have significant
environmental benefits. The energy savings would result in cumulative
greenhouse gas emission reductions of 27-106 million metric tons (Mt)
of carbon dioxide (CO2) from 2014 through 2043. During this
period, the standards would also result in emissions reductions \5\ of
22-39 thousand tons of nitrogen oxides (NOX) and 0.40-1.47
tons of mercury (Hg).\6\
---------------------------------------------------------------------------
\5\ DOE calculates emissions reductions relative to the most
recent version of the Annual Energy Outlook (AEO) Reference case
forecast. As noted in TSD chapter 16, this forecast accounts for
regulatory emissions reductions through 2008, including the Clean
Air Interstate Rule (CAIR, 70 FR 25162 (May 12, 2005)), but not the
Clean Air Mercury Rule (CAMR, 70 FR 28606 (May 18, 2005)).
Subsequent regulations, including the currently proposed CAIR
replacement rule, the Clean Air Transport Rule (75 FR 45210 (Aug. 2,
2010)), do not appear in the forecast.
\6\ Results for NOX and Hg are presented in short
tons. One short ton equals 2000 lbs.
---------------------------------------------------------------------------
The value of the CO2 reductions is calculated using a
range of values per metric ton of CO2 (otherwise known as
the Social Cost of Carbon, or SCC) developed by a recent interagency
process. The derivation of the SCC values is discussed in section V.L.
DOE estimates that the net present monetary value of the CO2
emissions reductions is between $0.26 and $3.94 billion, expressed in
2010$ and discounted to 2011. DOE also estimates that the net present
monetary value of the NOX emissions reductions, expressed in
2010$ and discounted to 2011, is $3.91 to $40.2 million at a 7-percent
discount rate, and $7.67 to $78.8 million at a 3-percent discount
rate.\7\
---------------------------------------------------------------------------
\7\ DOE is aware of multiple agency efforts to determine the
appropriate range of values used in evaluating the potential
economic benefits of reduced Hg emissions. DOE has decided to await
further guidance regarding consistent valuation and reporting of Hg
emissions before it once again monetizes Hg emissions reductions in
its rulemakings.
---------------------------------------------------------------------------
Table I.3 summarizes the national economic costs and benefits
expected to result from today's standards for fluorescent lamp
ballasts.
[[Page 70551]]
Table I.3--Summary of National Economic Benefits and Costs of
Fluorescent Lamp Ballast Energy Conservation Standards
------------------------------------------------------------------------
Present value Discount rate
Category Billion 2010$ (percent)
------------------------------------------------------------------------
Benefits
------------------------------------------------------------------------
Operating Cost Savings.............. 12.0 7
24.1 3
CO2 Reduction Monetized Value (at 0.26 5
$4.9/t) *..........................
CO2 Reduction Monetized Value (at 1.29 3
$22.3/t) *.........................
CO2 Reduction Monetized Value (at 2.16 2.5
$36.5/t) *.........................
CO2 Reduction Monetized Value (at 3.94 3
$67.6/t) *.........................
NOX Reduction Monetized Value (at 0.004 7
$450/ton) *........................
0.01 3
NOX Reduction Monetized Value (at 0.04 7
$4,623/ton) *......................
0.08 3
Total Benefits[dagger].............. 13.3 7
25.4 3
------------------------------------------------------------------------
Costs
------------------------------------------------------------------------
Incremental Installed Costs......... 3.68 7
6.91 3
------------------------------------------------------------------------
Net Benefits
------------------------------------------------------------------------
Including CO2 and NOX[dagger]....... 9.62 7
18.5 3
------------------------------------------------------------------------
* The CO2 values represent global monetized values of the SCC in 2010
under several scenarios. The values of $4.9, $22.3, and $36.5 per
metric ton (t) are the averages of SCC distributions calculated using
5%, 3%, and 2.5% discount rates, respectively. The value of $67.6/t
represents the 95th percentile of the SCC distribution calculated
using a 3% discount rate.
[dagger] Total Benefits for both the 3% and 7% cases are derived using
the SCC value calculated at a 3% discount rate, and the average of the
low and high NOX values used in DOE's analysis.
The benefits and costs of today's standards, for products sold in
2014-2043, can also be expressed in terms of annualized values. The
annualized monetary values are the sum of (1) the annualized national
economic value, expressed in 2010$, of the benefits from operating the
product (consisting primarily of operating cost savings from using less
energy, minus increases in equipment purchase and installation costs,
which is another way of representing consumer NPV, plus (2) the
annualized monetary value of the benefits of emission reductions,
including CO2 emission reductions.\8\
---------------------------------------------------------------------------
\8\ DOE used a two-step calculation process to convert the time-
series of costs and benefits into annualized values. First, DOE
calculated a present value in 2011, the year used for discounting
the NPV of total consumer costs and savings, for the time-series of
costs and benefits using discount rates of three and seven percent
for all costs and benefits except for the value of CO2
reductions. For the latter, DOE used a range of discount rates, as
shown in Table I.3. From the present value, DOE then calculated the
fixed annual payment over a 30-year period (2014 through 2043) that
yields the same present value. This payment includes benefits to
consumers which accrue after 2043 from the ballasts purchased from
2014 to 2043. Costs incurred by manufacturers, some of which may be
incurred prior to 2014 in preparation for the rule, are not directly
included, but are indirectly included as part of incremental product
costs. The fixed annual payment is the annualized value. Although
DOE calculated annualized values, this does not imply that the time-
series of cost and benefits from which the annualized values were
determined is a steady stream of payments.
---------------------------------------------------------------------------
Although adding the value of consumer savings to the values of
emission reductions provides a valuable perspective, two issues should
be considered. First, the national operating cost savings are domestic
U.S. consumer monetary savings that occur as a result of market
transactions, while the value of CO2 emissions reductions is
based on a global value. Second, the assessments of operating cost
savings and CO2 savings are performed with different methods
that use different time frames for analysis. The national operating
cost savings are measured for the lifetime of ballasts shipped in 2014-
2043. The SCC values, alternatively, reflect the present value of all
future climate-related impacts resulting from the emission of one
metric ton of CO2 in each year, with impacts continuing well
beyond 2100.
Estimates of annualized benefits and costs of today's standards are
shown in Table I.4. (The following monetary values are expressed in
2010$.) The results under the primary estimate are as follows. Using a
7-percent discount rate for benefits and costs other than
CO2 reduction, for which DOE used a 3-percent discount rate
along with the SCC series corresponding to a value of $22.3/ton in
2010, the cost of the standards in today's rule is $363 million per
year in increased equipment costs, while the benefits are $1.2 billion
per year in reduced equipment operating costs, $92 million in
CO2 reductions, and $2.2 million in reduced NOX
emissions. In this case, the net benefit amounts to $920 million per
year. Using a 3-percent discount rate for all benefits and costs and
the SCC series corresponding to a value of $22.3/ton in 2010, the cost
of the standards in today's rule is $385 million per year in increased
equipment costs, while the benefits are $1.3 billion per year in
reduced operating costs, $92 million in CO2 reductions, and
$2.4 million in reduced NOX emissions. In this case, the net
benefit amounts to $1.1 billion per year.
[[Page 70552]]
Table I.4--Annualized Benefits and Costs of New and Amended Standards for Ballasts Sold in 2014-2043*
----------------------------------------------------------------------------------------------------------------
Monetized million 2010$/year
-----------------------------------------------------------
Low estimate High estimate
Discount rate (emerging (existing
Primary estimate technologies, roll- technologies,
up scenario) shift scenario)
----------------------------------------------------------------------------------------------------------------
Benefits
----------------------------------------------------------------------------------------------------------------
Operating Cost Savings.......... 7%................ 1,189............. 886............... 1,492.
3%................ 1,344............. 934............... 1,754.
CO2 Reduction at $4.9/t**....... 5%................ 20................ 9................. 30.
CO2 Reduction at $22.3/t**...... 3%................ 92................ 41................ 143.
CO2 Reduction at $36.5/t**...... 2.5%.............. 151............... 66................ 237.
CO2 Reduction at $67.6/t**...... 3%................ 280............... 124............... 435.
NOX Reduction at $2,537/t**..... 7%................ 2.2............... 1.3............... 3.0.
3%................ 2.4............... 1.6............... 3.2.
Total (Operating Cost Savings, 7% plus CO2 range. 1,211 to 1,471.... 896 to 1,011...... 1,525 to 1,930.
CO2 Reduction and NOX
Reduction)[dagger].
7%................ 1,283............. 928............... 1,637.
3%................ 1,438............. 976............... 1,900.
3% plus CO2 range. 1,366 to 1,626.... 945 to 1,059...... 1,788 to 2,193.
----------------------------------------------------------------------------------------------------------------
Costs
----------------------------------------------------------------------------------------------------------------
Incremental Product Costs....... 7%................ 363............... 227............... 498.
3%................ 385............... 218............... 553.
----------------------------------------------------------------------------------------------------------------
Net Benefits/Costs
----------------------------------------------------------------------------------------------------------------
Total (Operating Cost Savings, 7% plus CO2 range. 848 to 1,108...... 669 to 784........ 1,027 to 1,432.
CO2 Reduction and NOX
Reduction, Minus Incremental
Product Costs)[dagger].
7%................ 920............... 700............... 1,139.
3%................ 1,053............. 758............... 1,347.
3% plus CO2 range. 981 to 1,241...... 727 to 842........ 1,235 to 1,640.
----------------------------------------------------------------------------------------------------------------
* This table presents the annualized costs and benefits associated with fluorescent lamp ballasts shipped
between 2014 and 2043. These results include benefits to consumers which accrue after 2043 from the ballasts
purchased from 2014 to 2043. Costs incurred by manufacturers, some of which may be incurred prior to 2014 in
preparation for the rule, are not directly included, but are indirectly included as part of incremental
product costs. The Primary, Low Benefits, and High Benefits Estimates utilize forecasts of energy prices and
housing starts from the AEO2010 Reference case, with the Low and High Estimates based on forecasted ballast
shipments in the Emerging Technologies, Roll-up and Existing Technologies, Shift scenarios, respectively. In
addition, all estimates use incremental product costs that reflect constant prices (no learning rate) for
product prices. The different techniques used to evaluate projected price trends for each estimate are
discussed in section V.E.1.
** The CO2 values represent global monetized values (in 2010$) of the social cost of CO2 emissions in 2010 under
several scenarios. The values of $4.9, $22.3, and $36.5 per metric ton are the averages of SCC distributions
calculated using 5-percent, 3-percent, and 2.5-percent discount rates, respectively. The value of $67.6/t
represents the 95th percentile of the SCC distribution calculated using a 3-percent discount rate. The value
for NOX (in 2010$) is the average of the low and high values used in DOE's analysis.
[dagger] Total Benefits for both the 3-percent and 7-percent cases are derived using the SCC value calculated at
a 3-percent discount rate, which is $22.3/t in 2010 (in 2010$). In the rows labeled as ``7% plus CO2 range''
and ``3% plus CO2 range,'' the operating cost and NOX benefits are calculated using the labeled discount rate,
and those values are added to the full range of CO2 values.
D. Conclusion
Based on the analyses culminating in this final rule, DOE found the
benefits to the nation of the standards (energy savings, consumer LCC
savings, positive NPV of consumer benefit, and emission reductions)
outweigh the costs (loss of INPV). DOE has concluded that the standards
in today's final rule represent the maximum improvement in energy
efficiency that is technologically feasible and economically justified,
and would result in significant conservation of energy. DOE further
notes that in all product classes, ballasts achieving the standard
levels are already commercially available.
II. Introduction
The following section briefly discusses the statutory authority
underlying today's final rule, as well as some of the historical
background related to the establishment of standards for ballasts.
A. Authority
Title III, Part B of the Energy Policy and Conservation Act of
1975, Public Law 94-163 (42 U.S.C. 6291-6309, as codified) established
the Energy Conservation Program for Consumer Products Other Than
Automobiles,\9\ a program covering most major household appliances
(collectively referred to as ``covered products''), which includes the
types of ballasts that are the subject of this final rule. (42 U.S.C.
6292(a)(13)) EPCA prescribed energy conservation standards for these
products (42 U.S.C. 6295(g)(5), (6), and (8)), and directed DOE to
conduct two cycles of rulemakings to determine whether to amend these
standards. (42 U.S.C. 6295(g)(7))
---------------------------------------------------------------------------
\9\ For editorial reasons, upon codification in the U.S. Code
(U.S.C.), Part B was redesignated Part A.
---------------------------------------------------------------------------
Pursuant to EPCA, DOE's energy conservation program for covered
products consists essentially of four parts: (1) Testing; (2) labeling;
(3) the establishment of Federal energy conservation standards; and (4)
certification and enforcement procedures. The Federal Trade Commission
(FTC) is primarily responsible for labeling, and DOE
[[Page 70553]]
implements the remainder of the program. 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. 6293) 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. Id. The DOE test procedures for
ballasts currently appear at 10 CFR part 430, subpart B, appendices Q
and Q1. Compliance with the ballast efficacy factor energy conservation
standards, required until the compliance date specified in the DATES
section, is determined according to appendix Q. Compliance with the BLE
standards adopted in this rule must be determined according to appendix
Q1. The procedures in appendix Q1 were established by the ballast
active mode test procedure final rule. 76 FR 25211 (May 4, 2011).
DOE must follow specific statutory criteria for prescribing new or
amended standards for covered products. As indicated in the beginning
of section I, any new or amended standard for a covered product must be
designed to achieve the maximum improvement in energy efficiency that
is technologically feasible and economically justified. (42 U.S.C.
6295(o)(2)(A)) Furthermore, 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 ballasts, if no test procedure has been established
for the product, or (2) if DOE determines by rule that the new or
amended standard is not technologically feasible or economically
justified. (42 U.S.C. 6295(o)(3)(A)-(B)) In deciding whether a new or
amended standard is economically justified, DOE must determine whether
the benefits of the standard exceed its burdens. (42 U.S.C.
6295(o)(2)(B)(i)) DOE must make this determination after receiving
comments on the proposed standard, and by considering, to the greatest
extent practicable, the following seven factors:
1. The economic impact of the standard on manufacturers and
consumers of the products subject to the standard;
2. The savings in operating costs throughout the estimated average
life of the covered products in the type (or class) compared to any
increase in the price, initial charges, or maintenance expenses for the
covered products that are likely to result from the imposition of the
standard;
3. The total projected amount of energy, or as applicable, water,
savings likely to result directly from the imposition of the standard;
4. Any lessening of the utility or the performance of the covered
products likely to result from the imposition of the standard;
5. The impact of any lessening of competition, as determined in
writing by the Attorney General, that is likely to result from the
imposition of the standard;
6. The need for national energy and water conservation; and
7. Other factors the Secretary of Energy (the Secretary) considers
relevant.
(42 U.S.C. 6295(o)(2)(B)(i)(I)-(VII))
EPCA, as codified, also contains what is known as an ``anti-
backsliding'' provision, which prevents the Secretary from prescribing
any new or amended standard that either increases the maximum allowable
energy use or decreases the minimum required energy efficiency of a
covered product. (42 U.S.C. 6295(o)(1)) Also, the Secretary may not
prescribe a new or amended standard if interested parties 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))
Further, EPCA, as codified, establishes a rebuttable presumption
that a standard is economically justified if the Secretary finds that
the additional cost to the consumer of purchasing a product complying
with an energy conservation standard level will be less than three
times the value of the energy savings during the first year that the
consumer will receive as a result of the standard, as calculated under
the applicable test procedure. See 42 U.S.C. 6295(o)(2)(B)(iii).
Additionally, 42 U.S.C. 6295(q)(1) specifies requirements when
promulgating a standard for a type or class of covered product that has
two or more subcategories. DOE must specify a different standard level
than that which applies generally to such type or class of products for
any group of covered products which have the same function or intended
use if products within such group--(A) consume a different kind of
energy from that consumed by other covered products within such type
(or class); or (B) have a capacity or other performance-related feature
which other products within such type (or class) do not have and such
feature justifies a higher or lower standard. Id. In determining
whether a performance-related feature justifies a different standard
for a group of products, DOE must consider such factors as the utility
to the consumer of such a feature and other factors DOE deems
appropriate. Id. Any rule prescribing such a standard must include an
explanation of the basis on which such higher or lower level was
established. (42 U.S.C. 6295(q)(2))
Federal energy conservation requirements generally supersede State
laws or regulations concerning energy conservation testing, labeling,
and standards. (42 U.S.C. 6297(a)-(c)) DOE may, however, grant waivers
of Federal preemption for particular State laws or regulations, in
accordance with the procedures and other provisions set forth under 42
U.S.C. 6297(d).
Pursuant to the amendments contained in section 310(3) of the
Energy Independence and Security Act of 2007 (EISA 2007), 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 the 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)) DOE has determined
that ballasts do not operate in an ``off mode'' as defined by EPCA (42
U.S.C. 6291(gg)(1)(A)(ii)), and that the only ballasts that consume
power in a ``standby mode'' as defined by EPCA (42 U.S.C.
6291(gg)(1)(A)(iii)) are those that incorporate an electronic circuit
enabling the ballast to communicate with and be part of a lighting
control system. DOE's test procedures for ballasts address such standby
mode energy use. 74 FR 54455 (October 22, 2009) and 76 FR 25211 (May 4,
2011); 10 CFR part 430, subpart B, appendix Q, section 3.2 and appendix
Q1, section 3. DOE did not adopt standards for standby mode energy use,
however, because DOE did not find any covered ballasts capable of
operating in this
[[Page 70554]]
mode in its search of the marketplace. Therefore, this final rule does
not include energy conservation standards for standby mode energy use.
See section III.B for more detail.
DOE has also reviewed this regulation pursuant to Executive Order
13563, issued on January 18, 2011 (76 FR 3281, Jan. 21, 2011). EO 13563
is supplemental to and explicitly reaffirms the principles, structures,
and definitions governing regulatory review established in Executive
Order 12866. To the extent permitted by law, agencies are required by
Executive Order 13563 to: (1) Propose or adopt a regulation only upon a
reasoned determination that its benefits justify its costs (recognizing
that some benefits and costs are difficult to quantify); (2) tailor
regulations to impose the least burden on society, consistent with
obtaining regulatory objectives, taking into account, among other
things, and to the extent practicable, the costs of cumulative
regulations; (3) select, in choosing among alternative regulatory
approaches, those approaches that maximize net benefits (including
potential economic, environmental, public health and safety, and other
advantages; distributive impacts; and equity); (4) to the extent
feasible, specify performance objectives, rather than specifying the
behavior or manner of compliance that regulated entities must adopt;
and (5) identify and assess available alternatives to direct
regulation, including providing economic incentives to encourage the
desired behavior, such as user fees or marketable permits, or providing
information upon which choices can be made by the public.
DOE emphasizes as well that Executive Order 13563 requires agencies
``to use the best available techniques to quantify anticipated present
and future benefits and costs as accurately as possible.'' In its
guidance, the Office of Information and Regulatory Affairs has
emphasized that such techniques may include ``identifying changing
future compliance costs that might result from technological innovation
or anticipated behavioral changes.'' For the reasons stated in the
preamble, DOE concludes that today's final rule is consistent with
these principles, including the requirement that, to the extent
permitted by law, benefits justify costs and that net benefits are
maximized. Consistent with EO 13563, and the range of impacts analyzed
in this final rule, the energy efficiency standards adopted herein by
DOE achieve maximum net benefits.
B. Background
1. Ballast Efficacy Factor Standards
The Federal energy conservation standards for ballasts expressed in
terms of ballast efficacy factor are set forth in Table II.1 and Table
II.2. The standards in Table II.1 were adopted in a final rule
published on September 19, 2000, which completed the first of the two
rulemakings required under 42 U.S.C. 6295(g)(7) to consider amending
the standards for ballasts (hereafter referred to as the 2000 Ballast
Rule). 65 FR 56739. The standards in Table II.2 were established by
amendments to EPCA in the Energy Policy Act of 2005 (EPAct 2005), Pub.
L. 109-58.
Table II.1--Energy Conservation Standards From the 2000 Ballast Rule
----------------------------------------------------------------------------------------------------------------
Ballast input Total nominal Ballast efficacy
Application for operation of * voltage lamp watts factor
----------------------------------------------------------------------------------------------------------------
One F40T12 lamp........................................... 120 40 2.29
277 40 2.29
Two F40T12 lamps.......................................... 120 80 1.17
277 80 1.17
Two F96T12 lamps.......................................... 120 150 0.63
277 150 0.63
Two F96T12HO lamps........................................ 120 220 0.39
277 220 0.39
----------------------------------------------------------------------------------------------------------------
* F40T12, F96T12, and F96T12HO are defined in Appendix Q to Subpart B of Part 430.
10 CFR 430.32(m)(3).
Table II.2--Energy Conservation Standards From EPAct 2005
----------------------------------------------------------------------------------------------------------------
Ballast input Total nominal Ballast efficacy
Application for operation of * voltage lamp watts factor
----------------------------------------------------------------------------------------------------------------
One F34T12 lamp........................................... 120/277 34 2.61
Two F34T12 lamps.......................................... 120/277 68 1.35
Two F96T12/ES lamps....................................... 120/277 120 0.77
Two F96T12HO/ES lamps..................................... 120/277 190 0.42
----------------------------------------------------------------------------------------------------------------
* F34T12, F96T12/ES, and F96T12HO/ES are defined in Appendix Q to Subpart B of Part 430.
(42 U.S.C. 6295(g)(8)(A); 10 CFR 430.32(m)(5))
In summary, as reflected in the previous two tables, the ballasts
currently regulated under EPCA consist of ballasts that are designed to
operate:
One and two nominally 40-watt (W) and 34W 4-foot T12
medium bipin (MBP) lamps (F40T12 \10\ and F34T12);
---------------------------------------------------------------------------
\10\ A notation in the form ``F40T12'' identifies a lamp type.
This particular notation refers to a lamp that: (1) Is fluorescent;
(2) has a nominal wattage of 40 W; (3) is linear (tubular); and (4)
has a diameter of 12 eighths of an inch.
---------------------------------------------------------------------------
Two nominally 75W and 60W 8-foot T12 single-pin (SP)
slimline lamps (F96T12 and F96T12/ES); and
Two nominally 110W and 95W 8-foot T12 recessed double
contact high output lamps (F96T12HO and F96T12HO/ES) at nominal input
voltages of 120 or 277 volts (V) with an input current frequency of 60
hertz (Hz).
[[Page 70555]]
In addition, several ballasts are exempt from standards. These
exemptions consist of ballasts designed to operate those lamps listed
in Table II.1 that:
Are designed for dimming to 50 percent or less of its
maximum output;
Are designed for use with two F96T12 high output (HO)
lamps at ambient temperatures of -20 degrees Fahrenheit (F) or less and
for use in an outdoor sign; or
Have a power factor of less than 0.90 and are designed and
labeled for use only in residential building applications.
2. History of Standards Rulemaking for Fluorescent Lamp Ballasts
EPCA establishes energy conservation standards for certain ballasts
and requires that DOE conduct two cycles of rulemaking to determine
whether to amend the standards for these ballasts, including whether to
adopt standards for additional ballasts. (42 U.S.C. 6295(g)(5)-(8)) As
indicated in section II.B.1, DOE completed the first of these
rulemaking cycles by publishing the 2000 Ballast Rule. 65 FR 56740
(Sept. 19, 2000). In this rulemaking, the second rulemaking cycle
required by 42 U.S.C. 6295(g)(7), DOE is amending the existing
standards for ballasts and adopting standards for additional ballasts.
DOE initiated this rulemaking on January 14, 2008 by publishing in
the Federal Register a notice announcing the availability of the
``Energy Conservation Standards Rulemaking Framework Document for
Fluorescent Lamp Ballasts.'' (A PDF of the framework document is
available at https://www1.eere.energy.gov/buildings/appliance_standards/residential/pdfs/ballast_framework_011408.pdf.) In that
notice, DOE also announced a public meeting on the framework document
and requested public comment on the matters raised in the document. 73
FR 3653 (Jan. 22, 2008). The framework document described the
procedural and analytical approaches that DOE anticipated using to
evaluate energy conservation standards for the ballasts, and identified
various issues to be resolved in conducting this rulemaking.
DOE held the public meeting on February 6, 2008, where it:
Presented the contents of the framework document; described the
analyses it planned to conduct during the rulemaking; sought comments
from interested parties on these subjects; and in general, sought to
inform interested parties about, and facilitate their involvement in,
the rulemaking. Interested parties at the public meeting discussed the
active mode test procedure and several major analyses related to this
rulemaking. At the meeting and during the period for commenting on the
framework document, DOE received feedback that helped identify and
resolve issues involved in this rulemaking.
DOE then gathered additional information and performed preliminary
analyses to help develop potential energy conservation standards for
ballasts. DOE published in the Federal Register an announcement of the
availability of the preliminary technical support document (TSD) and of
another public meeting to discuss and receive comments on the following
matters: Product classes; the analytical framework, models, and tools
that DOE was using to evaluate standards; the results of the
preliminary analyses performed by DOE; and potential standard levels
that DOE could consider. 75 FR 14319 (March 24, 2010) (hereafter
referred to as the March 2010 notice). DOE also invited written
comments on these subjects. Id. The preliminary TSD is available at
https://www1.eere.energy.gov/buildings/appliance_standards/residential/fluorescent_lamp_ballasts_ecs_prelim_tsd.html. In the notice, DOE
also requested comment on other relevant issues that would affect
energy conservation standards for fluorescent lamp ballasts or that DOE
should address in the notice of proposed rulemaking (NOPR). Id. at
14322.
The public meeting announced in the March 2010 notice took place on
April 26, 2010. At that meeting, DOE presented the methodologies and
results of the analyses set forth in the preliminary TSD. Interested
parties discussed the following major issues at the public meeting: The
efficiency metric; how test procedure variation might affect efficiency
measurements; requirements for ballasts in environments that are
sensitive to electromagnetic interference (EMI); product classes;
manufacturer selling prices (MSPs) and overall pricing methodology;
markups; the maximum technologically feasible ballast efficiency;
cumulative regulatory burden; and shipments. DOE considered the
comments received since publication of the March 2010 notice, including
those received at the April 2010 public meeting, in the development of
the NOPR.
In April 2011, DOE proposed new and amended energy conservation
standards for fluorescent lamp ballasts. In conjunction with the NOPR,
DOE also published on its Web site the complete TSD for the proposed
rule, which incorporated the analyses DOE conducted and technical
documentation for each analysis. The TSD included the engineering
analysis spreadsheets, the LCC spreadsheet, the national impact
analysis spreadsheet, and the manufacturer impact analysis (MIA)
spreadsheet--all of which are available on DOE's Web site.\11\ The
proposed standards were as shown in Table II.3. 76 FR 20090, 20091
(April 11, 2011).
---------------------------------------------------------------------------
\11\ The Web site address for all the spreadsheets developed for
this rulemaking proceeding are available at: https://www1.eere.energy.gov/buildings/appliance_standards/residential/fluorescent_ballasts_nopr_analytical_tools.html.
Table II.3--Energy Conservation Standards Proposed in the April 2011
NOPR
------------------------------------------------------------------------
Product class Proposed BLE standard
------------------------------------------------------------------------
IS and RS ballasts that operate........ 1.32 * ln(total lamp arc power)
+ 86.11.
4-foot MBP lamps
8-foot slimline lamps
PS ballasts that operate............... 1.79 * ln(total lamp arc power)
+ 83.33.
4-foot MBP lamps
4-foot MiniBP SO lamps
4-foot MiniBP HO lamps
IS and RS ballasts that operate 8-foot 1.49 * ln(total lamp arc power)
HO lamps. + 84.32.
PS ballasts that operate 8-foot HO 1.46 * ln(total lamp arc power)
lamps. + 82.63.
Ballasts that operate 8-foot HO lamps 1.49 * ln(total lamp arc power)
designed for cold temperature outdoor + 81.34.
signs.
------------------------------------------------------------------------
[[Page 70556]]
In the NOPR, DOE invited comment in particular on the following
issues: (1) The exemption for T8 magnetic \12\ ballasts in EMI-
sensitive environments; (2) the appropriateness of establishing
efficiency standards using an equation dependent on lamp-arc power; (3)
the inclusion of several different ballast types in the same product
class; (4) the methodology used to calculate manufacturer selling
prices; (5) the efficiency levels considered; (6) the maximum
technologically feasible level; (7) markups; (8) the inclusion T12
ballasts in the baseline analysis for life cycle costs; (9) the
magnitude and timing of forecasted shipments; (10) the methodology and
inputs DOE used for the manufacturer impact analysis--specifically,
DOE's assumptions regarding markups, capital costs, and conversion
costs; (12) the potential impacts of amended standards on small
fluorescent lamp ballast manufacturers; (13) the trial standard levels
(TSLs) considered; (14) the proposed standard level; and (15) potential
approaches to maximize energy savings while mitigating impacts to
certain fluorescent ballast consumer subgroups. 76 FR 20090, 20177
(April 11, 2011).
---------------------------------------------------------------------------
\12\ When DOE refers to a magnetic ballast throughout this
document, it is referring to a low frequency ballast as defined by
as defined in ANSI C82.13-2002. Similarly, when DOE refers to an
electronic ballast, it is referring to a high frequency ballast as
defined by the same ANSI standard.
---------------------------------------------------------------------------
DOE held a public meeting on May 10, 2011, to hear oral comments on
and solicit information relevant to the proposed rule (hereafter the
May 2011 public meeting). At this meeting, the National Electrical
Manufacturers Association (NEMA) presented test data that they found
inconsistent with the data collected by DOE and that could affect the
standards established in the final rule. In general, NEMA's ballast
luminous efficiency values appeared to be lower than those obtained by
DOE. NEMA and other stakeholders agreed that there were discrepancies
between the two data sets and emphasized the importance of identifying
the source of the differences. In addition, DOE received comments on
the methodology used to account for compliance certification
requirements, design variation, and lab-to-lab variation and on the
appropriate shape of DOE's proposed efficiency level curves.
In light of these discrepancies, DOE published a notice of data
availability (NODA) on August 24, 2011 to: (1) Announce the
availability of additional test data collected by DOE and the data
submitted by NEMA; (2) address the differences between test data
obtained by DOE and test data submitted by NEMA; (3) describe the
methodological changes DOE was considering for the final rule based on
the additional data; (4) present efficiency levels developed using the
revised methodology and all available test data; and (5) request public
comment on these analyses.\13\
---------------------------------------------------------------------------
\13\ The August 2011 NODA and accompanying data are available
here: https://www1.eere.energy.gov/buildings/appliance_standards/residential/notice_of_data_availability.html.
---------------------------------------------------------------------------
DOE considered the comments received in response to both the April
2011 NOPR and the August 2011 NODA when developing this final rule, and
responds to these comments in the following sections.
III. Issues Affecting the Scope of This Rulemaking
A. Additional Fluorescent Lamp Ballasts for Which DOE is Adopting
Standards
1. Scope of EPCA Requirement That DOE Consider Standards for Additional
Ballasts
As discussed in section II.A, amendments to EPCA established energy
conservation standards for certain fluorescent lamp ballasts and
directed DOE to conduct two rulemakings to consider amending the
standards. The first amendment was completed with the publication of
the 2000 Ballast Rule. This rulemaking fulfills the statutory
requirement to determine whether to amend standards a second time. EPCA
specifically directs DOE, in this second amendment, to determine
whether to amend the standards in effect for fluorescent lamp ballasts
and whether such standards should be amended so that they would be
applicable to additional fluorescent lamp ballasts. (42 U.S.C.
6295(g)(7)(B))
The April 2011 NOPR notes that a wide variety of fluorescent lamp
ballasts are not currently covered by energy conservation standards,
and thus are potential candidates for coverage under 42 U.S.C.
6295(g)(7). DOE encountered similar circumstances in a recent
rulemaking that amended standards for general service fluorescent and
incandescent reflector lamps (hereafter referred to as the 2009 Lamps
Rule).\14\ 74 FR 34080, 34087-8 (July 14, 2009). In that rule, DOE was
directed by EPCA to consider expanding its scope of coverage to include
additional general service fluorescent lamps (GSFL). EPCA defines GSFLs
as fluorescent lamps that can satisfy the majority of fluorescent lamp
applications and that are not designed and marketed for certain
specified, non-general lighting applications. (42 U.S.C. 6291(30)(B))
As such, the term ``general service fluorescent lamp'' is defined by
reference to the term ``fluorescent lamp,'' which EPCA defines as ``a
low pressure mercury electric-discharge source in which a fluorescing
coating transforms some of the ultraviolet energy generated by the
mercury discharge into light,'' and as including the four enumerated
types of fluorescent lamps for which EPCA already prescribes standards.
(42 U.S.C. 6291(30)(A); 42 U.S.C. 6295(i)(1)(B)) To construe ``general
service fluorescent lamp'' in 42 U.S.C. 6295(i)(5) as limited to those
types of fluorescent lamps would mean there are no GSFLs that are not
already subject to standards, and hence, there would be no
``additional'' GSFLs for which DOE could consider standards. Such an
interpretation would conflict with the directive in 42 U.S.C.
6295(i)(5) that DOE consider standards for ``additional'' GSFLs,
thereby nullifying that provision.
---------------------------------------------------------------------------
\14\ Documents for the 2009 Lamps Rule are available at: https://www1.eere.energy.gov/buildings/appliance_standards/residential/incandescent_lamps.html.
---------------------------------------------------------------------------
Therefore, DOE concluded that the term ``additional general service
fluorescent lamps'' in 42 U.S.C. 6295(i)(5) allows DOE to set standards
for GSFLs other than the four enumerated lamp types specified in the
EPCA definition of ``fluorescent lamp.'' As a result, the 2009 Lamps
Rule defined ``fluorescent lamp'' to include:
(1) Any straight-shaped lamp (commonly referred to as 4-foot medium
bipin lamps) with medium bipin bases, a nominal overall length o