Guidelines for Voluntary Greenhouse Gas Reporting, 20784-20817 [06-3745]
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20784
Federal Register / Vol. 71, No. 77 / Friday, April 21, 2006 / Rules and Regulations
DEPARTMENT OF ENERGY
10 CFR Part 300
RIN 1901–AB11
Guidelines for Voluntary Greenhouse
Gas Reporting
Office of Policy and
International Affairs, U.S. Department of
Energy.
ACTION: Final rule.
AGENCY:
SUMMARY: Section 1605(b) of the Energy
Policy Act of 1992 directed the
Department of Energy (DOE) to issue
guidelines establishing a voluntary
greenhouse gas reporting program. On
February 14, 2002, the President
directed DOE, together with other
involved Federal agencies, to
recommend reforms to enhance the
Voluntary Reporting of Greenhouse
Gases Program established by DOE in
1994. DOE issued interim final General
Guidelines on March 24, 2005, and also
on that date published a notice of
availability inviting public comment on
draft Technical Guidelines needed to
fully implement the revised Voluntary
Reporting of Greenhouse Gases Program.
This notice of final rulemaking responds
to public comments on the interim final
General Guidelines and draft Technical
Guidelines; sets forth the final General
Guidelines; and announces the
availability of the final Technical
Guidelines.
Effective Date: The final General
Guidelines and Technical Guidelines
are effective June 1, 2006. The
incorporation by reference of the
Technical Guidelines is approved by the
Director of the Federal Register as of
June 1, 2006.
FOR FURTHER INFORMATION CONTACT:
Mark Friedrichs, PI–40, Office of Policy
and International Affairs, U.S.
Department of Energy, 1000
Independence Ave., SW., Washington,
DC 20585, or e-mail:
1605bguidelines.comments@hq.doe.gov
DATES:
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SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
A. Background
B. Process for Implementing the Guidelines
II. Overview of Major Changes Made in
Response to Comments
III. Discussion of Public Comments and the
Final Revised Guidelines
A. Implementation Schedule
B. Process for Updating or Amending the
Guidelines
C. Distinction Between Reporting Under
the Program and Registering Reductions
1. Reporting Under the Program
2. Registration Requirements
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D. Entity Definitions, Boundaries and
Statements
1. Entity Definition
2. Entity Boundaries—General
3. Entity Boundaries—U.S. and Non-U.S.
Emissions
4. Entity Statements
E. Large v. Small Emitters
F. Aggregators
G. Other Definitions
H. Start Year and First Reduction Year
I. Electricity Dactors and Benchmarks
J. Inventories
1. Requirement for Entity-Wide Inventories
With a Quality Rating of at Least 3.0
2. De minimis Exclusion From Entity-Wide
Emission Inventories
3. Ratings for Estimation Methods Using
Default Values
4. References to Continuous Emissions
Monitoring Systems (CEMS)
5. Citations of Protocols and Emission
Factors Developed by Other
Organizations
6. Options for Simplifying Emission
Reports
7. Eliminate Requirements To Report
Emissions From Biogenic Sources and
To Report Certain Non-Fuel Uses of
Fossil Fuels
8. Treatment of Agriculture and Forestry
9. Stationary Source Combustion
10. Mobile Sources
11. Industrial Processes
12. Indirect Emissions
13. Geologic Sequestration
K. Reductions
1. Selecting Appropriate Reduction
Calculation Methods
2. Base Periods and Base Values
3. Enabling Reporters To Choose More
Stringent Base Values
4. Emissions Intensity
5. Absolute Emissions
6. Changes in Carbon Stocks
7. Avoided Emissions
8. Action-Specific Methods
9. Estimating Reductions From Energy
Generation and Distribution
L. Offset Reductions
M. Certification and Verification
1. Certification
2. Independent Verification
N. Reporting and Recordkeeping
O. Report Review and Acceptance Process
P. Publication of General Guidelines in the
Code of Federal Regulations
IV. Regulatory Review and Procedural
Requirements
A. Review Under Executive Order 12866
B. Review Under the Regulatory Flexibility
Act
C. Review Under the Paperwork Reduction
Act
D. Review Under the National
Environmental Policy Act
E. Review Under Executive Order 13132
F. Review Under the Treasury and General
Government Appropriations Act, 2001
G. Review Under Executive Order 12988
H. Review Under the Unfunded Mandates
Reform Act of 1995
I. Review Under the Treasury and General
Government Appropriations Act, 1999
J. Review Under Executive Order 13211
K. Congressional Review
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I. Introduction
A. Background
Section 1605(b) of the Energy Policy
Act of 1992 (EPACT) directs the
Department of Energy, with the Energy
Information Administration (EIA), to
establish a voluntary reporting program
and database on emissions of
greenhouse gases, reductions of these
gases, and carbon sequestration
activities (42 U.S.C. 13385(b)). Section
1605(b) requires that DOE’s guidelines
provide for the ‘‘accurate’’ and
‘‘voluntary’’ reporting of information on:
(1) Greenhouse gas emission levels for a
baseline period (1987–1990) and
thereafter, annually; (2) greenhouse gas
emission reductions and carbon
sequestration, regardless of the specific
method used to achieve them; (3)
greenhouse gas emission reductions
achieved because of voluntary efforts,
plant closings, or state or federal
requirements; and (4) the aggregate
calculation of greenhouse gas emissions
by each reporting entity (42 U.S.C.
13385(b)(1)(A)–(D)). Section 1605(b)
contemplates a program whereby
voluntary efforts to reduce greenhouse
gas emissions can be recorded, with the
specific purpose that this record can be
used ‘‘by the reporting entity to
demonstrate achieved reductions of
greenhouse gases’’ (42 U.S.C.
13385(b)(4)).
In 1994, after notice and public
comment, DOE issued General
Guidelines and sector-specific
guidelines that established the
Voluntary Reporting of Greenhouse
Gases Program for recording voluntarily
submitted data and information on
greenhouse gas emissions and the
results of actions to reduce, avoid or
sequester greenhouse gas emissions. The
1994 General Guidelines and supporting
documents may be accessed at https://
www.eia.doe.gov/oiaf/1605/
guidelns.html. The Guidelines were
intentionally flexible to encourage the
broadest possible participation. They
permit participants to decide which
greenhouse gases to report, and allow
for a range of reporting options,
including reporting of total emissions or
emissions reductions or reporting of just
a single activity undertaken to reduce
part of their emissions. From its
establishment in 1995 through the 2004
reporting year, 417 entities, including
utilities, manufacturers, coal mine
operators, landfill operators and others,
have reported their greenhouse gas
emissions and/or their emission
reductions to EIA.
On February 14, 2002, the President
directed the Secretary of Energy, in
consultation with the Secretary of
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Commerce, the Secretary of Agriculture,
and the Administrator of the
Environmental Protection Agency, to
propose improvements to the current
section 1605(b) Voluntary Reporting of
Greenhouse Gases Program. These
improvements are to enhance
measurement accuracy, reliability, and
verifiability, working with and taking
into account emerging domestic and
international approaches.
On May 6, 2002, DOE published a
Notice of Inquiry soliciting public
comments on how best to improve the
Voluntary Reporting of Greenhouse
Gases Program (67 FR 30370). Written
comments were received from electric
utilities; representatives of energy,
manufacturing and agricultural sectors;
Federal and State legislators; State
agencies; waste management companies;
and environmental and other non-profit
research and advocacy organizations.
DOE held public workshops in
Washington, DC, Chicago, San Francisco
and Houston during November and
December of 2002 to receive information
and hear the views of interested
persons. In addition, the U.S.
Department of Agriculture sponsored
two workshops in January 2003 to
solicit input on the accounting rules and
guidelines for reporting greenhouse gas
emissions in the forestry and agriculture
sectors. These workshops explored in
greater depth many of the issues raised
in the Notice of Inquiry and addressed
in the written comments.
On December 5, 2003, DOE proposed
revised General Guidelines (68 FR
68204). A public workshop was held on
January 12, 2004, to discuss that
proposal and to receive public
comment. Approximately 200 persons
attended the workshop. In addition,
over 300 written comments were
received by the close of the public
comment period on February 17, 2004.
DOE published interim final revised
General Guidelines on March 24, 2005
(70 FR 15169), and, in a notice
published in the Federal Register on the
same day, made available for public
comment the draft Technical Guidelines
necessary to fully implement the
revisions to the Voluntary Program (70
FR 15164). DOE sponsored a public
workshop on these revised guidelines
on April 26 and 27, 2005, and USDA
and DOE co-sponsored another
workshop on May 5, 2005. In response
to public comments, DOE extended the
period for comments on the revised
guidelines by 30 days to June 22, 2005.
Ultimately, DOE received over 90
written comments, totaling over 1000
pages. All written comments and
transcripts of the public workshops are
available on the Web and can be
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accessed at: https://www.pi.energy.gov/
enhancingGHGregistry/. On September
19, 2005, DOE published a notice in the
Federal Register delaying the effective
date of the interim final guidelines until
June 1, 2006 (70 FR 54835).
DOE now publishes final General
Guidelines and announces the
availability of final Technical
Guidelines that are incorporated by
reference in the General Guidelines. The
revised General and Technical
Guidelines are designed to enhance the
measurement accuracy, reliability and
verifiability of information reported
under the 1605(b) program and to
contribute to the President’s climate
change goals. The key elements of the
revised guidelines remain the same as
those present in the interim final
General Guidelines:
• Enable larger emitters to register
reductions if they provide entity-wide
emissions data and can demonstrate
they achieved entity-wide emission
reductions that contribute to the
President’s goal of reducing the
greenhouse gas emissions of the U.S.
economy.
• Provide for simplified procedures
for small emitters to report and to
register reductions.
• Provide for simplified reports from
entities that do not want to register their
reductions.
• Encourage companies and other
reporting entities to report at the highest
level.
• Require participants to ensure the
accuracy and completeness of their
reports, and encourage independent
verification.
• Allow participants to report and
register reductions achieved
internationally.
Based on the framework set forth by
the interim final guidelines and the
various improvements made in response
to the public comments received,
today’s final revised guidelines will
enhance:
• Measurement accuracy by creating a
ranking system for methods to calculate
emissions, incorporating the best
available inventory methods, and
enabling more sources to be covered;
• Reliability by creating a more
systematic approach to reporting,
stressing inventories and entity-wide
reporting; and
• Verifiability by creating a more
transparent reporting system for
emissions and reductions, requiring
recordkeeping and encouraging
independent verification.
The Secretary of Energy has approved
issuance of this final rule.
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B. Process for Implementing the
Guidelines
The General Guidelines set forth in
this notice and the Technical Guidelines
incorporated by reference will go into
effect on June 1, 2006. In the near
future, EIA intends to make available for
public review and comment draft forms
for collecting the data covered by these
guidelines, including the Simplified
Emissions Inventory Tool (SEIT)
referenced in the guidelines. After
taking into account any public
comments it receives and complying
with the requirements of the Paperwork
Reduction Act of 1995, EIA anticipates
that final forms will be issued before the
end of 2006. In addition, EIA will be
developing the software necessary to
permit electronic reporting and the
creation of an automated and widely
accessible data base. EIA does not
anticipate completing the necessary
software until mid-2007. If time and
resources permit, EIA may conduct
cognitive testing of beta versions of the
reporting software. Should EIA conduct
such testing, EIA will solicit potential
participants via a public notice, postings
to its website, or some other means.
According to the forms and software
schedule currently anticipated by EIA,
the revised guidelines will be used to
govern the 2007 reporting cycle. Until
then, entities interested in reporting
under the program during the 2006
reporting cycle should use the existing
guidelines and forms.
II. Overview of Major Changes Made in
Response to Comments
The public comments received by
DOE expressed considerable support for
the emphasis of the revised guidelines
on entity-wide reporting on all
greenhouse gas emissions, including the
added requirements imposed on entities
that are seeking to register reductions.
There was also substantial support for
DOE’s efforts to enhance the quality,
consistency and credibility of the
emission inventories and reductions
being reported. The comments,
however, raised a number of concerns
regarding the potential burdens of
reporting under the revised guidelines,
possible incompatibilities with various
existing reporting programs or
protocols, and the limitations on
reporting certain types of emission
reductions, especially those occurring
outside the boundaries of the reporting
entity. While the basic framework of the
guidelines remains the same, DOE has
made a number of changes designed to
address these concerns, and has adopted
many of the specific recommendations
made during the comment period.
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To reduce the potential burdens of
reporting under the revised guidelines,
DOE’s final guidelines:
• Enable entities that have their
reports independently verified or that
certify their use of higher quality
inventory methods to file less detailed
reports;
• Increase the ratings of some
commonly used methods for estimating
emissions;
• Enable reports on non-U.S.
emissions to be consolidated regionally
or globally (as long as U.S. data is kept
separate); and
• Clarify the flexibility available to
reporters that wish to avoid or minimize
the complexities of accounting for
changes in carbon stock or other
provisions.
To increase the compatibility of the
revised guidelines with various existing
reporting programs and protocols,
DOE’s final guidelines update its
references to existing protocols and
update the emission factors drawn from
such protocols; provide an exception in
section 300.5(b) for participants in
EPA’s Climate Leaders or DOE’s Climate
VISION who may wish to use base
periods that end as early as 2000; and
attempt to increase the alignment of
various definitions and methods with
those used by other existing programs.
To expand the opportunities for
reporting offset emission reductions,
DOE’s final guidelines, among other
things: (1) Add new action-specific
methods for demand-side management
programs, the substitution of fly ash for
cement by concrete mixers, and
anaerobic digestion of waste at
agricultural facilities and wastewater
treatment plants; (2) enable multiple
reporting entities to register portions of
the offset reductions achieved by a
single other entity, as long as the other
entity complies with all of the
requirements for registration and has
entered into an agreement with each of
the reporting entities; and (3) permit the
accelerated reporting of carbon stock
increases expected to occur on land that
is being reforested, restored and
permanently protected.
DOE has not adopted the
recommendation of commenters who
advocated that DOE mandate
participation in the 1605(b) program
because such a mandate is beyond the
statutory authority of DOE.
to the guidelines that DOE has made in
response to the comments.
III. Discussion of Public Comments and
the Final Revised Guidelines
This section of the Supplementary
Information discusses the issues raised
by the public comments on the interim
final General Guidelines and the draft
Technical Guidelines and any changes
C. Distinction Between Reporting Under
the Program and Registering Reductions
The revised guidelines set forth the
requirements for all reporters under the
1605(b) program as well as requirements
that must be met by only those reporters
that are seeking to register emission
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A. Implementation Schedule
A few comments suggested that DOE
consider a delay in the start of the
revised program or a phased
implementation of the new
requirements. DOE does not consider
either a delayed or phased
implementation of the revised
guidelines to be necessary or practical.
Starting the program in calendar year
2007 should give most reporters
sufficient time to prepare to meet the
requirements of the new program. If
individual reporters require additional
time, they may delay their own
participation. Entities that are unable to
meet all of the requirements for
registration may simply choose to meet
only the requirements for reporting
under the program until such time as
they are prepared to meet all of the
requirements for registration. Another
available option would be to take more
time to complete the entity’s first or
second annual reports. For example, an
entity could decide to submit its report
on 2006 emissions during 2008, rather
than by the 2007 deadline for reports
that are to be included in EIA’s first
public report on 2006 emissions (likely
to be issued in late 2007 or early 2008).
Entities may submit reports on prior
year emissions and emission reductions
at any time.
B. Process for Updating or Amending
the Guidelines
DOE intends to review and, if
necessary, update the guidelines
approximately every three years,
although exceptional circumstances
may require amendment of the
guidelines at other times. Modifications
to either the General Guidelines or the
Technical Guidelines will be subject to
public notice and comment. Some
commenters noted that this public
process might be too cumbersome and
time consuming for the adoption of
routine updates to the many emission
factors and protocols cited by the
guidelines. To address this concern,
DOE has modified some provisions of
the Technical Guidelines to direct
reporters to use the most current version
of certain government-sponsored or
consensus-based factors, methods and
protocols.
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reductions (see section 300.1(b) and (c)
of this rule for a description of the
requirements for reporting and
registering emissions and reductions).
More specifically, while some new
requirements are imposed on all
reporters by the revised guidelines, the
requirements for entity-wide reports and
use of high quality emission inventory
and reduction methods are imposed
only on those entities that are seeking to
register reductions. The distinct
requirements for reporting under the
program and for registering reductions
are key to achieving DOE’s objective of
enhancing the overall quality and
credibility of the reductions
documented by the program, while at
the same time preserving most of the
flexibility available to reporters under
the original program guidelines.
Some commenters recommended that
the distinction between reporting under
the program and registering emission
reductions be eliminated, which would
enable all reporters to receive the same
level of recognition, regardless of
whether or not they met the entity-wide
reporting requirements. DOE believes
that the elimination of this distinction
would significantly diminish the
incentive for large emitters to improve
the overall quality of their reports by
undertaking the more costly activities
associated with emission inventories
and entity-wide assessments of
reductions, which are required for
registration.
In addition to objecting on policy
grounds to the distinction between
reported registered reductions and other
reported reductions, one commenter
argued that in the absence of express
authorization, there is no legal basis in
section 1605(b) for changing from a
unitary system of reporting to a two-tier
system that distinguishes between two
types of reported emissions and
reductions. Other commenters
contended that because section 1605(b)
expressly includes reductions from
plant closings among the information
that entities may report under the
program, DOE may not exclude such
reductions from the reductions that can
be registered under the revised
guidelines.
DOE rejects the comments arguing
that DOE may not distinguish among
different types of reported emissions
and reductions within EIA’s database
because there is no express authority for
such differentiation in section 1605(b).
Section 1605(b) broadly charges DOE
with issuing guidelines, after
opportunity for public comment, for the
‘‘voluntary collection and reporting of
information on sources of greenhouse
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gases.’’ 42 U.S.C. 13385(b)(1). Further,
the guidelines must include:
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Procedures for the accurate voluntary
reporting of information on—(A) greenhouse
gas emissions [starting with a statutorilyprescribed baseline period and annually
thereafter]; (B) annual reductions of
greenhouse gas emissions and carbon fixation
achieved through any measures, including [a
list of such measures]; (C) reductions in
greenhouse gas emissions achieved as a
result of—(i) voluntary reductions; (ii) plant
or facility closings; and (iii) State or Federal
requirements; and (D) an aggregate
calculation of greenhouse gas emissions by
each reporting entity.
42 U.S.C. 133385(b)(1)(A)–(D) (emphasis
added).
Nothing in the statute limits the
information on sources of greenhouse
gases reported under the program to that
described in section 1605(b)(1)(A)–(D).
Rather, the information described in (A)
through (D) is the minimum information
that may be reported under DOE’s
procedures. While the text of section
1605(b) does not specifically address the
question of whether DOE may create
categories of reported greenhouse gas
information within the EIA database,
DOE’s procedures must provide for the
accurate voluntary reporting of
information. One of the goals of
registration under the final revised
guidelines is to enhance the accuracy
and reliability of greenhouse gas
emissions and reductions information.
Thus, the text of section 1605(b), read in
its entirety, supports DOE’s view that
establishment of a category of registered
emissions for emissions and reductions
that meet certain requirements for
entity-wide reporting is implicitly
authorized by the statute.
DOE also rejects the comment that
because section 1605(b) expressly
includes reductions from plant and
facility closings among the information
that entities may report under DOE’s
procedures, DOE may only establish
categories of reported information that
include reductions from plant and
facility closings. DOE’s textual analysis
stated above in rejecting the argument
that DOE may not establish a two-tiered
reporting system applies here as well.
Nothing in the statute limits DOE’s
authority to go beyond the minimum
information categories in section
1605(b)(1)(A)–(D), and the requirement
that DOE’s procedures provide for the
accurate voluntary reporting of
information is implicit authorization for
DOE to establish a system of registration
that enhances the accuracy and
reliability of information reported on an
entity-wide basis.
Several commenters suggested that
the revised program guidelines should
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include a summary of the guidelines’
requirements for reporting and for
registering emissions and reductions. In
response, DOE is providing a summary
of the requirements in section 300.1 of
today’s General Guidelines. The
requirements for reporting and
registering emissions and reductions are
described in the following sections of
this Supplementary Information.
1. Reporting Under the Program
Each reporter under the program must
be an ‘‘entity,’’ as defined in the
guidelines and must file an entity
statement. Reporters not intending to
register emission reductions must, at
minimum, meet the entity statement,
record keeping, and certification
requirements set forth in sections
300.5(f), 300.9, and 300.10, respectively.
They may choose to report their
emissions and/or their emission
reductions on an entity-wide basis or for
selected elements of their entities,
selected gases or selected sources.
Emission inventories for any year back
to 1990 may be reported, and emission
reductions may be reported for any year
back to 1991, relative to base periods of
one to four years, ending no earlier than
1990. All reporting entities, whether or
not they intend to register reductions,
must use the emission inventory and
emission reduction calculation methods
specified in the Technical Guidelines.
For example, as discussed in section
III.K.8. of this Supplementary
Information, the guidelines now provide
for the reporting of the emissions and
reductions associated with
chlorofluorocarbons (CFCs), although
such reductions are not eligible for
registration. In the future, DOE may
revise the guidelines to add methods
that permit the reporting and, in some
cases, the registration of reductions
associated with other gases. While
entities that do not intend to register
reductions need not ensure that their
emission inventories achieve a weighted
average quality rating of 3.0 or higher (a
requirement that is discussed in section
III.J.1 below), they must calculate and
report the weighted average quality
rating of any emission inventories they
do report. In most situations, entities
not registering reductions may choose
an emissions intensity, absolute
emissions or generic action-specific
method to calculate the emission
reductions they report. However, in
those situations where a special
calculation method is provided, such as
sequestration, the sale of distributed
energy, or an action-specific method,
the entity must use the appropriate
method provided in the Technical
Guidelines. Entities not intending to
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register reductions may also report (but
not register) offset reductions achieved
by third parties outside their boundaries
as long as such reductions are reported
separately and calculated in accordance
with methods specified in the
guidelines. The third party that
achieved these reductions must agree to
their being reported as offset reductions,
and must also meet all of the other
minimum requirements of reporting
under the program, including the
provision of an entity statement, the
maintenance of records, and necessary
certifications as stipulated in §§ 300.9
and 300.10.
2. Registration Requirements
Entities that intend to register
reductions must meet a number of
additional requirements, although these
requirements differ depending on
whether the entity is a large or small
emitter.
To be eligible for registration, a
reduction must have been calculated
using a base period ending no later than
2002, unless the entity has committed
under the Climate Leaders or Climate
VISION programs to reduce its entitywide emissions relative to a base period
that ends earlier than 2002, but no
earlier than 2000.
In order to register reductions, large
emitters must submit entity-wide
emission inventories that meet or
exceed the minimum quality
requirements specified in § 300.6(b) and
the Technical Guidelines. Any
registered reductions must be based on
entity-wide assessments of annual
changes in net emissions, determined in
accordance with §§ 300.7 and 300.8 and
the Technical Guidelines. They must
also meet the entity statement and
certification requirements specified in
§§ 300.5 and 300.10.
Small emitters must also submit
emission inventories that meet
minimum quality requirements and base
their registered reductions on
assessments of annual changes in net
emissions, but small emitters may
restrict these inventories and
assessments to a single type of activity,
such as forest management, building
operations or agricultural tillage, rather
than covering all of their entity’s
emissions. Small emitters must also
submit entity statements, certify the
accuracy of their reports and meet other
requirements of reporting and
registering.
Both large emitters and small emitters
that have met the requirements for
registering their own reductions may
also register offset reductions achieved
by other entities, as long as they have
an agreement with the third party to do
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so and these third parties have met all
of the requirements for registration.
Small emitters that serve as aggregators
may register offset reductions without
reporting on their own emissions.
Entities that report offset reductions
achieved by very small emitters (those
typically emitting less than 500 metric
tons of CO2 equivalent emissions per
year) as a result of demand management
or other programs that reduce
greenhouse gas emissions, may register
such reductions as long as they are
calculated in accordance with the
action-specific method identified in
section 300.8(h)(5).
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D. Entity Definitions, Boundaries and
Statements
Most of the comments on these
provisions of the interim final
guidelines were generally supportive,
although a few significant concerns
were raised and a number of specific
changes were recommended.
1. Entity Definition
Several commenters urged DOE to
require entities to report at their highest
level of aggregation within the United
States, while other commenters urged
DOE to provide entities even more
flexibility in how they define
themselves for the purpose of reporting
under the program. The final guidelines
retain the basic approach put forward in
the interim final General Guidelines:
entities must have a legal basis and are
encouraged—but not required—to report
at their highest level of aggregation
within the United States. If an entity
chooses to report at a lower level of
aggregation, the reporting entity must
have a legal basis and must be defined
in a way that is consistent with the
management structure of the parent
company or organization.
Section 300.2 of the interim final rule
defines ‘‘entity or reporting entity’’ as
the whole or part of any business,
institution, organization or household
that is recognized as an entity under any
U.S. Federal, State or local law that
applies to it; is located, at least in part,
in the United States; and whose
operations affect U.S. emissions of
greenhouse gases. Some commenters
argued that the ‘‘legally distinct entity’’
test is too inflexible and urged DOE to
abandon the test. One stated that
electricity providers may have different
reporting options due to differences in
State regulation or the absence of such
regulation. The commenter
recommended revising the definition to
allow an entity to consist of a set of
corporate business and other
organizational units that comprise a
single business activity, even though
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they may not be legally distinct.
Another commenter stated that the
definition of ‘‘entity’’ would pose a
problem for global corporations that are
legally structured by product line, rather
than by country. A large industry
association did not criticize the
substance of DOE’s definition of ‘‘entity
or reporting entity,’’ but rather offered
drafting guidance that it considered
would better accomplish DOE’s intent.
It also suggested a separate definition of
‘‘reporting entity.’’
After considering the comments, DOE
has retained the requirement that an
entity that reports under the 1605(b)
program must be recognized as an entity
under a U.S. Federal, State or local law.
In light of changes to the provisions for
reporting non-U.S. emissions (discussed
elsewhere in this Supplementary
Information), DOE does not believe the
definition of ‘‘entity’’ in the final
guidelines will pose a problem for
global corporations. While not
necessarily agreeing with many of the
criticisms of the interim final guideline
definition of ‘‘entity or reporting
entity,’’ DOE found the suggested
drafting improvements to be helpful and
has included several of them in revised
definitions for the terms ‘‘entity’’ and
‘‘reporting entity.’’ These changes
include increased emphasis on the
coverage of government bodies, agencies
or other institutions, which DOE always
intended to be encompassed by the
broad definition of entity included in
the guidelines.
2. Entity Boundaries—General
The organizational boundaries of
reporting entities largely determine
which emissions and sources are
covered by the entity’s reports. DOE’s
interim final General Guidelines
encourage entities to use financial
control as the primary basis for
determining the organizational
boundaries of the reporting entity.
While the interim guidelines encourage
the use of financial control as the basis
for setting organizational boundaries,
they permit entities to use other
methods, such as equity share or
operational control, as long as they are
explained.
Boundary definitions are important
because they determine what emission
and emission reductions a particular
reporting entity may assume
responsibility for when reporting under
the program. As a voluntary reporting
program, however, 1605(b) boundaries
do not determine the legal rights of
reporting entities to emissions or
emission reductions. They are used only
as the basis for DOE recognition of any
registered reductions reported under the
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program. The comments received by
DOE on these provisions of the
guidelines were generally supportive of
DOE’s approach, although some
encouraged even more flexibility. No
changes have been made to the
provisions included in the interim final
guidelines.
Financial control encompasses all
buildings, facilities, lands, vehicles and
equipment that are wholly owned by the
entity or in which the entity has a
controlling financial interest.
Conversely, it usually does not include
buildings, facilities, lands, vehicles and
equipment that are wholly owned by a
different entity or in which another
entity has a controlling financial
interest. However, financial control
would exist if an entity has a long-term
lease or other long-term agreement that
gives it effective control over capital
investment and operational decisions.
An alternative method for
determining entity boundaries is equity
share, where more than one entity has
a financial interest in a particular
facility or emission source, and each of
the entities takes responsibility for
reporting only a portion of the facilities
emissions and reductions. Operational
control, where an entity controls the
day-to-day operations of facility or
source, but does not exercise long term
financial control might also be an option
under certain circumstances. If either
equity share or operational control is
chosen as the method for determining
boundaries, the reporting entity must
inform the other entities that share
responsibility for particular sources of
its intention to report under the 1605(b)
in order to ensure that the sources
emissions or reductions are not doublecounted under the program. Finally, the
General Guidelines have been modified
to provide further guidance regarding
the coverage of partially-owned or
leased sources, and sources that are
neither owned nor leased by the
reporting entity.
3. Entity Boundaries—U.S. and NonU.S. Emissions
The interim final guidelines permit
entities to define their entity so as to
include operations, and their associated
emissions, located outside of the United
States. They also permit certain nonU.S. entities to be the source of offset
emission reductions, as long as they
meet all of the requirements of the
revised guidelines. The interim final
General Guidelines would allow entities
to both report and register emissions
and emission reductions occurring
outside of the United States, subject to
certain requirements. One of these
requirements is that non-U.S. emissions
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and reductions must be reported
separately from U.S. emissions and
reductions. DOE has clarified the
guidelines to indicate that this does not
mean that the U.S. and non-U.S.
emissions and reductions must be
submitted in separate reports. Under the
final guidelines, non-U.S. emissions and
reductions must be included in one or
more distinct subentities identified in
the entity’s report to EIA and must be
separately sub-totaled before being
considered as part of the entity’s net
emission reductions qualifying for
registration. Unless specifically
identified by the report, EIA will
presume that all non-U.S. reductions are
governed, at least in part, by national or
international greenhouse gas
regulations, and that such reductions
might be eligible for transfer or trading
to other entities. However, reporters will
not be able to register emission
reductions that do not meet the
requirements of these guidelines,
whether or not they are eligible for
transfer or trading under a foreign
national or multi-national scheme.
In allowing entities to both report and
register emissions and emission
reductions occurring outside of the
United States, the interim final General
Guidelines require that emissions and
reductions for each country be
segregated in the report submitted to
EIA. One stakeholder, a large
multinational corporation, argued that
this would place an undue burden on
companies having operations in
numerous countries, particularly where
business units that provide an
appropriate level of aggregation (i.e., as
separate subentities) cross national
borders. In the final guidelines, DOE
encourages entities that wish to report
or register non-U.S. activities to
segregate emissions and reductions from
each country in a separate subentity.
However, reporters are permitted to
aggregate non-U.S. emissions and
reductions at regional and even nonU.S. global levels, as long as they
identify each of the countries covered
and the country-specific factors used to
generate their reports.
4. Entity Statements
DOE’s interim final guidelines
include a number of specific
requirements for the contents of the
entity statements to be submitted by all
reporters, although the specific
requirements vary somewhat depending
on whether the reporter is a large or
small emitter interested in registering
reductions, or a reporter that is not
intending to register reductions. Very
few comments were received on the
requirements and no significant changes
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have been made to the provisions
concerning the entity statement.
E. Large v. Small Emitters
Under the interim final guidelines,
‘‘small emitters’’ are a special category
of reporters that are exempted from
certain requirements for the registration
of reductions, including entity-wide
emission inventories and entity-wide
assessments of reductions. DOE
received a substantial number of
comments on these provisions. Several
of these comments were critical of the
exemptions and argued that small
emitters deserve no special treatment.
These were countered by a number of
other comments that argued that the
burdens on small emitters under the
interim final guidelines are too onerous,
and the exemptions should be
expanded. After considering these
comments, DOE believes that the
provisions in the interim final
guidelines strike the proper balance
between relieving the burden on small
emitters and requiring the submission of
emissions information for registration.
Consequently, DOE has not significantly
altered these provisions of the
guidelines. It should be noted that small
emitters seeking to register reductions
are only required to report on the
emissions and reductions associated
with a single, chosen ‘‘activity,’’ rather
than all of the entity’s activities. Finally,
the guidelines continue to permit
entities to use a Simplified Emissions
Inventory Tool (SEIT), to be provided by
the Energy Information Administration,
to estimate their emissions for purposes
of determining whether the entity is a
small or large emitter, and for estimating
the quantity of emissions excluded as de
minimis. The guidelines now clearly
state that the SEIT may not be used for
the preparation of emission inventories.
F. Aggregators
In the interim final guidelines, DOE
provides some special guidance for
entities that register reductions on
behalf of other entities, so-called
‘‘aggregators.’’ Large emitters that serve
as aggregators must meet all of the
requirements for registration, including
submission of entity-wide emission
inventories and entity-wide assessment
of their emission reductions. However,
entities that are small emitters can
register the offset reductions of other
entities and not report on any of their
own emissions or reductions, although
such small emitters would have to
submit an entity-statement and an
estimate of their total emissions
indicating that they qualified as a small
emitter. While aggregators can be either
small or large emitters, DOE believes
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that most are likely to be small
organizations or companies that would
qualify as small emitters. Some
aggregators, such as trade associations,
might report on behalf of large emitters,
but the potential benefits of such
indirect reporting by large emitters are
limited because essentially the same
data and certifications would have to be
provided to DOE, whether the entity
reported directly or through an
aggregator. DOE received some requests
for clarification of these requirements,
but none of the comments suggested
major changes.
G. Other Definitions
The interim final General Guidelines,
and the Glossary accompanying the
draft Technical Guidelines, define terms
used in the guidelines. These
definitions were the focus of
considerable comment, and many
comments offered specific suggestions
for changes. Others recommended the
addition of new definitions of terms or,
in some cases, the transfer of a
definition that appeared in the Glossary
to the definition section of the General
Guidelines. A few comments noted
differences between terms and
definitions used in the DOE guidelines
and comparable terms and definitions
used in other protocols for the reporting
of greenhouse gas emissions. While DOE
has attempted to minimize such
differences, DOE has concluded that in
some situations, it is necessary to use a
new term or define a term in a way that
differs from the usage or definition of
the term used by other programs. For
this reason, DOE urges reporters and
other users to carefully review the
definitions contained in both the final
General Guidelines and the final
Technical Guidelines.
The following sections summarize the
comments received on definitions and
DOE’s response to the comments.
Activity of a small emitter. This term
is used to define the minimum scope of
reports by small emitters interested in
registering reductions. It has been
modified slightly to more clearly
indicate that it applies to anthropogenic
actions that result in emissions or
sequestration.
Anthropogenic. This definition has
been moved from the Glossary to the
General Guidelines and has been
modified to more closely parallel the
definition of this term under the Climate
Leaders and Climate VISION programs.
Avoided emissions. The definition of
this term has been modified to enable it
to encompass more types of ‘‘avoided
emissions’’ in the future. Its practical
scope is still strictly limited by the
reduction calculation methods
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specifically identified and permitted
under the guidelines. As modified, the
term encompasses any emission
reduction that occurs outside an entity’s
boundary that results from changes in
the activity of an entity, but in practice
avoided emissions is still strictly
limited to the emissions displaced by
increases in the distribution of various
types of energy that have been derived
from renewable, nuclear or other low or
non-emitting sources.
Carbon dioxide equivalent. A
definition for this term has been added
to the General Guidelines.
Carbon stocks. The definition of this
term has been slightly modified to
clarify its scope in the context of these
guidelines, as suggested by public
comment.
Climate Leaders and Climate VISION.
The definitions of these programs have
been modified and moved to the
General Guidelines.
Direct emissions. The definition has
been modified to link such emissions to
sources within the organizational
boundaries of reporting entities.
Distributed energy. A definition for
this term has been added to the General
Guidelines. The term ‘‘exported
energy,’’ sometimes used in the interim
final guidelines, is no longer used.
The definition for ‘‘entity-level
reporting,’’ which previously appeared
in the Glossary, has been deleted.
The definition of ‘‘entity statements’’
that appears in the Glossary has been
deleted. The meaning of the term
‘‘Entity Statements’’ is fully described in
section 300.5(d) and (e).
Greenhouse gases. The definition has
been modified to more clearly identify
the gases that may be the subject of
reports under the guidelines.
Incidental lands. A definition for this
term has been added to the General
Guidelines.
Indirect emissions. The definition for
this term has been modified to parallel
similar modifications made to the
definition of ‘‘direct emissions.’’ The
definition of ‘‘emission, indirect’’,
which appears in the Glossary, is
repetitive and has been deleted. While
the indirect emissions are currently
limited to those associated with the
generation of energy by another entity
that is ultimately used by the reporting
entity, the definition leaves open the
possibility that other types of indirect
emissions may be added in the future.
Intergovernmental Panel on Climate
Change (IPCC). The definition for the
IPCC that appears in the Glossary has
been modified in response to comments
received.
Net emission reductions. This refers
to the sum of all reductions in a given
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year that qualify for consideration as
registered reductions. It has been only
slightly modified to improve its clarity.
Offset. The definition has been
modified to improve its clarity.
Registration. A definition for this term
has been added to the General
Guidelines.
Reporting entity. A definition for this
term has been added to the General
Guidelines.
Sequestration. The definition has
been simplified, but its intended scope
remains broad.
Source. The definition has been
slightly expanded to emphasize its
broad scope.
Small emitter and large emitter.
Definitions for both of these terms have
been added to the General Guidelines.
Start year. The definition has been
simplified to improve its clarity, as
suggested by public comments.
Total emissions. The definition has
been modified to correct an error, as
suggested by public comments.
H. Start Year and First Reduction Year
The interim final General Guidelines
provide that reporters not intending to
register reductions can establish base
periods as early as the 1987–1990
timeframe identified in section 1605(b)
and can report reductions beginning as
early as 1991. However, the interim
final guidelines provide that entities
intent on registering reductions must
establish base periods of no more than
four years that end no earlier than 2002,
and may not register reductions that
were achieved prior to 2003.
DOE received a number of comments
on these provisions of the interim final
guidelines, most of which
recommended that entities be allowed
to report emissions and emission
reductions that occurred prior to 2002/
2003. Some commenters indicated that
they had made commitments under the
Climate Leaders or Climate VISION
programs that used base periods that
ended prior to 2002 and that they were
able to report the progress made toward
the achievement of these commitments
prior to 2003. In response to these
comments, DOE has modified the
guidelines to permit entities that have
made a commitment to reduce entitywide emissions under the Climate
Leaders or Climate VISION to establish
base periods that end as early as 2000.
This exception would permit most, but
not all participants in these programs to
use the same base periods used in such
voluntary programs in their reports to
DOE under the 1605b program.
DOE believes that even with this
exception, the program will continue to
be focused on recent and future efforts
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to reduce greenhouse gas emissions and
consistent with providing an indication
of the reporting entities’ contributions to
the President’s goal of reducing
greenhouse gas emissions intensity of
the U.S. economy by 18 percent
between 2002 and 2012. The revised
General Guidelines still permit
reporting of historical activity, however,
and therefore fully comply with the
statutory requirements of section
1605(b).
I. Electricity Factors and Benchmarks
The interim final guidelines establish
several different kinds of emission
factors and benchmarks intended to
approximate the emissions associated
with electricity use, the emissions
avoided as a result of reduced electricity
demand, or the emissions avoided by
increasing generation from non-emitting
or low-emitting sources. For emission
inventories, the interim final guidelines
provide that entities should convert
their electricity demand to emissions
using factors supplied by DOE that
would be based on the regional averages
of electric sector emissions intensities.
DOE stated that entities should use
factors that were derived from the
national average emissions intensity of
the electric sector as a whole for
calculating reductions associated with
reduced electricity demand or increased
generation from non-emitting or lowemitting sources. DOE indicated that the
national average emissions intensity
was considered to be a better indicator
of the actual emissions likely to be
displaced by reduced demand or
increased generation.
Many commenters recommended
making the factors used for inventories
and for calculating reductions the same,
although some supported the DOE’s
rationale for proposing different factors.
Some advocated regional factors as
better indicators of the emissions and
reductions associated with specific
sources. Others advocated national
factors as good indicators of actual
emissions and reductions, and as a way
of simplifying the reporting burden of
entities that operated in multiple
regions. Some utilities recommended
that the benchmark used for estimating
avoided emissions be based on the
regional averages of fossil-fired
generating plants, which they argued
would be a better indictor of the
emissions being displaced. Other
utilities recommended that entities be
permitted to choose either a systemspecific benchmark, based on the
emissions intensity of marginal plants,
or a regional average.
After careful consideration of the
comments, DOE has adopted the
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recommendation of some utilities to
base the factors used to estimate the
emissions avoided by reduced
electricity demand or increased
generation from non-emitting or lowemitting sources on the regional average
emissions intensities of fossil-fired
generating plants, with the proviso that
no regional value may exceed 0.9 metric
tons of CO2 per megawatt hour (MWH).
The maximum value of 0.9 metric tons
per MWH is designed to ensure that all
utilities have a clear incentive to build
new capacity that is at least as efficient
as the most efficient coal-fired
generating plants. DOE chose not to
provide generators with the flexibility to
choose national or regional values, or to
develop their own, system-specific
values in order to avoid the significant
self-selection bias that would result
from such flexibility.
The definition of the U.S. regions to
be used in calculating the indirect
emissions associated with electricity use
and avoided emission benchmarks is an
important technical issue. In the draft
Technical Guidelines, DOE indicated its
intent to use North American Electric
Reliability Council (NERC) regions as
the basis for the indirect emission
factors used in preparing emission
inventories. Some comments suggested
that NERC subregions, especially for the
western United States would be more
appropriate. Others urged DOE to
consider the use of EPA’s eGRID
regions. In choosing among these and
other options, DOE considered whether:
(1) It would be possible to provide
meaningful values for all possible
reporting years (the earliest possible
reporting year is 1987) based on readily
available public data; (2) reporters
would be able to readily determine
which factor applied to specific
facilities or operations; and (3) the
resulting factors would provide a good
approximation of the indirect emissions
associated with electricity use or
demand reductions in a particular
region. After careful consideration, DOE
concluded that basing indirect emission
factors on either NERC or eGRID regions
would not achieve one or more of these
three objectives. For example, because
the NERC and eGRID regions cut across
state lines, it will likely be difficult for
reporters to determine which region is
applicable to a specific facility.
Consequently, DOE decided to base
these factors on the electric sector
emission intensities of state-based
regions that approximate the most
current NERC regions and, in the case
of the western United States,
appropriate subregions. The purpose of
these state-based regions is to
approximate the actual emissions
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associated with the electricity supplied
to users, while also utilizing data that is
readily available for all reporting years
and boundaries that are well recognized
by potential reporters. EIA will
determine the most appropriate State
groupings for the development of the
indirect and avoided emission factors
based on NERC regions and applicable
subregions, as defined in June 2006.
Generally, those states that are split
among two or more NERC regions or
subregions should be assigned to the
state grouping that contains most of the
state’s population. One possible
grouping that will be considered by EIA
is: (1) New York, Connecticut, Rhode
Island, Massachusetts, Vermont, New
Hampshire and Maine; (2) New Jersey,
Delaware, Pennsylvania, Maryland,
West Virginia, Ohio, Indiana and
Michigan; (3) Illinois and Wisconsin; (4)
Missouri, Kentucky, Virginia, Arkansas,
Tennessee, North Carolina, South
Carolina, Louisiana, Mississippi,
Alabama and Georgia; (5) Florida; (6)
Texas; (7) Oklahoma and Kansas; (8)
North Dakota, South Dakota, Nebraska,
Minnesota and Iowa; (9) Colorado, Utah,
Nevada, Wyoming and Montana; (10)
New Mexico and Arizona; (11) Oregon,
Washington and Idaho; (12) California;
(13) Hawaii; and (14) Alaska. EIA will
provide factors for 1999 and subsequent
data years and will periodically (e.g.,
every three to five years) update these
factors to reflect what they determine to
be significant and lasting changes in the
electric sector emissions intensity of the
established state groupings. EIA will
also provide a set of values to be used
for all data years prior to 1999.
Several comments focused on the
treatment of transmission and
distribution (T&D) losses in the
calculation of the factors used to
represent the emissions associated with
electricity demand (to be included in
emission inventories) and reductions in
electricity demand (to be included in
emission reduction calculations). Some
noted that T&D losses were not included
in the emission factors widely used by
the Climate Leaders program. Others
favored the inclusion of such T&D
losses in the factors representing
emissions associated with electricity
demand and reductions. DOE decided to
continue to include such losses in the
factors used to estimate both the
inventories and reductions associated
with electricity use. By including such
losses, these factors will provide a better
indicator of the emissions resulting from
electricity demand. Entities that wish to
include both generation and T&D losses
in their reporting of indirect emissions
to the Climate Leaders program may do
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so, as long as they note that their reports
include both types of losses, based on
the factors provided by DOE.
J. Inventories
The interim final guidelines provide
detailed guidelines for the conduct of
emission inventories. DOE received a
large number of comments that touched
on emission inventory guidelines in
some way. Most comments were
generally supportive of the framework
for emission inventories set forth in the
General Guidelines and the more
detailed provisions of the draft
Technical Guidelines. However, some
commenters raised concerns regarding
the start year and de minimis
requirements of the interim final
guidelines, while others suggested
various improvements to the methods
cited or the quality ratings assigned to
these methods.
In the final guidelines, an emissions
inventory is an accounting of an entity’s
actual emissions (direct, indirect and
sequestered) during a specified year. An
emissions inventory provides, by itself,
a useful record of an entity’s actual
emissions over time, but it also serves
as one of the inputs necessary for the
calculation of the base values used in
determining emission reductions. For
this reason, an emissions inventory is
usually a major element of an entity’s
first report under the program.
Since emission inventories are a
critical part of calculating emission
reductions, all reports under the revised
program should include some kind of
inventory. Entities that do not intend to
register reductions and small emitters
may restrict their inventory data to
those sources or activities that will be
the focus of future emission reduction
calculations. However, large emitters
that intend to register reductions must
submit entity-wide emission inventories
and may exclude from such inventories
only de minimis emissions. Any entity
that wishes to register reductions must
ensure that its annual inventories meet
the minimum quality requirements
specified in the guidelines.
The following sections summarize the
major comments that addressed the
emission inventory requirements of the
interim final guidelines and DOE’s
responses to the comments.
1. Requirement for Entity-Wide
Inventories With a Quality Rating of at
Least 3.0
The interim final guidelines
established a quality rating system for
emission inventories. Reporters could
choose among a range of different
methods for measuring or estimating the
emissions from specific sources. Each
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different method was assigned a rating
of A, B, C or D and each of these ratings
was assigned a numerical value from 4.0
(for A rated methods) to 1.0 (for D rated
methods). Entities that were intent on
registering reductions would be
required to complete emission
inventories that had a quantity-weighted
quality rating of at least 3.0.
Most comments received by DOE
supported the emphasis of the interim
final guidelines on quality entity-wide
inventories. The final rule retains the
requirement for a 3.0 quality rating for
the emissions inventories that large
emitters must submit as a prerequisite
for registering reductions. DOE believes
that methods given an A or B rating are
sufficiently accurate to serve as the basis
for entity-wide reporting, while
methods given a C or D rating should be
used only for those gases or sources that
represent a small share of the reporting
entity’s total emissions. Several
commenters suggested that the A and B
methods available for specific sources or
industrial sectors are too burdensome
and will make it difficult for some
entities to prepare inventories that meet
the 3.0 quality rating. DOE has made
some modifications to the ratings for the
available methods to ensure that a costeffective and practical A- or B-rated
method is available for every emissions
source.
As the table below demonstrates,
three very different companies with
diverse emission profiles could meet the
3.0 quality rating threshold using an
inventory approach specific to their
company. Company A is a large electric
utility, with a vast preponderance of
Emissions
metric tons
CO2e
Source
emissions attributable to stationary
fossil fuel combustion. As a result, this
company may use lower rated (and
lower cost) methods for estimating
emissions from its smaller sources, such
as fleet vehicles and sulfur hexafluoride
used as an insulator on transmission
lines. Similarly, a landfill operator
could achieve the quality-rating
threshold by ensuring that it uses ‘‘B’’
or better-rated methods for estimating
methane emissions from the landfill.
Company C, a large Federal defense
contractor, is able to offset its lower
rated estimates of emissions from
mobile sources with higher rated
methods for estimating emissions from
stationary combustion at its lone
manufacturing facility.
Method
grade
Emissions weighted grade
300,000
10,000
500
A=4
C=2
C=2
300,000*4 = 1,200,000
10,000*2 = 20,000
500*2 = 1,000
1,000
B=3
1,000*3 = 3,000
Total .............................................................................................................
311,500
3.92
1,224,000/311,500 = 3.92
Company B (Landfill Operator)
Direct Emissions:
Methane from Decomposition ............................................................................
Heavy Duty Vehicle Fuel Use ............................................................................
Indirect Emissions:
Electricity Consumption ......................................................................................
50,000
200
B=3
B=3
50,000*3 = 150,000
200*3 = 600
50
A=4
50*4 = 200
Total .............................................................................................................
50,250
3.00
150,800/50,250 = 3.00
Company C (Large Federal Defense Contractor)
Direct Emissions:
Vehicle Fuel Use ................................................................................................
Stationary Combustion at Manufacturing Facility ...............................................
Indirect Emissions:
Electricity in Commercial Offices ........................................................................
500
800
C=2
A=4
500*2 = 1,000
800*4 = 3,200
9,000
B=3
9,000*3 = 27,000
Total .............................................................................................................
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Company A (Large Utility)
Direct Emissions:
Stationary Combustion .......................................................................................
Fleet Vehicles .....................................................................................................
Sulfur Hexafluoride on T&D System ..................................................................
Indirect Emissions:
Electricity in Commercial Offices ........................................................................
10,300
3.03
31,200/10,300 = 3.03
DOE has modified the guidelines to
enable entities that obtain independent
verification to simplify their inventory
reports and to permit entities that certify
their use of only A or B methods to
forego the reporting or calculation of a
quantity-weighted quality rating.
Finally, DOE has made some clarifying
changes to emphasize that prior year
inventories may be modified only to
correct significant errors, and that
entities may choose at any time to
modify the methods used to prepare
their current and future year
inventories. DOE hopes that such
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modifications lead to improvements in
inventories over time.
2. De Minimis Exclusion From EntityWide Emission Inventories
Numerous comments proposed
changes to the provision of the interim
final General Guidelines that allows
entities to exclude from their entitywide emission inventories up to 3
percent of their total emissions. Many of
these commenters recommended that
entities be permitted to exclude up to 5
percent of their total emissions, while
others proposed to permit entities to
exclude certain types of sources
entirely, such as motor vehicles that are
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not an integral part of the production
process or small tracts of undeveloped
land. On the other hand, a number of
commenters requested that the de
minimis exclusion be removed from the
guidelines, and that all entities be
required to inventory all of their
emissions every year. Still others
recommended the use of some kind of
‘‘materiality’’ test to determine whether
or not certain emissions could be
excluded. After serious consideration of
all of these comments, DOE decided not
to make any change in the de minimis
provisions of the General Guidelines.
DOE believes that the 3 percent de
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minimis exclusion is appropriate
because a larger de minimis exclusion
risks ignoring sources that could affect
the assessment of entity-wide emission
reductions. DOE emphasizes that it will
be possible for entities to achieve an
overall 3.0 quality rating with limited
use of low cost, D-rated estimation
methods for small emission sources. A
major reason for the introduction of the
quality rating system is that it gives
entities the ability to complete
inventories that are more
comprehensive without incurring the
high costs of applying high quality
measurement methods to comparatively
small, dispersed sources. With respect
to land holdings, the guidelines do
provide for the exclusion of incidental,
forested lands, as long as they are not
actively managed for wood production
or otherwise developed.
3. Ratings for Estimation Methods Using
Default Values
The interim final Technical
Guidelines contain a rating system for
determining the quality of emission
inventories reported under the 1605(b)
program. Up to four methods are
identified and rated for measuring or
estimating the emissions from every
source, with the highest rating being an
A (worth 4 points) and the lowest a D
(worth 1 point). For each distinct
source, the ratings are ordinal—meaning
that the best method received an A
rating and the poorest method received
a D. Under the interim final guidelines,
this approach results in some very large
disparities between the ‘‘A’’ methods of
different sources. For some sources,
where field measurement methods are
not practical and estimation methods
are not well developed, a method that
relies on default factors is given an ‘‘A’’
rating because it is the best available
method. In other cases, such as forest
ecosystems, the use of well-researched
default factors rate a ‘‘C’’ or ‘‘D’’, unless
they have been validated by
independent data from the specific site
and management condition. These
disparities were the focus of a number
of critical comments.
In response to these comments, the
final guidelines have been modified to
restrict ‘‘A’’ ratings to methodologies
where computations are based primarily
on values indicative of on-site
conditions measured continuously or
over multiple periods. In cases where no
methodology qualifies for an A rating,
the best method will be rated ‘‘B’’ and
given a value of three points. Using this
approach, the best methods for certain
agricultural sources warrant only a B.
A related issue concerns the quality
ratings given methods that rely upon
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default factors that have been widely
reviewed and adopted by a public
agency, a standards-setting organization
or an industry group. The draft
Technical Guidelines could have made
it difficult for reporters in certain
industries to receive a 3.0 quality rating
or above, even though they utilized
methods and factors that were generally
accepted within the relevant industry as
being the most practical and effective
means of estimating emissions from
certain sources. For example, in many
cases, the draft technical guidelines
provided a C rating for widely accepted
default factors, even though sourcespecific emission measurements would
be very costly or impractical. To correct
this problem, the final guidelines raise
certain consensus-based default factors
to ‘‘B’’ ratings where more accurate
methods are not considered costeffective and where the default factors
have been established by an industrywide peer review process, with public
documentation.
4. References to Continuous Emissions
Monitoring Systems (CEMS)
A number of commenters pointed out
that CEMS are not practical for many
industrial applications. For such
applications, mass balance or default
emission factors may be the only
practical options. In the oil and gas
exploration and production industry, for
example, estimating emissions by using
measured activity data and emission
factors available through government
(AP–42, available at: https://
www.epa.gov/ttn/chief/ap42/) or
industry (API Compendium, available
at: https://api-ec.api.org/policy/
index.cfm?objectid=C79E99D5-E714–
40ED–81C8C32F1492851C&
method=display_body&er=1&
bitmask=001001004001000000)
approved methodologies is the most
accurate method available and warrants
a high rating.
If CEMS are used, albeit rarely, for a
particular source, direct measurement is
kept in the final guidelines as an Arated option, while other methods for
this source that use mass balance or
default emission factors methods are
also given an ‘‘A’’ rating, as long as they
are derived from site-specific
measurements.
5. Citations of Protocols and Emission
Factors Developed by Other
Organizations
The interim final guidelines include
citations to several other protocols or
standards, and include a number of
emission factors drawn from such
protocols or standards. Numerous
comments noted that some of the
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documents and emission factors cited in
the guidelines had not been
subsequently updated. Many of these
comments recommended that DOE
update these citations and some
recommended that DOE’s guidelines
direct reporters to use future updates of
such protocols or standards, as they
become available.
The final guidelines do include a
number of updated references and
emission factors, as recommended by
commenters. In addition, they direct
reporters to use the most current
methods established by specified
government agencies (EPA, USDA) or
independent standards-setting
organizations (IPCC) and direct EIA to
periodically update forms/instructions
to reflect such methods/factors. With
regard to methods in other sources, the
final guidelines provide that DOE will
review and update, as appropriate, the
guidelines periodically and in response
to specific requests.
6. Options for Simplifying Emission
Reports
A number of entities expressed
concerns regarding the potential
burdens of reporting detailed, entitywide inventories and a few suggested
options for reducing these burdens. In
the final guidelines, DOE provides for
two approaches that will enable entities
to reduce the detail of the reports
submitted to DOE. First, if an entity
certifies that it has used only A or B
rated emission inventory methods, it
need not calculate or report the
quantity-weighted average quality rating
of its emissions inventory. When
accepted, EIA will indicate in the
database that the quality rating of the
inventory meets or exceeds the 3.0 level.
Second, if an entity has its report
independently verified, including the
quantity-weighted quality rating of its
inventory, it may report its inventory
data at a higher level of aggregation (by
greenhouse gas, rather than by source
category).
7. Eliminate Requirements To Report
Emissions From Biogenic Sources and
To Report Certain Non-Fuel Uses of
Fossil Fuels
The interim final guidelines require
the reporting of many uses of fossil fuels
and a determination of whether a nonfuel use of a fossil fuel involves a
sequestering, non-sequestering, or
partially sequestering activity. The
interim final guidelines also require the
reporting of certain biogenic emissions,
such as the carbon dioxide emitted by
combusting ethanol in vehicles. To
reduce the burdens of reporting, the
final guidelines require reporters to
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report only anthropogenic emissions of
greenhouse gases. Entities should not
report biogenic emissions or nonemitting uses of fossil fuels, such as
fuels used to create materials used to
manufacture products.
8. Treatment of Agriculture and Forestry
The draft Technical Guidelines would
provide extensive new methodologies
for estimating greenhouse gas emissions
and carbon sequestration from the forest
and agriculture sectors. A number of
commenters expressed appreciation for
the improvements in the draft
guidelines, noting specifically the
benefit of the COMET model for
estimating changes in carbon stocks on
agricultural soils and new advances in
estimating forest carbon. Several
comments proposed improvements in
the technical methods and underlying
coefficients and data. Some commenters
expressed concern that the methods
proposed were too complex and
detailed. Other commenters maintained
that the methods were not adequate and
included significant uncertainties that
would limit their use under a potential
future regulatory system.
USDA and DOE reviewed the
inventory methods for forestry and
agriculture in light of these comments
and made changes where appropriate to
reflect new information. The review
noted that relatively simple inventory
methods are available for virtually all of
the sources and sinks in the agriculture
and forest sectors. The availability of
methods for all greenhouse gas emission
sources and carbon sinks was important
to enable entities to provide
comprehensive entity-wide inventories.
The review also noted that alternative
methods are provided for many sources
and that these alternative methods vary
from the simple to the complex. The
complex methods generally provide
entities with the ability to reduce
uncertainties. For some agricultural
sources, the guidelines only provide
simple default methodologies. In the
draft guidelines, these methods were
given an ‘‘A’’ rating. In the final
guidelines, these methods are given a
‘‘B’’ rating. The explanation for these
changes is explained in section J.3.,
above.
a. Sustainable forest management.
Provisions of the draft Technical
Guidelines would allow entities to
report a default carbon flux value of
‘‘zero’’ for forestlands that are verified
through third-party certification as
being sustainably managed. DOE
received comments questioning the
credibility of certain sustainable forest
certification systems and the
assumption that it is ‘‘highly unlikely’’
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that carbon stocks decline in sustainably
managed forests. Other comments
agreed with this assumption and
recommended that § 300.6(g)(1) be
modified to clearly state that any
changes in sequestration for forests
managed under certified sustainable
management systems are de minimis
and need not be a part of entity’s annual
report.
The USDA Forest Service reviewed
four existing certification systems and
determined that while there are some
differences among the major
certification programs in their goals and
technical details, all of the programs set
high standards, have rigorous thirdparty audit protocols, are generally
viewed as credible by many stakeholder
groups, and can assure (with reasonable
confidence) long-term carbon neutrality.
Therefore, the final guidelines specify
that any changes in sequestration for
forests managed under certified
sustainable management systems need
not be part of an entity’s annual report.
All or part of an entity’s forest land can
be certified as being managed
sustainably. If an entity chooses to use
the assumption that sustainable forest
lands are de minimis on part of their
lands and report actual changes in
carbon stocks on other lands, the entity
should document that the certification
of sustainability applies to the lands
being considered de minimis,
independent of the entity’s other lands.
Once an entity classifies a portion or all
of its lands as sustainably managed
forest, it may not report carbon
sequestration on the lands categorized
as sustainably managed in future
reports. If a portion of certified land is
sold or loses its certification, these
changes must be reported to EIA and the
remaining land must either be
recertified or the entity must report
actual changes in carbon stocks on all
the affected land.
DOE received comments urging it to
eliminate provisions of the interim final
guidelines that require reporting of
carbon stock changes on forestlands.
These comments contend that the
sequestration accounting requirement in
§ 300.6(f) is complex, costly and
intrusive. The comments further
contend that detecting meaningful
periodic change in large forest
inventories is a daunting task, both
logistically and statistically, even for
entities with sophisticated commercial
timberland inventories.
No changes were made to the
guidelines in response to these
comments. The guidelines provide three
classes of methods to estimate changes
in carbon stocks from forests. The
guidelines provide default lookup
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tables, guidance on the use of models,
and procedures for applying sampling
techniques. In addition, the guidelines
allow land that has been certified by
third parties as being sustainably
managed to be considered de minimis
for reporting purposes. These options
provide sufficient flexibility to entities
in reporting changes in carbon stocks on
forested land that they own or control,
while maintaining consistency with
overall objectives of the program for
comprehensive reporting of greenhouse
gas emissions and sinks. DOE notes that
the guidelines do not require entities to
continue to account for changes in the
carbon stock that occur on land no
longer owned by the entity, although the
entity must ask EIA to remove from its
records any carbon stock increases (or
decreases) that were attributed to such
lands in prior year reports.
b. Wood products. DOE received
comments regarding the allocation of
carbon embedded in wood products. In
particular, commenters noted that
manufacturers should be provided the
option to register the carbon embedded
in products and treat it as carbon
sequestration. Under the interim final
guidelines, forest landowners are
responsible for reporting carbon
emissions from wood products. The
forest land owner can simply assume
that the carbon embedded in products,
such as building materials, is emitted
when harvested or use one of the
methods provided to estimate rates of
emissions from such wood products
over time. Allowing the manufacturer of
wood products to treat the
manufacturing process as a
sequestration activity would require that
the forest land owner treat the
harvesting activity as an emission. The
broader implication of this interim final
guideline provision is that all transfers
(sales of wood products) would need to
be tracked and reported by entities as
either emissions or sequestration. DOE
and USDA viewed this option as overly
complex and one that would require a
significant amount of additional record
keeping and reporting. The final
guidelines maintain the original
provisions for the reporting of carbon
embedded in wood products.
c. Inclusion of forest sequestration.
One commenter recommended that
terrestrial sequestration be removed
from the inventory guidelines for large
entities. They asserted that by requiring
large entities to report changes in
terrestrial carbon stocks, the guidelines
place the federal government squarely
in the middle of private land use and
property rights issues, and establish
complex, costly, and intrusive
regulatory burdens for no apparent
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benefits in terms of carbon
sequestration. This comment was not
adopted. DOE believes that the proposal
would undermine the entire objective of
encouraging comprehensive reporting. It
is important to note that the program is
voluntary, not mandatory. Also, the
program places no legal restrictions on
landowners regarding carbon
sequestered on their lands, even if that
carbon has been reported to the 1605(b)
program.
d. Accelerated reporting of carbon
stock changes on permanently restored
land. Normally, entities may include in
their annual assessments of emission
reductions only those changes in
emissions or carbon stocks that occurred
during the year that is the subject of the
report. Comments recommended,
however, that entities be permitted to
accelerate the reporting of carbon stock
increases on land that was being
reforested, especially if it was to be
permanently restored and protected.
Because of the very long term carbon
sequestration and other benefits
associated with such permanent
restoration and protection, DOE has
modified the guidelines to permit
entities that have undertaken such a
restoration project and established a
permanent easement or deed restriction
to protect the land to report, during the
next reporting cycle, carbon stock
increases that are equal to 50% of the
total carbon stock increases expected on
that land over the next 50 years. The
50% discounting of the 50-year carbon
stock increases closely approximates the
present value of a 50-year stream of
annual benefits discounted at a rate of
3 percent per year. The sequestration
occurring on such lands would still
have to be reported as part of the
entity’s annual emissions inventory, but
would be excluded from all future
assessments of emission reductions.
9. Stationary Source Combustion
Several changes to the ‘‘Stationary
Source Combustion’’ part of the
inventory guidelines were made in
response to comments. Some were
motivated by a desire to simplify the
reporting process or render it more
accurate. For example, the draft
Technical Guidelines would have
required entities to identify and report
emissions from non-fuel use of fossil
fuels. Several commenters felt that the
requirement placed too great a burden
given the small amount of potential
emissions involved. While DOE has
modified the guidelines to indicate that
biogenic emissions and non-fuel uses of
fossil fuels need not be reported, the
final guidelines continue to require the
reporting of all emissions for which
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measurement or estimation methods are
identified. The draft Technical
Guidelines would have required that
combined heat and power (CHP) plants
assume an 80% thermal generating
efficiency. The final guidelines follow
the World Resources Institutes and
World Business Council for Sustainable
Development (WRI/WBCSD)
Greenhouse Gas Protocol of allowing
plants to enter their own estimated
efficiency values. Also, the draft
Technical Guidelines would not provide
for the registering of avoided emissions
associated with the use of coal
combustion products. The final
guidelines recognize fly ash use through
an action-specific method.
Some changes were made to make the
rating system for methods used to
measure stationary combustion
emissions compatible with the new
procedure outlined above. The mass
balance approach was raised to an ‘‘A’’
status for emissions from hydrogen
plants and certain non-CEMS methods
were given the same rating or raised to
a ‘‘B’’ if based on regular site-specific
measurements and fuel use default
values derived through a consensus
process. Some suggested changes, such
as the proposal to treat methane from
landfills as a biogenic emission, were
not accepted. Here the wording of the
draft Technical Guidelines was retained
because DOE views the emissions of
methane from landfills as
anthropogenic. Only the CO2 emissions
from the combustion of landfill methane
is treated as biogenic.
One commenter sought clarification
on the exclusion from entity-wide
inventories of carbon dioxide emissions
from biomass combustion. Another
wanted to ensure that non-combustion
biomass oxidation was also excluded
from entity-wide inventories. The DOE
has revised the Technical Guidelines to
clearly confirm the exclusion of these
biogenic emission sources.
10. Mobile Sources
One major change in the ‘‘Mobile
Sources’’ part of the inventory
guidelines was made in response to
comments that specific emission factors
were outdated, according to the most
recent government or private industry
publications. DOE has updated many of
these emission factors and has revised
the guidelines to provide that reporters
and EIA should use to develop their
inventories future updates to factors
made by certain government agencies or
consensus-based standards
organizations. However, the final
guidelines do not provide for the
automatic updating of factors developed
by trade groups or other industry
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20795
sources, such as the American
Petroleum Institute’s Compendium of
Greenhouse Gas Emission
Methodologies. DOE will consider
updates of such industry-developed
values during DOE’s planned periodic
updates to the guidelines.
Another suggestion made by
commenters was to exclude vehicles
unless they were ‘‘integral to
production.’’ Several commenters state
that it is overly burdensome for
emission inventories to include mobile
source related emissions where mobile
sources are not an entity’s dominant
greenhouse gas emitting activity. DOE
disagrees with the comment that mobile
sources should be excluded. While
mobile source emissions may be a small
share for many reporters, they may be
large in absolute terms, and they are a
substantial source of emissions for some
entities. Therefore, the final guidelines
continue to require inventories to
include all vehicles within the
organizational boundaries defined by
the reporting entity, which would
normally include all vehicles that are
owned or under the financial control of
the entity. DOE notes that under the
final guidelines, entities are permitted
to exclude such emissions as de
minimis if they are less than 3% of total
emissions.
DOE received comments requesting
clarification on the effect on inventory
quality ratings of using default emission
factors versus measured data on heat
content, density, or carbon content of
fuel data for mobile source emissions.
The draft Technical Guidelines have
been revised to provide such
clarification.
11. Industrial Processes
Some of the same issues that arose in
the Stationary Source Combustion and
Mobile Sources parts of the guidelines
also appeared in the comments on the
Industrial Processes part. Several
commenters pointed out that CEMS
methods are not appropriate or practical
for many industrial applications
because of cost considerations. After
considering these comments, DOE has
dropped CEMS as an ‘‘A’’ method for
some industrial sources, and elevated
the rating of other methods. The final
guidelines allow direct measurements
(for mass balance or default factors) an
‘‘A’’ rating if they are based on sitespecific, periodic measurements.
Several comments on this part of the
Technical Guidelines also urged DOE to
use the most recent emission factors
established by other government,
consensus or industry protocols. These
factors have been updated and the final
guidelines provide that values from
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government agency or consensus-based
sources will be automatically updated
by EIA, while updates contained in
industry-developed protocols will be
considered during DOE’s periodic
updates to the guidelines.
The National Lime Association (NLA)
recommended that the guidelines adopt
its method for estimating CO2 emissions
from lime production. The NLA asserts
that its method is more accurate because
it relies on the specific characteristics of
the lime produced (calcium oxide and
magnesium oxide content) rather on
default values for different classes of
lime. DOE agrees and has adopted the
NLA method for the ‘‘A’’ rated method
for estimating CO2 emissions from lime
production.
One commenter from the pulp and
paper industry requested that a
statement be added to the guidelines
indicating that the emissions from the
manufacture of lime in the Kraft pulping
process are biogenic and that emissions
from this source should not be included
in emission inventories. The pulp and
paper mill module prepared under the
auspices of the Climate Change Working
Group of the International Council of
Forest and Paper Associations (ICFPA),
which has been adopted by the WRI/
WBCSD Greenhouse Gas Protocol
Initiative, states that ‘‘the carbon
released from CaCO3 is biomass carbon
that originates in wood and should not
be included in GHG emissions totals.’’ 1
DOE agrees with this recommendation
and has added the appropriate language
to the Industrial Process Emissions part
of the Technical Guidelines (Section
1.E.3.3).
The industry trade group noted the
absence of methods for estimating
methane emissions from petrochemical
production and DOE has added these
methods to the Industrial Process part of
the Technical Guidelines.
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12. Indirect Emissions
The treatment of indirect emissions
under the interim final guidelines was
the subject of a number of comments.
Some expressed concern about the
mixing of indirect and direct emissions
and reductions. In response to these
comments, DOE has modified the
guidelines to emphasize that indirect
emissions must be reported separately
from direct emissions in inventories,
although they are added together to
determine the total emissions of a
reporting entity. Direct and indirect
1 National Council for Air and Stream
Improvement, Inc. (NCASI), Calculation Tools for
Estimating Greenhouse Gas Emissions from Pulp
and Paper Mills, The Climate Change Working
Group of The International Council of Forest and
Paper Associations, Version 1.1, July 8, 2005, p. 23.
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emissions are often combined in a single
emission reduction calculation formula,
but emission factors used for indirect
emissions ensure that there is no
double-counting by electricity
generators and users.
Some comments were directed at the
emission factors used to calculate the
emissions associated with electricity
use. Although some comments
suggested that these emission factors
exclude the losses associated with
electricity transmission and distribution
(T&D) losses, the final guidelines
continue to include these losses because
they provide a better indication of the
total emissions avoided by reductions in
electricity consumption.
Some commenters suggested that the
owners of electricity T&D systems be
required to include in their emission
inventories the indirect emissions
associated with T&D system losses.
Because such indirect emissions would
overlap with the direct emissions of
some entities (that both generate and
distribute electricity) and because T&D
system losses are often associated the
transmission of power from one system
to another, DOE has decided not to
require the indirect emissions
associated with T&D system losses to be
included in the inventories of owners of
electricity T&D systems at this time.
However, if an entity chooses to report
(or register) the emission reductions
associated with its efforts to reduce such
losses, then it must calculate such
reductions based on a system-wide
assessment, as specified in the actionspecific method provided for this
purpose in the Technical Guidelines.
13. Geologic Sequestration
Geologic sequestration is still an
emerging field with few generally
recognized standards for accounting and
monitoring. As a result, several
comments requested that DOE clarify
and/or add information to the interim
final guidelines and regularly review
work by other governments and
organizations for relevant guidance.
Recognizing that this is a rapidly
developing and changing field, DOE
will continue to monitor the
development of new accounting
standards for geologic sequestration
and, whenever appropriate, revise the
reporting guidelines accordingly. DOE
also has clarified the inventory guidance
for geologic sequestration in the final
Technical Guidelines. For example, in
response to a request that naturally
occurring carbon dioxide emissions
near, but unrelated to, an enhanced oil
recovery field should be excluded from
an entity’s inventory, DOE added text
specifically stating that entities may
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exclude emissions of CO2 that have been
demonstrated to be naturally occurring.
Only emissions caused by the entity
itself should be addressed in the
inventory.
The monitoring approaches for
geologic sequestration in the draft
Technical Guidelines were the subject
of a number of comments. One
commenter argued that to avoid
excessive monitoring, entities should be
able to use technical, site-specific
monitoring approaches developed in
response to rules by relevant regulatory
agencies. Accordingly, DOE has added
text to permit other monitoring plans
that have been agreed to by a relevant
Federal or state agency, if these plans
have specific provisions for tracking the
amount of carbon dioxide being rereleased from the storage site.
Another commenter objected to the
requirement that reporters assume that
all stored carbon dioxide will be reemitted to the atmosphere and to
include all such future emissions in the
current inventory year. According to
this commenter, reporters have enough
understanding of reservoir
characteristics to generate a reasonable
prediction of future losses.
In October 2005, the
Intergovernmental Panel on Climate
Change (IPCC) published its Special
Report on Carbon Dioxide Capture and
Storage, which includes a
comprehensive discussion of available
monitoring techniques for geologic
sequestration. Noting that all monitoring
options recommended by the IPCC are
based on site monitoring, DOE revised
the final guidelines to also require sitespecific monitoring to be an element of
any acceptable method. For entities that
do not wish to report reductions
associated with geologic sequestration,
DOE has retained the requirement that
they assume that all injected carbon
dioxide will be reemitted over time and
report such emissions in the current
year. However, if an entity wishes to
report reductions associated with
geologic sequestration, they must use a
method that includes an active
monitoring component, as required in
the final guidelines.
K. Reductions
The interim final guidelines identify
five categories of methods for
calculating emission reductions:
emissions intensity, absolute emissions,
changes in carbon stocks, avoided
emissions and action-specific methods.
They also specify the use of an
integrated method—combining
emissions intensity and avoided
emissions—by electricity and other
generators of distributed energy that
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were increasing the quantity of energy
they had generated and exported to
other entities.
DOE received a large number of
comments on its guidelines for
calculating emission reductions, some
of which raised broad concerns. One
commenter urged DOE to focus
emission reductions calculations on
either emissions intensity or absolute
emissions, and to exclude emission
reductions resulting from increases in
carbon stock, energy-related avoided
emissions or other action-specific
methods until a comprehensive project
accounting framework is established.
On the other hand, a number of other
commenters urged DOE to retain and
expand the provisions for recognizing
reductions from sequestration, avoided
emissions and additional action-specific
methods. While DOE agrees that most
reporters can and should rely primarily
on emissions intensity or absolute
emissions methods to assess annual
changes in their emissions, we also see
a need for the retention of other
emission reduction calculation methods
in order to permit the reporting and
registration of reductions associated
with certain special sources and actions.
A few commenters continued to urge
DOE to permit the registration of
reductions resulting from stand-alone
projects, especially when undertaken to
reduce emissions outside the
boundaries of the reporting entity (offset
reductions). Other commenters,
however, supported DOE’s emphasis on
an assessment of entity-wide emission
trends, rather than on the results of
individual projects. While DOE
recognizes that entities are undertaking
a wide range of actions that can reduce
its emissions of greenhouse gases, DOE
believes that the enhanced program, to
be consistent with the objectives
established by the President’s Global
Climate Change Initiative of February
2002, should focus on the net result of
such actions on an entity’s overall
emissions and sequestration, and its
contribution to the goal of reducing the
nation’s emissions intensity. Therefore,
DOE has not changed the requirement
that large emitters calculate their
registered reductions on the basis of an
entity-wide assessment. It has, however,
modified the guidelines to permit the
reporting and registration of additional
types of action-specific reductions, and
to emphasize that all reporters have the
option to continue to report, but not
register, the emission reductions
resulting from a wide array of actionspecific efforts.
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1. Selecting Appropriate Reduction
Calculation Methods
The interim final guidelines
emphasize that entities must choose
among the five categories of reduction
calculation methods identified in the
guidelines. Some of the public
comments received by DOE indicated
that there was some confusion regarding
the degree of choice available to
individual reporters. DOE provides the
following guidance to clarify how it
views reporters’ selection of calculation
methods under the final guidelines. The
appropriate calculation methods a
reporter uses should be determined
largely by the characteristics of the
reporting entity and its emission sources
and sinks. Most reporters will find it
advantageous, where feasible, to use an
emissions intensity metric as the basic
calculation tool for determining the
emission reductions achieved by most
or all of the entity. Changes in absolute
emissions may be used as an alternative,
as long as the economic output
associated with the emissions is not
declining. If output is flat or increasing,
the reductions calculated using the
absolute emissions method should
always be equal to or less than the
reductions calculated using an emission
intensity method. For all terrestrial
sequestration, entities should assess the
annual changes in carbon stock. Entities
that generate electricity, steam, hot or
chilled water for distribution to other
entities should use the energy-related
avoided emissions method or the
integrated method to assess the
reductions associated with such
generation. Finally, entities should use
the action-specific methods only in
situations specifically addressed by the
methods provided in § 300.8(h)(5), or
situations where no other methods are
applicable.
2. Base Periods and Base Values
The interim final guidelines describe
how entities should establish and use
base periods and base values in the
process of calculating and reporting
emissions reductions. They also define
the circumstances that might require
some entities to adjust their base values
or, under certain circumstances,
establish new base periods and base
values.
In all cases, the final year of the
chosen base period must immediately
precede the first year of reported or
registered reductions. Some commenters
suggested that entities be permitted to
establish base periods that ended one or
more years prior the first reduction year.
DOE did not adopt this suggested
change because it believes that all
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reductions should be based on an
uninterrupted record of emissions from
the base period onward.
Several commenters expressed
concerns about the provisions covering
revisions to base periods, base values,
and methods due to boundary changes,
such as acquisitions, divestitures,
mergers, and the outsourcing or
insourcing of emissions-producing
operations. Some commenters argued
that assigning a different base period for
acquired operations other than that used
by the original entity would impose a
significant administrative burden for
some reporters. Other commenters
suggested that requiring an entity to
adjust its base value to include the
emissions of an acquisition would make
that entity responsible for any changes
in the acquisition’s emissions that had
occurred between the base period and
the year of acquisition.
DOE has retained a degree of
flexibility in the final guidelines
regarding whether an entity must
recalculate base values and change base
periods. The Technical Guidelines
establish some general principles in
section 2.3.3 regarding whether and
how base values and base periods
should be adjusted to reflect boundary
changes. However, a reporting entity
may incorporate a new acquisition into
an existing base value only if the
reporting entity has all of the required
emissions and other data for the
established base period. If this historical
data do not exist, the reporting entity
must establish a new base period for the
acquired subentity. Whenever base
values and base periods are adjusted,
the reporting entity must include a
discussion of the rationale for the
adjustment in the report it submits to
EIA.
Several stakeholders expressed
concern that they will be required to
recalculate reductions and resubmit
prior year reports to reflect boundary
changes. DOE has clarified § 300.8(f) of
the final rule to indicate that
resubmission of previous years’ reports
revised to reflect boundary changes
occurring in subsequent years is not
required. In general, the final guidelines
provide that previously reported or
registered emission reductions may not
be altered unless such an alteration is
necessary to correct a significant
reporting error.
One stakeholder proposed providing a
grace period of 18 months before a
reporter is required to adjust base values
or base periods to reflect a boundary
change to allow time for emissions
accounting systems to be reconfigured.
DOE recognizes that such boundary
changes can pose significant problems
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for reporters regarding the integration of
emissions accounting systems and,
therefore, it has amended the guidelines
(section 300.5(g)) to provide for a grace
period of at least 18 months before such
changes must be reflected in 1605(b)
reports. For boundary changes occurring
after May 31 of a particular calendar
year, base values would not have to be
adjusted until the report that is
submitted for the following calendar
year. For example, for an acquisition
made after May 31, 2005, a reporter
would not be required to make any
adjustments to its base value or values
until it reports on its 2006 activities.
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3. Enabling Reporters To Choose More
Stringent Base Values
One commenter requested that DOE
allow reporters to establish base values
that are more stringent than those
derived from historical performance.
While it is unlikely that many reporters
would take advantage of such flexibility,
DOE concedes that using a more
stringent base value could be desirable
under some circumstances (e.g., where
another voluntary program establishes
an emission reduction target based on
improvements compared to an industrywide benchmark). Therefore, DOE has
revised the guidelines to permit
selection of a more stringent base value,
provided the reporter demonstrates that
the base value is indeed more stringent
than that required by the relevant
method specified by the guidelines.
4. Emissions Intensity
In 2002, the President set a goal of
reducing U.S. emissions intensity by 18
percent in 2012, relative to 2002.
Establishing methods for tracking the
contribution that individual entities are
making to this national goal is one of the
key objectives of the revised guidelines
for the 1605(b) program. Thus, the
interim final General Guidelines and
draft Technical Guidelines define a
method for calculating emission
reductions based on declines in
emissions intensity.
Most comments were generally
supportive of the guidelines for
calculating reductions based on
emission intensity, including the
flexibility to use either physical or
monetary methods for calculating
reductions. Some commenters, however,
opposed the registration of reductions
based on declining emissions intensity
because it would permit entities with
rising output to qualify for registered
reductions even though their net,
absolute emissions might be increasing.
Others pointed out that since most
industries experienced declining
emissions intensity over time, as a result
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of technological and productivity
improvements, emission reductions
derived from declines in emissions
intensity do not necessarily reflect any
new efforts to reduce emissions by the
reporting entity. Still others appeared to
oppose such reductions because they
implicitly exclude reductions
attributable to declining output. After
considering the comments, many of
which raised some valid concerns, DOE
has nonetheless concluded that
emissions intensity remains the best
approach to measuring emission
reductions because it avoids adverse
economic impacts on entities. DOE also
has concluded that the basic
methodology set forth in the interim
final guidelines is valid.
5. Absolute Emissions
The interim final guidelines provide a
method for calculating reductions from
declines in absolute emissions, as long
as the output associated with these
emissions had not declined. The
requirement for output to be level or
increasing was the focus of most of the
comments received on these provisions
of the guidelines. Some companies
stated that this requirement would
prevent them from registering
reductions that were recognized under
other reporting programs. Several
companies also raised concerns about
the apparent exclusion in the draft
inventory guidelines of emission
reductions associated with plants or
other facilities that are closed.
Since a key objective of the revised
program is to give special recognition to
reductions that contribute to the
national goal defined by the President,
DOE has retained the provision that
permits the registration of reductions
calculated using the absolute emissions
method only if the economic output
associated with such reductions is not
declining. However, since some plant
closings can contribute to reduced
emissions intensity or to declines in
absolute emissions, even if the output of
an entity is stable or increasing, DOE
has struck the language in the inventory
guidelines that appeared to exclude
such emission reductions from the
reductions calculation. In addition, DOE
has modified the guidelines to more
clearly permit entities to report (but not
register) absolute emission reductions
when output is declining.
One entity suggested that DOE permit
entities to adjust the base value used in
calculating absolute emission
reductions to reflect the prior year
emissions of acquisitions, even if the
data available for the acquired entity
does not match the base period used by
the reporting entity. DOE has not
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accepted the suggestion because it
would lead to base values that were no
longer tied to specific base periods. In
such circumstances, an entity should
establish a new sub-entity to account for
each acquisition. The new sub-entity
could have its own unique base period
and base value.
6. Changes in Carbon Stocks
The draft Technical Guidelines allow
entities to register 1/100th of the base
year/base period carbon stocks on
preserved forestland plus any
incremental carbon stocks gained in the
reporting year. Comments received on
the draft guidelines were critical of this
provision, citing it as arbitrary and
stating that only increases (or decreases)
in existing carbon stocks should be
eligible for registration; that an
easement in and of itself is not an
adequate basis for assessing avoided
emissions; and that the approach is not
scientifically valid.
In response to these comments, USDA
conducted a further review of this
provision and has determined that
preserved forests are not static with
respect to carbon stocks. Vegetation
growth and mortality will occur, and the
balance between those two factors will
determine whether the net carbon flow
is positive or negative. Preserved forests
are likely to be affected by natural
disturbances that affect growth and
mortality rates, and, therefore, carbon
stocks can be altered both positively and
negatively by such changes. USDA also
concluded that there is no technical
basis for the registration of 1/100th, or
any fraction, of the base period carbon
stocks in preserved forests. DOE has
eliminated from the final guidelines the
provision providing special treatment of
forest preservation. Entities reporting
and registering forest preservation
should follow the methods described in
section 1.I.2 of the Technical
Guidelines.
Another commenter expressed
concern that DOE had not made a clear
enough distinction between increases in
carbon sequestration and emission
reductions achieved through other
forestry-related activities. Detailed
methods for calculating changes in
carbon storage as well as methods for
calculating emission reductions from
other forestry-related activities are
included under individual sections of
the Technical Guidelines. The
distinction between these multiple
methods of reducing atmospheric
carbon loadings is included in multiple
sections of the General Guidelines and
most specifically in Part I of the
Technical Guidelines.
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7. Avoided Emissions
The interim final guidelines provide a
method for calculating the emissions
avoided by generating electricity, steam,
or hot/chilled water from non-emitting
or low-emitting sources of energy and
distributing these secondary forms of
energy to users. To estimate the quantity
of emissions that would be avoided by
the distribution of electricity generated
from non-emitting or low-emitting
sources, the draft Technical Guidelines
used a ‘‘benchmark’’ value based on the
average emissions intensity of the U.S.
electricity generating sector,
approximately 0.6 metric tons of CO2
per megawatt hour (MWH) of power
generated.
Numerous comments were received
on the avoided emissions method and
the benchmark value for distributed
electricity in the draft Technical
Guidelines. Several commenters noted
that the national average intensity of the
U.S. electricity generating sector is not
necessarily a good indicator of the
emissions avoided by the distribution of
non-emitting or low-emitting
generation. They stated that regional
averages of fossil-fired generation are
likely to be a better indicator, because
such averages exclude hydro-electric,
nuclear and other sources of power that
tend to be fully utilized, regardless of
changes in electricity usage or the
availability of other forms of generation.
DOE has decided to change the avoided
emissions benchmark for electricity to
the regional fossil-fired averages for the
electric sector, but the final guidelines
impose a maximum value of 0.9 metric
tons of CO2 per MWH. State-based
regions that approximate appropriate
NERC regions and subregions, together
the specific factors to be used by
reporters, will be specified by EIA. This
maximum value, which approximates
the average emissions intensity of fossilfired electric power generating plants in
the United States, will provide an
incentive for all utilities to build new
generating capacity at least as efficient
as the most efficient coal-fired
generating technologies.
Other commenters expressed
concerns regarding assignment of all
reductions associated with avoided
emissions to the generator, rather than
to the buyer or ultimate user. DOE has
not changed this aspect of the
guidelines, but it has attempted to
provide a workable mechanism by
which the generators of avoided
emissions can permit registered
reductions to be registered by buyers or
users, if they so choose.
Some commenters recommended that
DOE expand the concept of avoided
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emissions to encompass other areas
where conventional fossil-fuels are
being replaced by fuels generated from
low-emitting and largely renewable
resources. The interim final guidelines
provide an action-specific method for
recognizing the emissions avoided by
the productive use of methane
recovered from landfills. The final
guidelines provide additional actionspecific methods to recognize the
emissions avoided by the expanded
production of methane from anaerobic
digestion of waste at agricultural
facilities and wastewater treatment
plants. These methods are described in
more detail in the action-specific
methods section that follows. During the
development of these guidelines, DOE
also considered the possibility of
changing the treatment of ethanol used
in the transportation sector so as to shift
the recognition for the emission
reductions that result from increased
ethanol supply and use from vehicleowners to producers. Recognition of
producers might encourage such
companies to participate and report on
all of their emissions, including those
associated with ethanol production.
While the guidelines continue to
consider the emissions from ethanol
combustion as biogenic and the
responsibility of users, DOE may
reconsider the treatment of ethanol in
the future.
Several commenters also pointed out
that actions taken by an entity affecting
the emissions of one or more other
entities are not limited to the export or
import of energy products. These
commenters provided examples such as
the reuse of fly ash as a substitute for
Portland cement in concrete, which
displaces emissions from the
manufacture of Portland cement, and
post-consumer materials recycling,
which reduces emissions associated
with the manufacture of materials from
virgin resources. Many of these actions
are not conducive to the use of entitywide methods to estimate emissions
reductions. DOE has modified the
definition of ‘‘avoided emission’’ to
make it more clearly applicable to these
other types of avoided emissions, and it
has included an action-specific method
for estimating reductions associated
with fly ash reuse as a substitute for
Portland cement in concrete. DOE may
consider in the future additional actionspecific methods for estimating
reductions of indirect emissions from
such activities as manufacturing of
energy efficient products and increased
recycling of certain materials.
With respect to the increased
manufacturing of energy efficient
products, DOE may seek to develop
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methods capable of quantifying the net
emission reductions realized by very
small emitters as a result of the efforts
of some manufacturers to increase the
average efficiency of their products to
levels well above Federally-mandated
efficiency standards. Such very small
emitters are very unlikely to participate
directly in the 1605(b) reporting
program, so doublecounting of such
emission reductions would not be
likely.
For recycled materials, DOE may seek
to develop methods capable of
quantifying the net emission reductions
that result from increased use of
recycled materials in new products,
taking into account the full life cycle
emissions associated with production,
recovery, transport and reprocessing of
the affected materials, while also
ensuring that the double registration of
reductions associated with increased
recycling is prevented.
8. Action-Specific Methods
The interim final guidelines provide
for the use of action-specific methods
under a number of different
circumstances. A generic method is
provided that was designed to be used
in estimating the reductions that
resulted from a variety of different types
of actions, such as fuel switching or
efficiency investments. In addition,
several other methods included in the
interim final guidelines are designed to
estimate the reductions resulting from
specific types of actions, including
landfill gas recovery, coal mining gas
recovery, geologic sequestration, and
transmission and distribution losses. It
was DOE’s intent in the interim final
guidelines to permit reporters not
planning to register reductions to use
action-specific methods wherever they
are applicable. Reporters intending to
register reductions, however, are
permitted to use action-specific
methods only when none of the other
four methods are applicable. As a result
of this limitation, it was expected that
entities registering reductions would
generally use action-specific methods
only for sources or activities for which
they were specifically designed. In
general, entities were strongly
encouraged to report on an entity-wide
basis and use emissions intensity or
absolute emission methods as their
primary means of estimating their
reductions.
DOE received a large number of
comments on these provisions of the
interim final guidelines. Many of these
comments urged DOE to expand the
opportunities to register emission
reductions estimated using actionspecific (or project-based) methods.
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Several reporters argued that projectbased reporting should be an accepted
basis for registered reductions, noting
that project reporting is contemplated
by section 1605(b) and much of the
greenhouse gas emissions trading being
conducted in the U.S. is project-based.
Other comments urged the addition of
action-specific methods capable of
estimating reductions from other types
of actions, such as anaerobic digesters or
demand-side management programs.
The final guidelines retain the
provisions of the interim final
guidelines that strictly limit the use of
action-specific methods as the basis for
registered reductions, while not
restricting the use of other actionspecific methods by reporters not
interested in registering reductions. The
experience under the existing 1605(b)
reporting program has shown that the
relationship between individual projects
and an entity’s overall emissions is
ambiguous, because so many factors
other than emission reduction projects
conducted by the entity can affect these
emissions. DOE believes that allowing
registration of project-based reductions
would invite criticism similar to that
directed at the existing 1605(b) program,
namely that it allows entities to ‘‘cherrypick’’ activities that achieve emission
reductions while obscuring the overall
emission performance of the
organization. However, DOE recognizes
that data on project-level emission
reductions can be useful in
disseminating information on effective
ways to reduce emissions of greenhouse
gases, and DOE has clarified the final
guidelines to place more emphasis on
the two ways that reporters can
highlight individual actions that they
believe have contributed to their
improved greenhouse gas emissions
profile. First, they can quantify the
effects of specific actions or projects by
reporting, but not registering, reductions
using a reporter-defined action-specific
method; and, second, they can provide
anecdotal information regarding
emission reduction activities in the
summary description of actions taken to
reduce emissions required by § 300.8(i).
Section 300.8(h)(5) of the interim final
guidelines states that an entity-wide
reporter may use the action-specific
approach to estimate emission
reductions for actions within the
entities boundaries only if it is not
possible to measure accurately emission
changes based on changes in emissions
intensity, changes in absolute
emissions, changes in carbon storage, or
changes in avoided emissions as
outlined in section 300.8, paragraphs
(h)(1) through (h)(4). In the draft
Technical Guidelines accompanying the
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interim final General Guidelines, DOE
identified several specific actions for
which it will be difficult to accurately
measure emission reductions using the
methods in section 300.8 paragraphs
(h)(1) through (h)(4). They are: coalmine
methane recovery, landfill methane
recovery, geologic sequestration, and
transmission and distribution
improvements.
a. Integrating action-specific emission
reductions with other emission
reductions. Comments sought
clarification on the integration of actionspecific emission reductions with those
measured using methods set forth in
section 300.8, paragraphs (h)(1) through
(h)(4) of the interim final General
Guidelines. Entities may add actionspecific reductions to their net entitywide registered reductions if they meet
all other requirements of these
guidelines for registration and estimate
action-specific reductions using
methods contained in the Technical
Guidelines. Among the constraints the
final Technical Guidelines place on the
use of action-specific reductions are: (1)
The emissions affected by the action
may not appear in any other subentity
or entity-wide emission reduction
calculation submitted by the reporter;
and (2) emission reductions using this
calculation may not be reported by any
other entity on an entity-wide or subentity basis.
b. Expanding the range of actionspecific reductions. A number of
comments sought expansion of the
range of action-specific reductions.
Some commenters cited the language of
section 1605(b) that directs the
Secretary of Energy to establish
procedures for the accurate voluntary
reporting of information on annual
reductions of greenhouse gas emissions
and carbon fixation achieved through
any measures, including fuel switching,
forest management practices, tree
planting, use of renewable energy,
manufacture or use of vehicles with
reduced greenhouse gas emissions,
appliance efficiency, methane recovery,
cogeneration, chlorofluorocarbon
capture and replacement, and power
plant heat rate improvement. Elsewhere
in this Supplementary Information (see
II. C. above, on the distinction between
reporting under the program and
registering reductions), DOE addresses
comments that question DOE’s authority
under section 1605(b) to establish
separate classes of reporting in the
database maintained by EIA. That
discussion is relevant here. DOE
reiterates that entities may report
reductions resulting from a broad range
of specific actions under the revised
guidelines; it is only registered
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reductions that limit the use of actionspecific methods to those reductions
which cannot be captured by one of the
other emission reduction calculation
methods.
Other comments sought to expand the
range of action-specific reductions
allowed to be registered. DOE was
persuaded that methods for several of
these actions should be added to the
guidelines. These include a method for
measuring action-specific reductions
from anaerobic digestion of waste at
agricultural facilities or wastewater
treatment plants. DOE views this
method as similar to and a logical
extension of methods for estimating
reductions from coal mine and landfill
gas recovery. DOE was also persuaded
that the volume and magnitude of
reductions attributable to residential
and commercial demand-side
management and other programs, and
the limited likelihood that individual
residential and small commercial endusers would be participants in the
program, justified a method for electric
power generators and others that
implement such programs to register
emissions reductions that can be
reliably attributed to those efforts.
However, the final guidelines provide
that reporting entities must certify that
the program was directed at residential
or other very small emitters (such as
small businesses or other entities that
the reporter estimates typically emit less
than 500 metric tons of CO2 annually).
The new action-specific method
established in the Technical Guidelines
attempts to ensure that the reductions
reported are only those that can be
attributed to the specific effects of the
demand-side management or other
program evaluated, and not to other
market or regulatory changes. DOE has
also provided a new action-specific
method for calculating reductions
associated with increased use of flyash
by concrete mixers.
Several commenters sought inclusion
of action-specific methods for
registering reductions from increases in
the manufacturing and sale of energy
efficient products such as home
appliances and automobiles, and others
requested a method for registering
reductions from increased materials
recycling. Although DOE has not
adopted these additional methods, DOE
expects in the future to solicit comment
on methods for calculating reductions
from energy efficient products and
materials recycling and will then
consider incorporating suitable methods
in the Technical Guidelines.
c. Changes to proposed action-specific
methods. Several comments offered
alternative methods for calculating
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action-specific reductions from landfill
gas recovery and transmission and
distribution improvement. For landfill
gas recovery, commenters recommended
methods placing a greater reliance on
modeled emissions. However, DOE did
not adopt these recommendations
because it is concerned they would add
uncertainty and reduced transparency of
action-specific reductions from this
source. Similarly, a request for
quantifying emission reductions for
displacing coal or oil with landfill gas
by a landfill gas purchaser was not
adopted because those reductions will
be captured in changes in the
purchaser’s emission intensity, and
inclusion would result in double
counting. DOE, however, has adjusted
the method for estimating reductions
from transmission and distribution
improvements to emphasize changes in
system-wide transmission and
distribution emission intensity.
Comments related to geologic
sequestration were also provided,
focusing on monitoring and ownership.
One commenter asked whether available
monitoring methods only apply to
enhanced oil recovery, or to all geologic
sequestration projects. DOE clarified
that the monitoring methods should be
used for all types of geologic
sequestration. Another commenter
argued that site-specific monitoring
should be required of all available
monitoring options, including those
based on estimating future losses of
carbon dioxide after injection has been
completed. The argument is that the
data and methodologies for undertaking
such estimates of future losses are
insufficient. In October 2005, the IPCC
published a Special Report on Carbon
Dioxide Capture and Storage, which
includes a comprehensive discussion of
available monitoring techniques for
geologic sequestration. Noting that all
monitoring options recommended by
the IPCC are site-specific, DOE has
revised the guidelines to also require
site-specific monitoring for all of its
monitoring methods. In addition, DOE
has clarified its guidelines to ensure that
entities may not claim offset or other
types of reductions associated with the
capture and sale of CO2 unless they
have an agreement with the entity that
is permanently sequestering the CO2, in
accord with DOE’s Technical
Guidelines.
d. Ozone-depleting gases. One
commenter argued for inclusion of
ozone depleting gases, such as
chlorofluorocarbons (CFCs) and
hydrochlorofluorocarbons (HCFCs),
because it would encourage recovery
and destruction of these greenhouse
gases. Section 1605(b) expressly permits
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reporting of annual reductions of
greenhouse gas emissions achieved
through chlorofluorocarbon capture and
replacement. While these gases have
radiative forcing properties, they also
destroy stratospheric ozone, which may
influence global climate. The IPCC has
not determined definitive global
warming potential (GWP) for CFCs and
HCFCs. It has, instead, estimated these
gases in broad ranges. For example, the
IPCC Third Assessment Report gives the
net 100-year GWP for CFC–11 as a
minimum of ¥600 and a maximum of
3600.
Because of the development of rated
methods for calculating emissions and
emission reductions of ozone depleting
substances would be complex and timeconsuming, the final guidelines do not
permit the registration of reductions of
these gases. However, DOE has included
an action-specific method for
calculating reductions from the
destruction of CFCs that have been
captured or replaced, and these
reductions may be reported under the
1605(b) program. DOE may in the future
solicit comment on methods for
calculating reductions of other ozone
depleting substances and will consider
incorporating suitable methods in the
Technical Guidelines.
9. Estimating Reductions From Energy
Generation and Distribution
For electricity generators, the interim
final guidelines provide a single formula
that integrates the emissions intensity
and avoided emissions methods. DOE
considered this integrated formula to be
necessary to provide the same
opportunity for recognition to any
generator of additional electric power,
regardless of the characteristics of that
entity’s base period generation. Some
utilities objected to the use of the
integrated formula and proposed that
DOE permit utilities to base the
emission reduction calculations on any
decline in the entity’s base period
emissions intensity, regardless of
whether the entity had increased its
power generation. After careful
consideration of these comments, DOE
has decided to retain the integrated
formula. Because the electricity
generating sector is both very diverse
and is given special recognition for
emissions avoided by addition of new
generation from non-emitting or lowemitting sources, the integrated formula
is necessary to give all generators a
roughly equal opportunity to qualify for
registered reductions.
The integrated formula uses the same
benchmark value used for the
calculation of avoided emissions from
electricity generation. In response to
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comments, DOE has decided to change
this benchmark to the regional average
emissions intensity of fossil-fired
generation. This decision is described in
more detail in the section on avoided
emissions, above.
One commenter asserted that the
method for allocating emissions to
thermal and electric streams for
combined heat and power (CHP)
generators does not accurately reflect
actual thermal efficiencies. The method
included in the interim final guidelines
requires reporters to assume the
efficiency of the thermal component of
CHP systems to be 80 percent. The final
guidelines are more flexible and allow
the reporter to use the actual efficiency
of thermal energy generation, if known.
Reporters may use a default value for
thermal efficiency of 80 percent if this
value is unknown.
L. Offset Reductions
The interim final guidelines provide a
mechanism by which a reporting entity
could register the reductions achieved
by another entity that was willing to
forego this recognition. To ensure that
this mechanism for reporting offset
reductions did not undermine the
emphasis on entity-wide reporting, the
interim final guidelines require that the
other entity complete annual reports
that meet all of DOE’s requirements and
that these reports be submitted to DOE
by the reporting entity.
A broad range of commenters noted
that this mechanism was simply not
practical for use in a number of
situations, such as:
• When multiple entities are
supporting the offset reductions
achieved by a single entity (such as a
group of utilities supporting
reforestation projects on the land of
single public agency, or when a number
of different electric power users seek
recognition for the offset reduction
reductions created by a single renewable
or nuclear power generator).
• When a reporting entity supports
the offset reductions achieved by a large
number of very small emitters, such as
a utility that supports a demand-side
management program that provides
incentives for the purchase of energy
efficient lights by homeowners.
To address these problems, DOE has
made a few modifications to the offset
reduction provisions of the guidelines.
The final guidelines now provide an
action-specific method to enable
utilities to register the reductions that
can be attributed specifically to the
effects of utility-sponsored demand-side
management programs. The guidelines
also permit more than one entity to be
the recipient of offset reductions from a
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single other entity. The assignment of
registered reductions to multiple
reporting entities, as offset reductions,
can only be done at the time they are
initially reported to EIA. In addition,
DOE has made it clear that the
guidelines permit other Federal agencies
or even smaller operational units, such
as a wildlife refuge, to generate
registered reductions that are reported
by other entities as offsets.
M. Certification and Verification
Most comments supported the need
for reporting entities to certify the
accuracy of their reports, although there
were different views on which
representatives of an entity should be
required to provide such certifications
and the nature of these certifications.
Similarly, there was widespread support
for DOE’s decision to encourage, but not
require, independent verification of
reports, and a number of specific
comments addressed how DOE should
define such an independent verification.
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1. Certification
Section 300.10 of the interim final
General Guidelines states that all reports
must be certified by the head of
household, chief executive officer,
agency head, or an officer or employee
of the entity who is responsible for
reporting the entity’s compliance with
environmental regulations. DOE
received comments calling for a higher
level of corporate certification and
others calling for more flexibility in the
identity of a certifier. DOE believes that
it has properly addressed the need for
a high level of certification while
granting sufficient flexibility to
participating entities.
More narrow comments sought a
definition of ‘‘reasonable steps,’’ in
§ 300.10(c)(1) of the interim final
General Guidelines, that a reporter must
have taken to ensure emissions,
emission reductions and/or
sequestration are not double-counted,
and asked that certification
requirements on third parties that are
redundant with those for reporting
entities be removed to limit reporter
burden. DOE has revised the final
guidelines language to address these
concerns by explaining what it
considers to be ‘‘reasonable steps’’ and
by eliminating certain redundant
certification requirements.
Several commenters expressed
concerns that the certification
requirements would discourage farmers,
ranchers, and small woodland owners
from participating in the 1605(b)
program. DOE has included provisions
for aggregators and offsets (described
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above) that should mitigate these
concerns.
2. Independent Verification
Section 300.11 of the interim final
General Guidelines states that reporting
entities are encouraged to have their
annual reports reviewed by independent
and qualified auditors and then defines
the characteristics required for an
auditor to be viewed by DOE as both
independent and qualified. That section
also enumerates the expected scope of
an independent verification.
DOE received a substantial number of
comments on independent verification.
Some comments expressed the view that
independent verification is necessary
for data credibility, and, therefore,
should be required rather than
encouraged. Other comments argued
against requiring independent
verification. DOE recognizes the value
of independent verification but remains
sensitive to the cost and burden it may
impose on prospective program
participants. DOE seeks in the final
guidelines to encourage independent
verification, while limiting reporter
burden, by permitting reporting entities
to register reductions without reporting
and rating emissions estimates at the
individual source or sink level if they
receive independent verification that
the quantity-weighted average of
methods used for preparing their
emissions inventory meet or exceed 3.0.
Further, DOE has extended the July 1
annual reporting deadline to September
1 for independently verified reports.
Other comments sought inclusion of
additional detail on the processes and
procedures that verifiers must follow
when undertaking an independent
verification, and expressed a desire for
consistency with existing standards.
DOE wishes to provide greater
flexibility than could be obtained
through the adoption of a single existing
standard, but it also wishes its
guidelines to be generally consistent
with current domestic and international
practices. Accordingly, the final
guidelines direct independent verifiers
to refer to such sources as the California
Climate Action Registry Certification
Protocol, the Climate Leaders Inventory
Management Plan Checklist and the
draft ISO 14064.3 standard when
completing a verification.
DOE received comments suggesting
that a separate and distinct set of rules
for ‘‘accrediting’’ verifiers should be
prepared by DOE. DOE believes this
approach is too prescriptive and
deterministic for a rapidly developing
and evolving field of expertise.
Moreover, DOE recognizes that many
potential reporters may seek
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independent verification of data
submitted to other domestic and
international programs, in addition to
the Voluntary Reporting of Greenhouse
Gases Program, and does not wish to
preclude verifiers accepted by other
programs from performing an
independent verification under these
guidelines. Consistent with that
approach, DOE has not created a new
set of rules for accrediting independent
verifiers; instead, the final guidelines
incorporate and reference elements of
the California Climate Action Registry
requirements and the draft ISO 14064.3
guidance.
N. Reporting and Record Keeping
Section 300.9 of the interim final
General Guidelines requires entities
intending to register reductions to
maintain adequate supporting records
for at least three years to enable
verification of all information reported.
A number of comments voiced concern
that the three-year requirement was not
long enough to support the transition to
a future regulatory program. The
comments sought a five-year or longer
recordkeeping requirement. Meanwhile,
other comments noted the potential
burden of even a three-year
recordkeeping requirement. It was not
DOE’s intent to envisage the existence
or design of a future regulatory regime,
but rather to ensure that reports
submitted to this program be verifiable
for a number of years subsequent to
submission. In addition, DOE believes
many entities are likely to retain records
beyond the period required by DOE
guidelines in anticipation that there
may be a regulatory program in the
future. Thus, DOE was not persuaded to
extend the overall recordkeeping
requirement. However, several of the
comments pointed out that such
verification would require base period
data that may pre-date the three year
recordkeeping requirement. In response,
DOE has extended the recordkeeping
requirement for base period data to the
duration of an entity’s participation in
the program.
O. Report Review and Acceptance
Process
Section 300.12 of the interim final
General Guidelines states that EIA will
review all reports to ensure that they are
consistent with the General Guidelines
and Technical Guidelines. Subject to the
availability of adequate resources, EIA
intends to notify reporters of the
acceptance or rejection of any report
within six months of receipt and sooner
if feasible. If EIA does not accept a
report or if it determines that emission
reductions intended for registration do
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not qualify, the report will be returned
with an explanation of its inadequacies.
The reporting entity may resubmit a
modified report for further
consideration at any time.
Comments indicated concern that the
EIA review process would not be
sufficiently rigorous in the absence of
independent verification. More
generally, comments sought inclusion of
more detail on the review process to be
undertaken by EIA. In response to these
comments, DOE has included additional
language on the specifics of EIA’s
review process.
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P. Publication of General Guidelines in
the Code of Federal Regulations
Several commenters claim that by
publishing the General Guidelines as a
rule for codification in the Code of
Federal Regulations, DOE exceeded its
authority under section 1605(b) to issue
voluntary guidelines for reporting. In
their view, the use of mandatory words
in the General Guidelines is
inconsistent with a voluntary program.
DOE addressed the question of
publication in the Code of Federal
Regulations in the preamble to the
notice of interim final guidelines
published on March 24, 2005 (70 FR
15176). In addition to giving reasons
favoring codification, DOE related that
the Director of the Federal Register had
written a letter in response to a request
from an interested person that stated his
conclusion that it is proper for DOE to
include the revised General Guidelines
in the Code of Federal Regulations. DOE
has placed the Director’s letter in the
administrative record for this
rulemaking.
DOE rejects the comments contending
that mandatory language may not be
used in the revised guidelines, for two
reasons. First, the revised guidelines are
largely procedural rules, and procedural
rules usually are stated in mandatory
terms. Second, the requirements in the
revised guidelines do not alter the
voluntary nature of the 1605(b) program.
Entities, in their sole discretion, may
decide to report under the Voluntary
Reporting of Greenhouse Gases Program.
Those who do decide to report may,
again in their sole discretion, decide to
seek the greater credibility that would
be associated with registering their
emissions and reductions. Their
participation is voluntary, but if they
decide to report or register their
emissions and reductions, then they
must abide by any requirements in the
revised guidelines. This is entirely
consistent with section 1605(b).
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IV. Regulatory Review and Procedural
Requirements
A. Review Under Executive Order 12866
Today’s action has been determined
to be ‘‘a significant regulatory action’’
under Executive Order 12866,
‘‘Regulatory Planning and Review’’ (58
FR 51735, October 4, 1993).
Accordingly, this action was subject to
review under that Executive Order by
the Office of Information and Regulatory
Affairs of the Office of Management and
Budget (OMB).
Because of new requirements
associated with the revised General
Guidelines and the Technical
Guidelines, it is anticipated that the
costs for participants to report and
register reductions are likely to increase.
The anticipated benefits of the new
requirements include enhanced data
quality associated with reported and
registered reductions. The magnitude of
these effects has not been assessed.
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 for any rule that by law must
be proposed for public comment, unless
the agency certifies that the rule, if
promulgated, will not have a significant
economic impact on a substantial
number of small entities. As required by
Executive Order 13272, ‘‘Proper
Consideration of Small Entities in
Agency Rulemaking’’ (67 FR 53461,
August 16, 2002), DOE published
procedures and policies to ensure that
the potential impacts of its draft rules
on small entities are properly
considered during the rulemaking
process (68 FR 7990, February 19, 2003),
and has made them available on the
Office of General Counsel’s Web site:
https://www.gc.doe.gov.
DOE has reviewed today’s revised
General Guidelines for the Voluntary
Greenhouse Gas Reporting Program
under the provisions of the Regulatory
Flexibility Act and the procedures and
policies published on February 19,
2003. The Guidelines establish
procedures and guidance for the
accurate voluntary reporting of
information on greenhouse gas
emissions and reductions. Participation
in the reporting program is voluntary,
and the Department anticipates that
small entities will weigh the benefits
and costs when deciding to participate.
To minimize the burden on small
entities that choose to participate, the
guidelines exempt ‘‘small emitters’’
(usually small businesses or
organizations) from requirements for an
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20803
entity-wide inventory and an entitywide assessment of emission reductions.
These exemptions mean that small
emitters can participate at a
significantly lower cost than otherwise.
On the basis of the foregoing, DOE
certifies that these guidelines will not
have a significant economic impact on
a substantial number of small entities.
Accordingly, DOE has not prepared a
regulatory flexibility analysis for this
rulemaking.
C. Review Under the Paperwork
Reduction Act
EIA previously obtained Paperwork
Reduction Act clearance by the Office of
Management and Budget (OMB) for
forms used in the current Voluntary
Reporting of Greenhouse Gases program
(OMB Control No. 1905–0194). EIA is
preparing new forms and associated
instructions to implement the revised
guidelines for the program, and it will
publish a separate notice in the Federal
Register requesting public comment on
the proposed collection of information
in accordance with 44 U.S.C.
3506(c)(2)(A). After considering the
public comments, EIA will submit the
new forms, instructions, and related
guidelines to OMB for approval
pursuant to 44 U.S.C. 3507(a)(1).
D. Review Under the National
Environmental Policy Act
DOE has concluded that these revised
General Guidelines fall into a class of
actions that will not individually or
cumulatively have a significant impact
on the human environment, as
determined by DOE’s regulations
implementing the National
Environmental Policy Act of 1969 (42
U.S.C. 4321 et seq.). This action deals
with the procedures and guidance for
entities that wish to voluntarily report
their greenhouse gas emissions and their
reduction and sequestration of such
emissions to EIA. Because the
guidelines relate to agency procedures,
they are covered under the Categorical
Exclusion in paragraph A6 to subpart D,
10 CFR part 1021. Accordingly, neither
an environmental assessment nor an
environmental impact statement is
required.
E. Review Under Executive Order 13132
Executive Order 13132, ‘‘Federalism’’
(64 FR 43255, August 4, 1999) imposes
certain requirements on agencies
formulating and implementing policies
or regulations that preempt State law or
that have federalism implications.
Agencies are required to examine the
constitutional and statutory authority
supporting any action that would limit
the policymaking discretion of the
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States and carefully assess the necessity
for such actions. The Executive Order
also requires agencies to have an
accountable process to ensure
meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications. On March 14, 2000, DOE
published a statement of policy
describing the intergovernmental
consultation process it will follow in the
development of such regulations (65 FR
13735). DOE has examined today’s
action and has determined that it does
not preempt State law and does not
have a substantial direct effect on the
States, on the relationship between the
national government and the States, or
on the distribution of power and
responsibilities among the various
levels of government. No further action
is required by Executive Order 13132.
F. Review Under the Treasury and
General Government Appropriations
Act, 2001
The Treasury and General
Government Appropriations Act, 2001
(44 U.S.C. 3516, note) provides for
agencies to review most disseminations
of information to the public under
guidelines established by each agency
pursuant to general guidelines issued by
OMB. OMB’s guidelines were published
at 67 FR 8452 (February 22, 2002), and
DOE’s guidelines were published at 67
FR 62446 (October 7, 2002). DOE has
reviewed today’s final rule under the
OMB and DOE guidelines and has
concluded that it is consistent with
applicable policies in those guidelines.
One organization commented on
DOE’s interim final and draft Technical
Guidelines and sought clarification on
whether and how DOE and EIA
information quality guidelines apply to
information submitted under section
1605(b). The organization criticized the
interim final guidelines for failing to
address issues that it thought would
arise when third parties challenge the
quality of publicly disseminated
emissions reduction data voluntarily
submitted to DOE by business and
industry stakeholders. In this
commenter’s view, third party
challenges will require EIA to request
substantiation of the validity of the
reported data and possibly lead to
disclosure of confidential business
information or trade secrets. This, it
argued, could cause business and
industry stakeholders to be reluctant to
take part in the voluntary reporting
program or, at least, add to the cost of
doing business. This commenter also
felt the perceived value of registered
reductions would be called into
question if, as a result of data quality
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challenges, the underlying data were
viewed as unreliable.
As requested, DOE clarifies here the
application of DOE and EIA information
quality guidelines to information
submitted under section 1605(b).
Agency information quality guidelines
apply to information disseminated by
DOE based on the voluntary reports of
greenhouse gas emissions information
reported to EIA under section 1605(b) of
the Energy Policy Act of 1992. When
EIA disseminates information reported
under section 1605, the public has the
opportunity to utilize DOE’s established
administrative mechanisms to seek and
obtain, where appropriate, timely
correction of information maintained
and disseminated by EIA that does not
comply with applicable information
quality guidelines. As set forth in DOE’s
Information Quality Guidelines,
requests for correction must: (1)
Specifically identify the information in
question and the document(s)
containing the information; (2) explain
with specificity the reasons why the
information is inconsistent with the
applicable quality standards in the
OMB, DOE, or EIA guidelines; (3)
present substitute information, if any,
with an explanation showing that such
information is consistent with the
applicable quality standards in the
OMB, DOE, or EIA guidelines; and (4)
justify the necessity for, and the form of,
the requested correction.
While DOE and EIA seek to ensure the
transparency and accuracy of 1605(b)
information by specifying the methods
that must be used to calculate emission
reductions that are to be registered and
by requiring certain information about
the entity that produced the emissions,
section 1605(b)(2) requires selfcertification by reporting entities and
does not authorize or direct EIA to
verify the accuracy of information in
reports. In addition, section 1605(b)(3)
provides that trade secret and
commercial or financial information
that is privileged or confidential shall be
protected as provided in 5 U.S.C.
552(b)(4). If a member of the public
seeking correction submits information
that calls into question the accuracy of
information in a particular 1605(b)
report, then EIA may ask the person
who submitted the report to respond to
the issues raised and, if appropriate,
submit corrected 1605(b) information.
G. Review Under Executive Order 12988
With respect to the review of existing
regulations and the promulgation of
new regulations, section 3(a) of
Executive Order 12988, ‘‘Civil Justice
Reform’’ (61 FR 4729, February 7, 1996),
imposes on Federal agencies the general
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duty to adhere to the following
requirements: (1) Eliminate drafting
errors and ambiguity; (2) write
regulations to minimize litigation; and
(3) provide a clear legal standard for
affected conduct rather than a general
standard and promote simplification
and burden reduction. Section 3(b) of
Executive Order 12988 specifically
requires that Executive agencies make
every reasonable effort to ensure that the
regulation: (1) Clearly specifies the
preemptive effect, if any; (2) clearly
specifies any effect on existing Federal
law or regulation; (3) provides a clear
legal standard for affected conduct
while promoting simplification and
burden reduction; (4) specifies the
retroactive effect, if any; (5) adequately
defines key terms; and (6) addresses
other important issues affecting clarity
and general draftsmanship under any
guidelines issued by the Attorney
General. Section 3(c) of Executive Order
12988 requires Executive agencies to
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, these
revised guidelines meet the relevant
standards of Executive Order 12988.
H. Review Under the Unfunded
Mandates Reform Act of 1995
Title II of the Unfunded Mandates
Reform Act of 1995 (Pub. L. 104–4)
requires each Federal agency to assess
the effects of a Federal regulatory action
on state, local, and tribal governments,
and the private sector. The Department
has determined that today’s action does
not impose a Federal mandate on state,
local or tribal governments or on the
private sector.
I. 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. These
revised guidelines 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.
J. Review Under Executive Order 13211
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355, May
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22, 2001) requires Federal agencies to
prepare and submit to the OMB, a
Statement of Energy Effects for any
proposed significant energy action. A
‘‘significant energy action’’ is defined as
any action by an agency that
promulgated or is expected to lead to
promulgation of a final rule, and that:
(1) Is a significant regulatory action
under Executive Order 12866, or any
successor order; and (2) is likely to have
a significant adverse effect on the
supply, distribution, or use of energy, or
(3) is designated by the Administrator of
OIRA as a significant energy action. For
any proposed significant energy action,
the agency must give a detailed
statement of any adverse effects on
energy supply, distribution, or use
should the proposal be implemented,
and of reasonable alternatives to the
action and their expected benefits on
energy supply, distribution, and use.
Today’s regulatory action would not
have a significant adverse effect on the
supply, distribution, or use of energy
and is therefore not a significant energy
action. Accordingly, DOE has not
prepared a Statement of Energy Effects.
K. Congressional Review
As required by 5 U.S.C. 801, DOE will
report to Congress the promulgation of
this rule prior to its effective date. The
report will state that it has been
determined that the rule is not a ‘‘major
rule’’ as defined by 5 U.S.C. 804(2).
List of Subjects in 10 CFR Part 300
Administrative practice and
procedure, Energy, Gases, Incorporation
by reference, Reporting and
recordkeeping requirements.
Issued in Washington, DC, on April 13,
2006.
Karen A. Harbert,
Assistant Secretary for Policy and
International Affairs.
Accordingly, the interim final rule
published at 70 FR 15169 on March 24,
2005, which added a new Subchapter B
to Title 10 of the Code of Federal
Regulations, is adopted as a final rule
with changes. Subchapter B consisting
of part 300 is revised to read as follows:
I
Subchapter B—Climate Change
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PART 300—VOLUNTARY
GREENHOUSE GAS REPORTING
PROGRAM: GENERAL GUIDELINES
Sec.
300.1 General.
300.2 Definitions.
300.3 Guidance for defining and naming the
reporting entity.
300.4 Selecting organizational boundaries.
300.5 Submission of an entity statement.
300.6 Emissions inventories.
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300.7 Net emission reductions.
300.8 Calculating emission reductions.
300.9 Reporting and recordkeeping
requirements.
300.10 Certification of reports.
300.11 Independent verification.
300.12 Acceptance of reports and
registration of entity emission
reductions.
300.13 Incorporation by reference.
Authority: 42 U.S.C. 7101, et seq., and 42
U.S.C. 13385(b).
§ 300.1
General.
(a) Purpose. The General Guidelines
in this part and the Technical
Guidelines incorporated by reference in
§ 300.13 govern the Voluntary Reporting
of Greenhouse Gases Program
authorized by section 1605(b) of the
Energy Policy Act of 1992 (42 U.S.C.
13385(b)). The purpose of the guidelines
is to establish the procedures and
requirements for filing voluntary
reports, and to encourage corporations,
government agencies, non-profit
organizations, households and other
private and public entities to submit
annual reports of their greenhouse gas
emissions, emission reductions, and
sequestration activities that are
complete, reliable and consistent. Over
time, it is anticipated that these reports
will provide a reliable record of the
contributions reporting entities have
made toward reducing their greenhouse
gas emissions.
(b) Reporting under the program. (1)
Each reporting entity, whether or not it
intends to register emissions as
described in paragraph (c) of this
section, must:
(i) File an entity statement that meets
the appropriate requirements in
§ 300.5(d) through (f) of this part;
(ii) Use appropriate emission
inventory and emission reduction
calculation methods specified in the
Technical Guidelines (incorporated by
reference, see § 300.13), and calculate
and report the weighted average quality
rating of any emission inventories it
reports;
(iii) Comply with the record keeping
requirements in § 300.9 of this part; and
(iv) Comply with the certification
requirements in § 300.10 of this part;
(2) Each reporting entity, whether or
not it intends to register emissions as
described in paragraph (c) of this
section, may report offset reductions
achieved by other entities outside their
boundaries as long as such reductions
are reported separately and calculated
in accordance with methods specified in
the Technical Guidelines. The thirdparty entity that achieved these
reductions must agree to their being
reported as offset reductions, and must
also meet all of the requirements of
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reporting that would apply if the thirdparty entity reported directly under the
1605(b) program.
(3) An entity that intends to register
emissions and emission reductions must
meet the additional requirements
referenced in paragraph (c) of this
section.
(4) An entity that does not intend to
register emissions and emission
reductions may choose to report its
emissions and/or emission reductions
on an entity-wide basis or for selected
elements of the entity, selected gases or
selected sources.
(5) An entity that does not intend to
register emissions may report emission
inventories for any year back to 1990
and may report emission reductions for
any year back to 1991, relative to a base
period of one to four years, ending no
earlier than 1990.
(c) Registration requirements. Entities
that seek to register reductions must
meet the additional requirements in this
paragraph; although these requirements
differ depending on whether the entity
is a large or small emitter.
(1) To be eligible for registration, a
reduction must have been achieved after
2002, unless the entity has committed
under the Climate Leaders or Climate
VISION programs to reduce its entitywide emissions relative to a base period
that ends earlier 2002, but no earlier
than 2000.
(2) A large emitter must submit an
entity-wide emission inventory that
meets or exceeds the minimum quality
requirements specified in § 300.6(b) and
the Technical Guidelines (incorporated
by reference, see § 300.13). Registered
reductions of a large emitter must be
based on an entity-wide assessment of
net emission reductions, determined in
accordance with § 300.8 and the
Technical Guidelines.
(3) A small emitter must also submit
an emission inventory that meets
minimum quality requirements
specified in § 300.6(b) and the Technical
Guidelines (incorporated by reference,
see § 300.13) and base its registered
reductions on an assessment of annual
changes in net emissions. A small
emitter, however, may restrict its
inventory and assessment to a single
type of activity, such as forest
management, building operations or
agricultural tillage.
(4) Reporting entities may, under
certain conditions, register reductions
achieved by other entities:
(i) Reporting entities that have met the
requirements for registering their own
reductions may also register offset
reductions achieved by other entities if:
(A) They have an agreement with the
third-party entities to do so and these
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third-party entities have met all of the
requirements for registration; or
(B) They were the result of qualified
demand management or other programs
and are calculated in accordance with
the action-specific method identified in
§ 300.8(h)(5).
(ii) Small emitters that serve as an
aggregator may register offset reductions
achieved by non-reporting entities
without reporting on their own
emissions, as long as they have an
agreement with the third-party entities
to do so and these third-party entities
have met all of the requirements for
registration.
(d) Forms. Annual reports of
greenhouse gas emissions, emission
reductions, and sequestration must be
made on forms or software made
available by the Energy Information
Administration of the Department of
Energy (EIA).
(e) Status of reports under previous
guidelines. EIA continues to maintain in
its Voluntary Reporting of Greenhouse
Gases database all reports received
pursuant to DOE’s October 1994
guidelines. Those guidelines are
available from EIA at https://
www.eia.doe.gov/oiaf/1605/
guidelns.html.
(f) Periodic review and updating of
General and Technical Guidelines. DOE
intends periodically to review the
General Guidelines and the Technical
Guidelines (incorporated by reference,
see § 300.13) to determine whether any
changes are warranted; DOE anticipates
these reviews will occur approximately
once every three years. These reviews
will consider any new developments in
climate science or policy, the
participation rates of large and small
emitters in the 1605(b) program, the
general quality of the data submitted by
different participants, and any changes
to other emissions reporting protocols.
Possible changes may include, but are
not limited to:
(1) The addition of greenhouse gases
that have been demonstrated to have
significant, quantifiable climate forcing
effects when released to the atmosphere
in significant quantities;
(2) Changes to the minimum,
quantity-weighted quality rating for
emission inventories;
(3) Updates to emission inventory
methods, emission factors and other
provisions that are contained in
industry protocols or standards. The
review may also consider updates to any
government-developed and consensusbased emission factors for which
automatic updating is not provided in
the Technical Guidelines;
(4) Modifications to the benchmarks
or emission conversion factors used to
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calculate avoided and indirect
emissions; and
(5) Changes in the minimum
requirements for registered emission
reductions.
§ 300.2
Definitions.
This section provides definitions for
commonly used terms in this part.
Activity of a small emitter means,
with respect to a small emitter, any
single category of anthropogenic
production, consumption or other
action that releases emissions or results
in sequestration, the annual changes of
which can be assessed generally by
using a single calculation method.
Aggregator means an entity that
reports to the 1605(b) program on behalf
of non-reporting entities. An aggregator
may be a large or small emitter, such as
a trade association, non-profit
organization or public agency.
Anthropogenic means greenhouse gas
emissions and removals that are a direct
result of human activities or are the
result of natural processes that have
been affected by human activities.
Avoided emissions means the
greenhouse gas emission reductions that
occur outside the organizational
boundary of the reporting entity as a
direct consequence of changes in the
entity’s activity, including but not
necessarily limited to the emission
reductions associated with increases in
the generation and sale of electricity,
steam, hot water or chilled water
produced from energy sources that emit
fewer greenhouse gases per unit than
other competing sources of these forms
of distributed energy.
Base period means a period of 1–4
years used to derive the average annual
base emissions, emissions intensity or
other values from which emission
reductions are calculated.
Base value means the value from
which emission reductions are
calculated for an entity or subentity.
The value may be annual emissions,
emissions intensity, kilowatt-hours
generated, or other value specified in
the 1605(b) guidelines. It is usually
derived from actual emissions and/or
activity data derived from the base
period.
Biogenic emissions mean emissions
that are naturally occurring and are not
significantly affected by human actions
or activity.
Boundary means the actual or virtual
line that encompasses all the emissions
and carbon stocks that are to be
quantified and reported in an entity’s
greenhouse gas inventory, including de
minimis emissions. Entities may use
financial control or another
classification method based on
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ownership or control as the means of
determining which sources or carbon
stocks fall within this organizational
boundary.
Carbon dioxide equivalent means the
amount of carbon dioxide by weight
emitted into the atmosphere that would
produce the same estimated radiative
forcing as a given weight of another
radiatively active gas. Carbon dioxide
equivalents are computed by
multiplying the weight of the gas being
measured by its estimated global
warming potential.
Carbon stocks mean the quantity of
carbon stored in biological and physical
systems including: trees, products of
harvested trees, agricultural crops,
plants, wood and paper products and
other terrestrial biosphere sinks, soils,
oceans, and sedimentary and geological
sinks.
Climate Leaders means the EPA
sponsored industry-government
partnership that works with individual
companies to develop long-term
comprehensive climate change
strategies. Certain Climate Leaders
Partners have, working with EPA, set a
corporate-wide greenhouse gas
reduction goal and have inventoried
their emissions to measure progress
towards their goal.
Climate VISION means the publicprivate partnership initiated pursuant to
a Presidential directive issued in 2002
that aims to contribute to the President’s
goal of reducing greenhouse gas
intensity through voluntary frameworks
with industry. Climate VISION partners
have signed an agreement with DOE to
implement various climate-related
actions to reduce greenhouse gas
emissions.
De minimis emissions means
emissions from one or more sources and
of one or more greenhouse gases that, in
aggregate, are less than or equal to 3
percent of the total annual carbon
dioxide (CO2) equivalent emissions of a
reporting entity.
Department or DOE means the U.S.
Department of Energy.
Direct emissions are emissions from
sources within the organizational
boundaries of an entity.
Distributed energy means electrical or
thermal energy generated by an entity
that is sold or otherwise exported
outside of the entity’s boundaries for
use by another entity.
EIA means the Energy Information
Administration within the U.S.
Department of Energy.
Emissions means the direct release of
greenhouse gases to the atmosphere
from any anthropogenic (human
induced) source and certain indirect
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emissions (releases) specified in this
part.
Emissions intensity means emissions
per unit of output, where output is
defined as the quantity of physical
output, or a non-physical indicator of an
entity’s or subentity’s productive
activity.
Entity means the whole or part of any
business, institution, organization,
government agency or corporation, or
household that:
(1) Is recognized under any U.S.
Federal, State or local law that applies
to it;
(2) Is located and operates, at least in
part, in the United States; and
(3) The emissions of such operations
are released, at least in part, in the
United States.
First reduction year means the first
year for which an entity intends to
register emission reductions; it is the
year that immediately follows the start
year.
Fugitive emissions means
uncontrolled releases to the atmosphere
of greenhouse gases from the processing,
transmission, and/or transportation of
fossil fuels or other materials, such as
HFC leaks from refrigeration, SF6 from
electrical power distributors, and
methane from solid waste landfills,
among others, that are not emitted via
an exhaust pipe(s) or stack(s).
Greenhouse gases means the gases
that may be reported to the Department
of Energy under this program. They are:
(1) Carbon dioxide (CO2)
(2) Methane (CH4)
(3) Nitrous oxide (N2O)
(4) HydrofluorocarbonsHFC-23
[trifluoromethane-(CHF3]HFC-32
[trifluoromethane-CH2F2], CH2CF3,
CH3F, CHF2CF3, CH2FCF3, CH3FCF3,
CHF2CH2F, CF3CH3, CH2FCH2F,
CH3CHF2, CH3CH2F, CF3CHFCF3,
CH2FCF3CF3, CHF2CHFCF3,
CF3CH2CF3, CH2FCF2CHF2,
CHF2CH2CF3, CF3CH2CF2CH3, CH3
CHFCHFCF2)
(5) Perfluorocarbons (perfluoromethaneCF4, perfluoroethane-C2F6, C3F8,
C4F10, c-C4F8, C5F12, C6F14)
(6) Sulfur hexafluoride (SF6)
(7) Chlorofluorocarbons (CFC-11
[trichlorofluoromethane-CCl3F],
CCl2F2, CClF3, CCl2FCClF2,
CClF2CClF2, ClF3CClF2,)
(8) Other gases or particles that have
been demonstrated to have
significant, quantifiable climate
forcing effects when released to the
atmosphere in significant quantities
and for which DOE has established or
approved methods for estimating
emissions and reductions. (Note: As
provided in § 300.6(i),
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chlorofluorcarbons and other gases
with quantifiable climate forcing
effects may be reported to the 1605(b)
program if DOE has established an
appropriate emission inventory or
emission reduction calculation
method, but reductions of these gases
may not be registered.)
Incidental lands are entity
landholdings that are a minor
component of an entity’s operations and
are not actively managed for production
of goods and services, including:
(1) Transmission, pipeline, or
transportation right of ways that are not
managed for timber production;
(2) Land surrounding commercial
enterprises or facilities; and
(3) Land where carbon stock changes
are determined by natural factors.
Indirect emissions means greenhouse
gas emissions from stationary or mobile
sources outside the organizational
boundary that occur as a direct
consequence of an entity’s activity,
including but not necessarily limited to
the emissions associated with the
generation of electricity, steam and hot/
chilled water used by the entity.
Large emitter means an entity whose
annual emissions are more than 10,000
metric tons of CO2 equivalent, as
determined in accordance with
§ 300.5(c).
Net emission reductions means the
sum of all annual changes in emissions,
eligible avoided emissions and
sequestration of the greenhouse gases
specifically identified in § 300.6(i), and
determined to be in conformance with
§§ 300.7 and 300.8 of this part.
Offset means an emission reduction
that is included in a 1605(b) report and
meets the requirements of this part, but
is achieved by an entity other than the
reporting entity. Offset reductions must
not be reported or registered by any
other entity and must appear as a
separate and distinct component of an
entity’s report. Offsets are not integrated
into the reporting entity’s emissions or
net emission reductions.
Registration means the reporting of
emission reductions that the EIA has
determined meet the qualifications for
registered emission reductions set forth
in the guidelines.
Reporting entity means an entity that
has submitted a report under the
1605(b) program that has been accepted
by the Energy Information
Administration.
Reporting year means the year that is
the subject of a report to DOE.
Sequestration means the process by
which CO2 is removed from the
atmosphere, either through biologic
processes or physical processes.
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Simplified Emission Inventory Tool
(SEIT) is a computer-based method, to
be developed and made readily
accessible by EIA, for translating
common physical indicators into an
estimate of greenhouse gas emissions.
Sink means an identifiable discrete
location, set of locations, or area in
which CO2 or some other greenhouse
gas is sequestered.
Small emitter means an entity whose
annual emissions are less than or equal
to 10,000 metric tons of CO2 equivalent,
as determined in accordance with
§ 300.5(c), and that chooses to be treated
as a small emitter under the guidelines.
Source means any land, facility,
process, vehicle or activity that releases
a greenhouse gas.
Start year means the year upon which
the initial entity statement is based and
the last year of the initial base period(s).
Subentity means a component of any
entity, such as a discrete business line,
facility, plant, vehicle fleet, or energy
using system, which has associated with
it emissions of greenhouse gases that
can be distinguished from the emissions
of all other components of the same
entity and, when summed with the
emissions of all other subentities, equal
the entity’s total emissions.
Total emissions means the total
annual contribution of the greenhouse
gases (as defined in this section) to the
atmosphere by an entity, including both
direct and indirect entity-wide
emissions.
United States or U.S. means the 50
States, the District of Columbia, the
Commonwealth of Puerto Rico, the
Commonwealth of the Northern Mariana
Islands, Guam, American Samoa, and
any other territory of the United States.
§ 300.3 Guidance for defining and naming
the reporting entity.
(a) A reporting entity must be
composed of one or more businesses,
public or private institutions or
organizations, households, or other
entities having operations that annually
release emissions, at least in part, in the
United States. Entities may be defined
by, as appropriate, a certificate of
incorporation, corporate charter,
corporate filings, tax identification
number, or other legal basis of
identification recognized under any
Federal, State or local law or regulation.
If a reporting entity is composed of more
than one entity, all of the entities
included must be responsible to the
same management hierarchy and all
entities that have the same management
hierarchy must be included in the
reporting entity.
(b) All reporting entities are strongly
encouraged to define themselves at the
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highest level of aggregation. To achieve
this objective, DOE suggests the use of
a corporate-level definition of the entity,
based on filings with the Securities and
Exchange Commission or institutional
charters. While reporting at the highest
level of aggregation is encouraged, DOE
recognizes that certain businesses and
institutions may conclude that reporting
at some lower level is desirable. Federal
agencies are encouraged to report at the
agency or departmental level, but
distinct organizational units (such as a
Department of the Interior Fish and
Wildlife Service National Wildlife
Refuge) may report directly if
authorized by their department or
agency. Once an entity has determined
the level of corporate or institutional
management at which it will report (e.g.,
the holding company, subsidiary,
regulated stationary source, state
government, agency, refuge, etc.), the
entity must include all elements of the
organization encompassed by that
management level and exclude any
organizations that are managed
separately. For example, if two
subsidiaries of a parent company are to
be covered by a single report, then all
subsidiaries of that parent company
must also be included. Similarly, if a
company decides to report on the U.S.
and Canadian subsidiaries of its North
American operations unit, it must also
report on any other subsidiaries of its
North American unit, such as a Mexican
subsidiary.
(c) A name for the defined entity must
be specified by all reporters. For entities
that intend to register reductions, this
should be the name commonly used to
represent the activities being reported,
as long as it is not also used to refer to
substantial activities not covered by the
entity’s reports. While DOE believes
entities should be given considerable
flexibility in defining themselves at an
appropriate level of aggregation, it is
essential that the name assigned to an
entity that intends to register reductions
corresponds closely to the scope of the
operations and emissions covered by its
report. If, for example, an individual
plant or operating unit is reporting as an
entity, it should be given a name that
corresponds to the specific plant or unit,
and not to the responsible subsidiary or
corporate entity. In order to distinguish
a parent company from its subsidiaries,
the name of the parent company
generally should not be incorporated
into the name of the reporting
subsidiary, but if it is, the name of the
parent company usually should be
secondary.
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§ 300.4 Selecting organizational
boundaries.
(a) Each reporting entity must disclose
in its entity statement the approach
used to establish its organizational
boundaries, which should be consistent
with the following guidelines:
(1) In general, entities should use
financial control as the primary basis for
determining their organizational
boundaries, with financial control
meaning the ability to direct the
financial and operating policies of all
elements of the entity with a view to
gaining economic or other benefits from
its activities over a period of many
years. This approach should ensure that
all sources, including those controlled
by subsidiaries, that are wholly or
largely owned by the entity are covered
by its reports. Sources that are under
long-term lease of the entity may,
depending on the provisions of such
leases, also be considered to be under
the entity’s financial control. Sources
that are temporarily leased or operated
by an entity generally would not be
considered to be under its financial
control.
(2) Entities may establish
organizational boundaries using
approaches other than financial control,
such as equity share or operational
control, but must disclose how the use
of these other approaches results in
organizational boundaries that differ
from those resulting from using the
financial control approach.
(3) Emissions from facilities or
vehicles that are partially-owned or
leased may be included at the entity’s
discretion, provided that the entity has
taken reasonable steps to assure that
doing so does not result in the double
counting of emissions, sequestration or
emission reductions. Emissions
reductions or sequestration associated
with land, facilities or other sources not
owned or leased by an entity may not
be included in the entity’s reports under
the program unless the entity has longterm control over the emissions or
sequestration of the source and the
owner of the source has agreed that the
emissions or sequestration may be
included in the entity’s report.
(4) If the scope of a defined entity
extends beyond the United States, the
reporting entity should use the same
approach to determining its
organizational boundaries in the U.S.
and outside the U.S.
(b) Each reporting entity must keep
separate reports on emissions or
emission reductions that occur within
its defined boundaries and those that
occur outside its defined boundaries.
Entities must also keep separate reports
on emissions and emission reductions
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that occur outside the United States and
those that occur within the United
States.
(c) An entity that intends to register
its entity-wide emissions reductions
must document and maintain its
organizational boundary for accounting
and reporting purposes.
§ 300.5
Submission of an entity statement.
(a) Determining the type of reporting
entity. The entity statement
requirements vary by type of reporting
entity. For the purposes of these
guidelines, there are three types of
entities:
(1) Large emitters that intend to
register emission reductions;
(2) Small emitters that intend to
register emission reductions; and
(3) Emitters that intend to report, but
not register emission reductions.
(b) Choosing a start year. The first
entity statement describes the make-up,
operations and boundaries of the entity,
as they existed in the start year.
(1) For all entities, it is the year
immediately preceding the first year for
which the entity intends to register
emission reductions and the last year of
the initial base period(s).
(2) For entities intending to register
emission reductions, the start year may
be no earlier than 2002, unless the
entity has made a commitment to
reduce its entity-wide emissions under
the Climate Leaders or Climate VISION
program. An entity that has made such
a commitment may establish a start year
derived from the base period of the
commitment, as long as it is no earlier
than 2000.
(i) For a large emitter, the start year is
the first year for which the entity
submits a complete emissions inventory
under the 1605(b) program.
(ii) The entity’s emissions in its start
year or its average annual emissions
over a period of up to four years ending
in the start year determine whether it
qualifies to begin reporting as a small
emitter.
(3) For entities not intending to
register reductions, the start year may be
no earlier than 1990.
(c) Determining and maintaining large
or small emitter reporting status. (1)
Any entity that intends to register
emission reductions can choose to
participate as a large emitter, but only
an entity that has demonstrated that its
annual emissions are less than or equal
to 10,000 metric tons of CO2 equivalent
may participate as a small emitter. To
demonstrate that its annual emissions
are less than or equal to 10,000 metric
tons of CO2 equivalent, an entity must
submit either an estimate of its
emissions during its chosen start year or
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an estimate of its average annual
emissions over a continuous period not
to exceed four years of time ending in
its chosen start year, as long as the
operations and boundaries of the entity
have not changed significantly during
that period.
(2) An entity must estimate its total
emissions using methods specified in
Chapter 1 of the Technical Guidelines
(incorporated by reference, see § 300.13)
or by using the Simplified Emission
Inventory Tool (SEIT) provided by EIA
and also discussed in Chapter 1. The
results of this estimate must be reported
to EIA. [Note: emission estimates
developed using SEIT may not be used
to prepare, in whole or part, entity-wide
emission inventories required for the
registration of reductions.]
(3) After starting to report, each small
emitter must annually certify that the
emissions-related operations and
boundaries of the entity have not
changed significantly since the previous
report. A new estimate of total
emissions must be submitted after any
significant increase in emissions, any
change in the operations or boundaries
of the small emitter, or every five years,
whichever occurs first. Small emitters
with estimated annual emissions of over
9,000 metric tons of CO2 equivalent
should re-estimate and submit their
emissions annually. If an entity
determines that it must report as a large
emitter, then it must continue to report
as a large emitter in all future years in
order to ensure a consistent time series
of reports. Once a small emitter becomes
a large emitter, it must begin reporting
in conformity with the reporting
requirements for large emitters.
(d) Entity statements for large emitters
intending to register reductions. When a
large emitter intending to register
emission reductions first reports under
these guidelines, it must provide the
following information in its entity
statement:
(1) The name to be used to identify
the participating entity;
(2) The legal basis of the named
entity;
(3) The criteria used to determine:
(i) The organizational boundaries of
the entity, if other than financial
control; and
(ii) The sources of emissions included
or excluded from the entity’s reports,
such as sources excluded as de minimis
emissions;
(4) The names of any parent or
holding companies the activities of
which will not be covered
comprehensively by the entity’s reports;
(5) The names of any large
subsidiaries or organizational units
covered comprehensively by the entity’s
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reports. All subsidiaries of the entity
must be covered by the entity’s reports,
but only large subsidiaries must be
specifically identified in the entity
statement;
(6) A list of each country where
operations occur, if the entity is
including any non-U.S. operations in its
report;
(7) A description of the entity and its
primary U.S. economic activities, such
as electricity generation, product
manufacturing, service provider or
freight transport; for each country listed
under paragraph (d)(6) of this section,
the large emitter should describe the
economic activity in that country.
(8) A description of the types of
emission sources or sinks to be covered
in the entity’s emission inventories,
such as fossil fuel power plants,
manufacturing facilities, commercial
office buildings or heavy-duty vehicles;
(9) The names of other entities that
substantially share the ownership or
operational control of sources that
represent a significant part of the
reporting entity’s emission inventories,
and a certification that, to the best of the
certifier’s knowledge, the direct
greenhouse gas emissions and
sequestration in the entity’s report are
not included in reports filed by any of
these other entities to the 1605(b)
program; and
(10) Identification of the start year.
(e) Entity statements for small
emitters intending to register reductions.
When a small emitter intending to
register emission reductions first reports
under these guidelines, it must provide
the following information in its entity
statement:
(1) The name to be used to identify
the participating entity;
(2) The legal basis of the named
entity;
(3) An identification of the entity’s
control over the activities covered by
the entity’s reports, if other than
financial control;
(4) The names of any parent or
holding companies the activities of
which will not be covered
comprehensively by the entity’s reports;
(5) An identification or description of
the primary economic activities of the
entity, such as agricultural production,
forest management or household
operation; if any of the economic
activities covered by the entity’s reports
occur outside the U.S., a listing of each
country in which such activities occur;
(6) An identification or description of
the specific activity (or activities) and
the emissions, avoided emissions or
sequestration covered by the entity’s
report, such as landfill gas recovery or
forest sequestration;
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(7) A certification that, to the best of
the certifier’s knowledge, the direct
greenhouse gas emissions and
sequestration in the entity’s report are
not included in reports filed by any
other entities reporting to the 1605(b)
program; and
(8) Identification of the start year.
(f) Entity statements for reporting
entities not registering reductions. When
a participant not intending to register
emission reductions first reports under
this part, it must, at a minimum,
provide the following information in its
entity statement:
(1) The name to be used to identify
the reporting entity;
(2) The legal basis of the entity;
(3) An identification of the entity’s
control over the activities covered by
the entity’s reports, if other than
financial control;
(4) A description of the entity and its
primary economic activities, such as
electricity generation, product
manufacturing, service provider, freight
transport, agricultural production, forest
management or household operation; if
any of the economic activities covered
by the entity’s reports occur outside the
United States, a listing of each country
in which such activities occur; and
(5) A description of the types of
emission sources or sinks, such as fossil
fuel power plants, manufacturing
facilities, commercial office buildings or
heavy-duty vehicles, covered in the
entity’s reports of emissions or emission
reductions.
(g) Changing entity statements. (1)
Reporting entities are required to
annually review and, if necessary,
update their entity statements.
(2) From time to time, a reporting
entity may choose to change the scope
of activities included within the entity’s
reports or the level at which the entity
wishes to report. A reporting entity may
also choose to change its organizational
boundaries, its base period, or other
elements of its entity statement. For
example, companies buy and sell
business units, or equity share
arrangements may change. In general,
DOE encourages changes in the scope of
reporting that expand the coverage of an
entity’s report and discourages changes
that reduce the coverage of such reports
unless they are caused by divestitures or
plant closures. Any such changes
should be reported in amendments to
the entity statement, and major changes
may warrant or require changes in the
base values used to calculate emission
reductions and, in some cases, the
entity’s base periods. Changes in the
scope of reporting made on or before
May 31 of a given calendar year must be
reflected in the report submitted
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covering emissions and reductions for
the following calendar year. Reporting
entities may choose to postpone
incorporating changes in the scope of
reporting made after May 31 until
submitting the report covering
emissions and reductions for the year
after the following calendar year.
However, in no case should there be an
interruption in the annual reports of
entities registering emission reductions.
Chapter 2 of the Technical Guidelines
(incorporated by reference, see § 300.13)
provides more specific guidance on how
such changes should be reflected in
entity statements, reports, and emission
reduction calculations.
(h) Documenting changes in amended
entity statements. A reporting entity’s
entity statement in subsequent reports
should focus primarily on changes since
the previous report. Specifically, the
subsequent entity statement should
report the following information:
(1) For significant changes in the
reporting entity’s scope or
organizational boundaries, the entity
should document:
(i) The acquisition or divestiture of
discrete business units, subsidiaries,
facilities, and plants;
(ii) The closure or opening of
significant facilities;
(iii) The transfer of economic activity
to or from specific subentities covered
by the entity’s reports, such as the
transfer of operations to non-U.S.
subsidiaries;
(iv) Significant changes in land
holdings (applies to entities reporting
on greenhouse gas emissions or
sequestration related to land use, land
use change, or forestry);
(v) Whether the reporting entity is
reporting at a higher level of aggregation
than it did in the previous report, and
if so, a listing of the subsidiary entities
that are now aggregated under a revised
conglomerated entity, including a listing
of any non-U.S. operations to be added
and the specific countries in which
these operations are located; and
(vi) Changes in its activities or
operations (e.g., changes in output,
contractual arrangements, equipment
and processes, outsourcing or
insourcing of significant activities) that
are likely to have a significant effect on
emissions, together with an explanation
of how it believes the changes in
economic activity influenced its
reported emissions or sequestrations.
§ 300.6
Emissions inventories.
(a) General. The objective of an
emission inventory is to provide a full
accounting of an entity’s emissions for
a particular year, including direct
emissions of the first six categories of
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gases listed in the definition of
‘‘greenhouse gases’’ in § 300.2, indirect
emissions specified in paragraph (e) of
this section, and all sequestration or
other changes in carbon stocks. An
emission inventory must be prepared in
accordance with Chapter 1 of the
Technical Guidelines (incorporated by
reference, see § 300.13). An inventory
does not include avoided emissions or
any offset reductions, and is not
subsequently adjusted to reflect future
acquisitions, divestitures or other
changes to the reporting entity (although
a reporting entity often makes these
types of adjustments when calculating
emission reductions under the
guidelines). Entity-wide inventories are
a prerequisite for the registration of
emission reductions by entities with
average annual emissions of more than
10,000 metric tons of CO2 equivalent.
Entities that have average annual
emissions of less than or equal to 10,000
metric tons of CO2 equivalent are
eligible to register emission reductions
associated with specific activities
without also reporting an inventory of
the total emissions, but such entities
should inventory and report the
emissions associated with the specific
activity(ies) they do cover in their
reports.
(b) Quality requirements for emission
inventories. The Technical Guidelines
(incorporated by reference, see § 300.13)
usually identify more than one
acceptable method of measuring or
estimating greenhouse gas emissions.
Each acceptable method is rated A, B, C
or D, with A methods usually
corresponding to the highest quality
method available and D methods
representing the lowest quality method
that may be used. Each letter is assigned
a numerical rating reflecting its relative
quality, 4 for A methods, 3 for B
methods, 2 for C methods and 1 for D
methods. Entities that intend to register
emission reductions must use emission
inventory methods that result in a
quantity-weighted average quality rating
of at least 3.0.
(1) Entities may at any time choose to
modify the measurement or estimation
methods that they use for their current
or future year emission inventories.
Such modifications would enable
entities to gradually improve the quality
of the ratings over time, but prior year
inventories may be modified only to
correct significant errors.
(2) Entities that have had their
emission quantities and the quantityweighted quality rating of their
emissions inventory independently
verified may report their emissions and
average quality ratings by greenhouse
gas, indirect emissions and
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sequestration, rather than by source or
sink category.
(3) Entities that certify that they have
used only A or B methods, may forego
indicating in their reports the quality
ratings of the methods used and may
forego calculating the quantity-weighted
average quality of their emission
inventories.
(c) Using estimation methods not
included in the Technical Guidelines.
An entity may obtain DOE approval for
the use of an estimation method not
included in the Technical Guidelines
(incorporated by reference, see § 300.13)
if the method covers sources not
described in the Technical Guidelines,
or if the method provides more accurate
results for the entity’s specific
circumstances than the methods
described in the Technical Guidelines.
If an entity wishes to propose the use of
a method that is not described in the
Technical Guidelines, the entity must
provide a written description of the
method, an explanation of how the
method is implemented (including data
requirements), empirical evidence of the
method’s validity and accuracy, and a
suggested rating for the method to
DOE’s Office of Policy and International
Affairs (with a copy to EIA). DOE
reserves the right to deny the request, or
to assign its own rating to the method.
By submitting this information, the
entity grants permission to DOE to
incorporate the method in a future
revision of the Technical Guidelines.
(d) Direct emissions inventories.
Direct greenhouse gas emissions that
must be reported are the emissions
resulting from stationary or mobile
sources within the organizational
boundaries of an entity, including but
not limited to emissions resulting from
combustion of fossil fuels, process
emissions, and fugitive emissions.
Process emissions (e.g., PFC emissions
from aluminum production) must be
reported along with fugitive emissions
(e.g., leakage of greenhouse gases from
equipment).
(e) Inventories of indirect emissions
associated with purchased energy. (1)
To provide a clear incentive for the
users of electricity and other forms of
purchased energy to reduce demand, an
entity must include the indirect
emissions from the consumption of
purchased electricity, steam, and hot or
chilled water in the entity’s inventory as
indirect emissions. To avoid double
counting among entities, the entity must
report all indirect emissions separately
from its direct emissions. Entities
should use the methods for quantifying
indirect emissions specified in the
Technical Guidelines (incorporated by
reference, see § 300.13).
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(2) Entities may choose to report other
forms of indirect emissions, such as
emissions associated with employee
commuting, materials consumed or
products produced, although such other
indirect emissions may not be included
in the entity’s emission inventory and
may not be the basis for registered
emission reductions. All such reports of
other forms of indirect emissions must
be distinct from reports of indirect
emissions associated with purchased
energy and must be based on emission
measurement or estimation methods
identified in the Technical Guidelines
(incorporated by reference, see § 300.13)
or approved by DOE.
(f) Entity-level inventories of changes
in terrestrial carbon stocks. Annual
changes in managed terrestrial carbon
stocks should be comprehensively
assessed and reported across the entity,
and the net emissions resulting from
such changes included in the entity’s
emissions inventory. Entities should use
the methods for estimating changes in
managed terrestrial carbon stocks
specified in the Technical Guidelines
(incorporated by reference, see
§ 300.13).
(g) Treatment of de minimis emissions
and sequestration. (1) Although the goal
of the entity-wide reporting requirement
is to provide an accurate and
comprehensive estimate of total
emissions, there may be small emissions
from certain sources that are unduly
costly or otherwise difficult to measure
or reliably estimate annually. An entity
may exclude particular sources of
emissions or sequestration if the total
quantities excluded represent less than
or equal to 3 percent of the total annual
CO2 equivalent emissions of the entity.
The entity must identify the types of
emissions excluded and provide an
estimate of the annual quantity of such
emissions using methods specified in
the Technical Guidelines (incorporated
by reference, see § 300.13) or by using
the Simplified Emissions Inventory Tool
(SEIT). The results of this estimate of
the entity’s total excluded annual
emissions must be reported to DOE
together with the entity’s initial entity
statement.
(2) After starting to report, each
reporting entity that excludes from its
annual reports any de minimis
emissions must re-estimate the quantity
of excluded emissions after any
significant increase in such emissions,
or every five years, whichever occurs
sooner.
(h) Separate reporting of domestic
and international emissions. Non-U.S.
emissions included in an entity’s
emission inventory must be separately
reported and clearly distinguished from
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emissions originating in the U.S.
Entities must identify any countryspecific factors used in the preparation
of such reports.
(i) Covered gases. Entity-wide
emissions inventories must include the
emissions of the first six categories of
named gases listed in the definition of
‘‘greenhouse gases’’ in § 300.2. Entities
may report chlorofluorocarbons and
other greenhouse gases with
quantifiable climate forcing effects as
long as DOE has established a method
for doing so, but such gases must be
reported separately and emission
reductions, if any, associated with such
other gases are not eligible for
registration.
(j) Units for reporting. Emissions and
sequestration should be reported in
terms of the mass (not volume) of each
gas, using metric units (e.g., metric tons
of methane). Entity-wide and subentity
summations of emissions and
reductions from multiple sources must
be converted into CO2 equivalent units
using the global warming potentials for
each gas in the International Panel on
Climate Change’s Third Assessment (or
most recent) Report, as specified in the
Technical Guidelines (incorporated by
reference, see § 300.13). Entities should
specify the units used (e.g., kilograms,
or metric tons). Entities may need to use
the standard conversion factors
specified in the Technical Guidelines to
convert existing data into the common
units required in the entity-level report.
Emissions from the consumption of
purchased electricity must be calculated
by region (from the list provided by
DOE in the Technical Guidelines) or
country, if outside the United States.
Consumption of purchased steam or
chilled/hot water must be reported
according to the type of system and fuel
used to generate it (from the list
provided by DOE in the Technical
Guidelines). Entities must convert
purchased energy to CO2 equivalents
using the conversion factors in the
Technical Guidelines. Entities should
also provide the physical quantities of
each type of purchased energy covered
by their reports.
§ 300.7
Net emission reductions.
(a) Entities that intend to register
emission reductions achieved must
comply with the requirements of this
section. Entities may voluntarily follow
these procedures if they want to
demonstrate the achievement of net,
entity-wide reductions for years prior to
the earliest year permitted for
registration. Only large emitters must
follow the requirements of paragraph (b)
of this section, but small emitters may
do so voluntarily. Only entities that
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qualify as small emitters may use the
special procedures in paragraph (c) of
this section. Entities seeking to register
emission reductions achieved by other
entities (offsets) must certify that these
emission reductions were calculated in
a manner consistent with the
requirements of paragraph (d) of this
section and use the emission reduction
calculation methods identified in
§ 300.8. All entities seeking to register
emission reductions must comply with
the requirements of paragraph (e) of this
section. Only reductions in the
emissions of the first six categories of
gases listed in the definition of
‘‘greenhouse gases’’ in § 300.2 are
eligible for registration.
(b) Assessing net emission reductions
for large emitters. (1) Entity-wide
reporting is a prerequisite for registering
emission reductions by entities with
average annual emissions of more than
10,000 metric tons of CO2 equivalent.
Net annual entity-wide emission
reductions must be based, to the
maximum extent practicable, on a full
assessment and sum total of all changes
in an entity’s emissions, eligible
avoided emissions and sequestration
relative to the entity’s established base
period(s). This assessment must include
all entity emissions, including the
emissions associated with any non-U.S.
operations covered by the entity
statement, although the reductions
achieved by non-U.S. operations must
be separately totaled prior to being
integrated with the net emission
reductions achieved by U.S. operations.
It must include the annual changes in
the total emissions of the entity,
including the total emissions of each of
the subentities identified in its entity
statement. All changes in emissions,
avoided emissions, and sequestration
must be determined using methods that
are consistent with the guidelines
described in § 300.8 of this part.
(2) If it is not practicable to assess the
changes in net emissions resulting from
certain entity activities using at least
one of the methods described in § 300.8
of this part, the entity may exclude them
from its estimate of net emission
reductions. The entity must identify as
one or more distinct subentities the
sources of emissions excluded for this
reason and describe the reasons why it
was not practicable to assess the
changes that had occurred. DOE
believes that few emission sources will
be excluded for this reason, but has
identified at least two situations where
such an exclusion would be warranted.
For example, it is likely to be impossible
to assess the emission changes
associated with a new manufacturing
plant that produces a product for which
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the entity has no historical record of
emissions or emissions intensity
(emissions per unit of product output).
However, once the new plant has been
operational for at least a full year, a base
period and base value(s) for the new
plant could be established and its
emission changes assessed in the
following year. Until the emission
changes of this new subentity can be
assessed, it should be identified in the
entity’s report as a subentity for which
no assessment of emission changes is
practicable. The other example involves
a subentity that has reduced its output
below the levels of its base period. In
such a case, the subentity could not use
the absolute emissions method and may
also be unable to identify an effective
intensity metric or other method.
(3) In calculating its net annual
emission reductions, an entity should
exclude any emissions or sequestration
that have been excluded from the
entity’s inventory. The entity should
also exclude all de minimis and
biogenic emissions that are excluded
from the entity’s inventory of
greenhouse gas emissions from its
assessments of emission changes.
(c) Assessing emission reductions for
entities with small emissions. (1)
Entities with average annual emissions
of less than or equal to 10,000 metric
tons of CO2 equivalent are not required
to inventory their total emissions or
assess all changes in their emissions,
eligible avoided emissions and
sequestration to qualify for registered
reductions. These entities may register
emission reductions that have occurred
since 2002 and that are associated with
one or more specific activities, as long
as they:
(i) Perform a complete assessment of
the annual emissions and sequestration
associated with each of the activities
upon which they report, using methods
that meet the same quality requirements
applicable to entity-wide emission
inventories; and
(ii) Determine the changes in the
emissions, eligible avoided emissions or
sequestration associated with each of
these activities.
(2) An entity reporting as a small
emitter must report on one or more
specific activities and is encouraged, but
not required to report on all activities
occurring within the entity boundary.
Examples of small emitter activities
include: vehicle operations; product
manufacturing processes; building
operations or a distinct part thereof,
such as lighting; livestock operations;
crop management; and power
generation. For example, a farmer
managing several woodlots and also
producing a wheat crop may report
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emission reductions associated with
managing an individual woodlot.
However, the farmer must also assess
and report the net sequestration
resulting from managing all the
woodlots within the entity’s boundary.
The small emitter is not required to
report on emissions or reductions
associated with growing the wheat crop.
(3) A small emitter must certify that
the reductions reported were not caused
by actions likely to cause increases in
emissions elsewhere within the entity’s
operations. This certification should be
based on an assessment of the likely
direct and indirect effects of the actions
taken to reduce greenhouse gas
emissions.
(d) Net emission reductions achieved
by other entities (offset reductions or
emission reductions submitted by
aggregators). A reporting entity or
aggregator under certain conditions may
report or register all or some of the net
emission reductions achieved by
entities that choose not to report under
the section 1605(b) program. In all
cases, an agreement must exist between
the reporting entity or aggregator and
the other entity that specifies the
quantity of the emission reductions (or
increases) achieved by the other entity
that may be reported or registered as an
offset reduction by the reporting entity
or aggregator. A large emitter that is
reporting on behalf of other entities
must meet all of the requirements
applicable to large emitters, including
submission of an entity statement, an
emissions inventory, and an entity-wide
assessment of emission reductions. If an
aggregator is a small emitter, it may
choose to report only on the activities,
emissions and emission reductions of
the entities on behalf of which it is
reporting and not to report on any of its
own activities or emission reductions.
The reporting entity or aggregator must
include in its report all of the
information on the other entity,
including an entity statement, an
emissions inventory (when required),
and an assessment of emission
reductions that would be required if the
other entity were directly reporting to
EIA. The net emissions reductions (or
increases) of each other entity will be
evaluated separately by EIA to
determine whether they are eligible for
registration in accordance with the
guidelines of this part. Those registered
reductions (or increases) assigned by the
other entity, by agreement, to a
reporting entity or aggregator will be
included in EIA’s summary of all
registered offset reductions for that
entity or aggregator. If the agreement
between the reporting entity and other
entity is discontinued, for any reason,
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the reporting entity must inform EIA
and must identify any emission
reductions previously reported that
could be attributable to an increase in
the carbon stocks of the other entity.
Such reductions will be removed by EIA
from the records of the reporting entity’s
offset reductions.
(e) Net emission reductions to be
reported by other entities as offset
reductions. Entities must identify in
their report the quantity of any net
emission reductions covered by the
report, if any, that another entity will
report as an offset reduction, including
the name of the other entity;
(f) Adjusting for year-to-year increases
in net emissions. (1) Normally, net
annual emission reductions for an entity
are calculated by summing the net
annual changes in emissions, eligible
avoided emissions and sequestration, as
determined using the calculation
methods identified in § 300.8 and
according to the procedures described
in paragraph (b) of this section for large
emitters, paragraph (c) for small emitters
of this section for small emitters, and
paragraph (d) of this section for offsets.
However, if the entity experienced a net
increase in emissions for one or more
years, these increases must be reported
and taken into account in calculating
any future year reductions. If the entity
subsequently achieves net annual
emission reductions, the net increases
experienced in the preceding year(s)
must be more than offset by these
reductions before the entity can once
again register emission reductions. For
example, if an entity achieved a net
emission reduction of 5,000 metric tons
of CO2 equivalent in its first year, a net
increase of 2,000 metric tons in its
second year, and a net reduction of
3,000 metric tons in its third year, it
would be able to register a 5,000 metric
ton reduction in its first year, no
reduction in its second year, and a 1,000
metric ton reduction in its third year
(3,000–2,000). The entity must file full
reports for each of these three years. Its
report for the second year would
indicate the net increase in emissions
and this increase would be noted in
EIA’s summary of the entity’s report for
that year and for any future year, until
the emissions increase was entirely
offset by subsequent emission
reductions. If this same entity achieved
a net reduction of only 1,000 metric tons
in its third year, it would not be able to
register additional reductions until it
had, in some future year, offset more
than its second year increase of 2,000
metric tons.
(2) [Reserved]
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§ 300.8
Calculating emission reductions.
(a) Choosing appropriate emission
reduction calculation methods. (1) An
entity must choose the method or
methods it will use to calculate
emission reductions from the list
provided in paragraph (h) of this
section. Each of the calculation methods
has special characteristics that make it
applicable to only certain types of
emissions and activities. An entity
should select the appropriate
calculation method based on several
factors, including:
(i) How the entity’s subentities are
defined;
(ii) How the reporter will gather and
report emissions data; and
(iii) The availability of other types of
data that might be needed, such as
production or output data.
(2) For some entities, a single
calculation method will be sufficient,
but many entities may need to apply
more than one method because discrete
components of the entity require
different calculation methods. In such a
case, the entity will need to select a
method for each subentity (or discrete
component of the entity with
identifiable emission or reductions).
The emissions and output measure
(generally a physical measure) of each
subentity must be clearly distinguished
and reported separately. Guidance on
the selection and specification of
calculation methods is provided in
Chapter 2 of the Technical Guidelines
(incorporated by reference, see
§ 300.13).
(b) Identifying subentities for
calculating reductions. If more than one
calculation method is to be used, an
entity must specify the portion of the
entity (the subentity) to which each
method will be applied. Each subentity
must be clearly identified. From time to
time, it may be necessary to modify
existing or create new subentities. The
entity must provide to EIA a full
description of such changes, together
with an explanation of why they were
required.
(c) Choosing a base period for
calculating reductions. In general, the
base period used in calculating emission
reductions is the single year or up to
four-year period average immediately
preceding the first year of calculated
emission reductions.
(d) Establishing base values. To
calculate emission reductions, an entity
must establish a base value against
which to compare reporting year
performance. The minimum
requirements for base values for each
type of calculation method are specified
in Chapter 2 of the Technical Guidelines
(incorporated by reference, see
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§ 300.13). In most cases, an historic base
value, derived from emissions or other
data gathered during the base period, is
the minimum requirement specified.
Entities may, however, choose to
establish base values that are more
stringent than the base values derived
from the methods specified in Chapter
2 of the Technical Guidelines as long as
their report indicates the rationale for
the alternative base value and
demonstrates that it would result in a
smaller quantity of emission reductions.
(e) Emission reduction and subentity
statements. For each subentity, an entity
must submit to EIA the following
information:
(1) An identification and description
of the method used to calculate
emission reductions, including:
(i) The type of calculation method;
(ii) The measure of output used (if
any); and
(iii) The method-specific base period
for which any required base value will
be calculated.
(2) The base period used in
calculating reductions. When an entity
starts to report, the base period used in
calculating reductions must end in the
start year. However, over time the
reporting entity may find it necessary to
revise or establish new base periods and
base values in response to significant
changes in processes or output of the
subentity.
(3) A description of the subentity and
its primary economic activity or
activities, such as electricity generation,
product manufacturing, service
provider, freight transport, or household
operation; and
(4) A description of the emission
sources or sinks covered, such as fossil
fuel power plants, manufacturing
facilities, commercial office buildings or
heavy-duty vehicles.
(f) Changes in calculation methods,
base periods and base values. When
significant changes occur in the
composition or output of reporting
entities, a reporting entity may need to
change previously specified calculation
methods, base periods or base values. A
reporting entity should make such
changes only if necessary and it should
fully document the reasons for any
changes. The Technical Guidelines
(incorporated by reference, see § 300.13)
describe when such changes should be
made and what information on such
changes must be provided to DOE. In
general, such changes should not result
in any alterations to previously reported
or registered emission reductions. A
reporting entity may alter previously
reported or registered emission
reductions only if necessary to correct
significant errors.
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(g) Continuous reporting. To ensure
that the summation of entity annual
reports accurately represents net, multiyear emission reductions, an entity must
submit a report every year, beginning
with the first reduction year. An entity
may use a specific base period to
determine emission reductions in a
given future year only if the entity has
submitted qualified reports for each
intervening year. If an interruption
occurs in the annual reports of an entity,
the entity must subsequently report on
all missing years prior to qualifying for
the registration of additional emission
reductions.
(h) Calculation methods. An entity
must calculate any change in emissions,
avoided emissions or sequestration
using one or more of the methods
described in this paragraph and in the
Technical Guidelines (incorporated by
reference, see § 300.13).
(1) Changes in emissions intensity. An
entity may use emissions intensity as a
basis for determining emission
reductions as long as the entity selects
a measure of output that is:
(i) A reasonable indicator of the
output produced by the entity;
(ii) A reliable indicator of changes in
the entity’s activities;
(iii) Related to emissions levels; and
(iv) Any appropriate adjustments for
acquisitions, divestitures, insourcing,
outsourcing, or changes in products
have been made, as described in the
Technical Guidelines (incorporated by
reference, see § 300.13).
(2) Changes in absolute emissions. An
entity may use changes in the absolute
(actual) emissions (direct and/or
indirect) as a basis for determining net
emission reductions as long as the entity
makes only those adjustments required
by the Technical Guidelines
(incorporated by reference, see
§ 300.13). An entity intending to register
emission reductions may use this
method only if the entity demonstrates
in its report that any reductions derived
from such changes were not achieved as
a result of reductions in the output of
the entity, and certifies that emission
reductions are not the result of major
shifts in the types of products or
services produced. Entities may report,
but not register, such reductions even if
the output associated with such
emissions is declining.
(3) Changes in carbon storage (for
actions within entity boundaries). An
entity may use changes in carbon
storage as a basis for determining net
emission reductions as long as the entity
uses estimation and measurement
methods that comply with the Technical
Guidelines (incorporated by reference,
see § 300.13), and has included an
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assessment of the net changes in all
sinks in its inventory.
(4) Changes in avoided emissions (for
actions within entity boundaries). An
entity may use changes in avoided
emissions to determine its emission
reductions. Avoided emissions eligible
to be included in the calculation of net
emission reductions that qualify for
registration include those associated
with the sale of electricity, steam, hot
water or chilled water generated from
non-emitting or low-emitting sources as
a basis for determining net emission
reductions as long as:
(i) The measurement and calculation
methods used comply with the
Technical Guidelines (incorporated by
reference, see § 300.13);
(ii) The entity certifies that any
increased sales were not attributable to
the acquisition of a generating facility
that had been previously operated,
unless the entity’s base period includes
generation values from the acquired
facility’s operation prior to its
acquisition; and
(iii) Generators of distributed energy
that have net emissions in their base
period and intend to report reductions
resulting from changes in eligible
avoided emissions, use a method
specified in the Technical Guidelines
(incorporated by reference, see § 300.13)
that integrates the calculation of
reductions resulting from both changes
in emissions intensity and changes in
avoided emissions.
(5) Action-specific emission
reductions (for actions within entity
boundaries). A number of source- or
situation-specific methods are provided
in the Technical Guidelines and these
methods must be used to assess the
annual changes in emissions for the
specific sources or situation addressed
by these methods. In addition, a generic
action-specific method is identified in
the Technical Guidelines. An entity
intending to register reductions may use
the generic action-specific approach
only if it is not possible to measure
accurately emission changes by using
one of the methods identified in
paragraphs (h)(1) through (h)(4) of this
section. Entities that intend to register
reductions and that use the generic
action-specific approach must explain
why it is not possible to use any of these
other methods. An entity not intending
to register reductions may use the
generic action-specific method to
determine emission reductions, as long
as the entity demonstrates that the
estimate is based on analysis that:
(i) Uses output, utilization and other
factors that are consistent, to the
maximum extent practicable, with the
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action’s actual performance in the year
for which reductions are being reported;
(ii) Excludes any emission reductions
that might have resulted from reduced
output or were caused by actions likely
to be associated with increases in
emissions elsewhere within the entity’s
operations; and
(iii) Uses methods that are in
compliance with the Technical
Guidelines (incorporated by reference,
see § 300.13).
(i) Summary description of actions
taken to reduce emissions. Each
reported emission reduction must be
accompanied by an identification of the
types of actions that were the likely
cause of the reductions achieved.
Entities are also encouraged to include
in their reports information on the
benefits and costs of the actions taken
to reduce greenhouse gas emissions,
such as the expected rates of return, life
cycle costs or benefit to cost ratios,
using appropriate discount rates.
(j) Emission reductions associated
with plant closings, voluntary actions
and government (including non-U.S.
regulatory regimes) requirements. (1)
Each report of emission reductions must
indicate whether the reported emission
reductions were the result, in whole or
in part, of plant closings, voluntary
actions, or government requirements.
EIA will presume that reductions that
were not the result of plant closings or
government requirements are the result
of voluntary actions.
(2) If emission reductions were, in
whole or in part, the direct result of
plant closings that caused a decline in
output, the report must identify the
reductions as such; these reductions do
not qualify for registration. EIA will
presume that reductions calculated
using the emissions intensity method do
not result from a decline in output.
(3) If the reductions were associated,
in whole or part, with U.S. or non-U.S.
government requirements, the report
should identify the government
requirement involved and the effect
these requirements had on the reported
emission reductions. If, as a result of the
reduction, a non-U.S. government
issued to the reporting entity a credit or
other financial benefit or regulatory
relief, the report should identify the
government requirement involved and
describe the specific form of benefit or
relief provided.
(k) Determining the entity responsible
for emission reductions. The entity that
EIA will presume to be responsible for
emission reduction, avoided emission or
sequestered carbon is the entity with
financial control of the facility, land or
vehicle which generated the reported
emissions, generated the energy that
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was sold so as to avoid other emissions,
or was the place where the sequestration
action occurred. If control is shared,
reporting of the associated emission
reductions should be determined by
agreement between the entities involved
so as to avoid double-counting; this
agreement must be reflected in the
entity statement and in any report of
emission reductions. EIA will presume
that an entity is not responsible for any
emission reductions associated with a
facility, property or vehicle excluded
from its entity statement.
§ 300.9 Reporting and recordkeeping
requirements.
(a) Starting to report under the
guidelines. An entity may report
emissions and sequestration on an
annual basis beginning in any year, but
no earlier than the base period of 1987–
1990 specified in the Energy Policy Act
of 1992. To be recognized under these
guidelines, all reports must conform to
the measurement methods established
by the Technical Guidelines
(incorporated by reference, see
§ 300.13).
(b) Revisions to reports submitted
under the guidelines. (1) Once EIA has
accepted a report under this part, it may
be revised by the reporting entity only
under the circumstances specified in
this paragraph and related provisions of
the Technical Guidelines (incorporated
by reference, see § 300.13). In general:
(i) Revised reports may be submitted
to correct errors that have a significant
effect on previously estimated emissions
or emission reductions; and
(ii) Emission inventories may be
revised in order to create a consistent
time series based on improvements in
the emission estimation or measurement
techniques used.
(2) Reporting entities must provide
the corrected or improved data to EIA,
together with an explanation of the
significance of the change and its
justification.
(3) If a change in calculation methods
(for inventories or reductions) is made
for a particular year, the reporting entity
must, if feasible, revise its base value to
assure methodological consistency with
the reporting year value.
(c) Definition and deadline for annual
reports. Entities must report emissions
on a calendar year basis, from January
1 to December 31. To be included in the
earliest possible EIA annual report of
greenhouse gas emissions reported
under this part, entity reports that have
not been independently verified must be
submitted to DOE no later than July 1
for emissions occurring during the
previous calendar year. Reports that
have been independently verified must
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be submitted by September 1 for
emissions occurring during the previous
year.
(d) Recordkeeping. Entities intending
to register reductions must maintain
adequate supporting records of base
period data for the duration of their
participation in the 1605(b) program.
Supporting records for all reporting year
data must be maintained for at least
three years subsequent to the relevant
reporting year to enable verification of
all information reported. The records
should document the basis for the
entity’s report to EIA, including:
(1) The content of entity statements,
including the identification of the
specific facilities, buildings, land
holding and other operations or
emission sources covered by the entity’s
reports and the legal, equity, operational
and other bases for their inclusion;
(2) Information on the identification
and assessment of changes in entity
boundaries, processes or products that
might have to be reported to EIA;
(3) Any agreements or relevant
communications with other entities or
third parties regarding the reporting of
emissions or emission reductions
associated with sources the ownership
or operational control of which is
shared;
(4) Information on the methods used
to measure or estimate emissions, and
the data collection and management
systems used to gather and prepare this
data for inclusion in reports;
(5) Information on the methods used
to calculate emission reductions,
including the basis for:
(i) The selection of the specific output
measures used, and the data collection
and management systems used to gather
and prepare output data for use in the
calculation of emission reductions;
(ii) The selection and modification of
all base years, base periods and
baselines used in the calculation of
emission reductions;
(iii) Any baseline adjustments made
to reflect acquisitions, divestitures or
other changes;
(iv) Any models or other estimation
methods used; and
(v) Any internal or independent
verification procedures undertaken.
(e) Confidentiality. DOE will protect
trade secret and commercial or financial
information that is privileged or
confidential as provided in 5 U.S.C.
552(b)(4). An entity must clearly
indicate in its 1605(b) report the
information for which it requests
confidentiality. DOE will handle
requests for confidentiality of
information submitted in 1605(b)
reports in accordance with the process
established in DOE’s Freedom of
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Information regulations at 10 CFR
§ 1004.11.
§ 300.10
Certification of reports.
(a) General requirement and certifying
official: All reports submitted to EIA
must include a certification statement,
as provided in paragraph (b) of this
section, signed by a certifying official of
the reporting entity. A household report
may be certified by one of its members.
All other reports must be certified by
the chief executive officer, agency head,
or an officer or employee of the entity
who is responsible for reporting the
entity’s compliance with environmental
regulations.
(b) Certification statement
requirements. All entities, whether
reporting or registering reductions, must
certify the following:
(1) The information reported is
accurate and complete;
(2) The information reported has been
compiled in accordance with this part;
and
(3) The information reported is
consistent with information submitted
in prior years, if any, or any
inconsistencies with prior year’s
information are documented and
explained in the entity statement.
(c) Additional requirements for
registering. The certification statement
of an entity registering reductions must
also certify that:
(1) The entity took reasonable steps to
ensure that direct emissions, emission
reductions, and/or sequestration
reported are neither double counted nor
reported by any other entity. Reasonable
steps include telephone, fax, letter, or
e-mail communications to ensure that
another entity does not intend to report
the same emissions, emission
reductions, and/or sequestration to
DOE. Direct communications of this
kind with participants in demand-side
management or other programs directed
at very small emitters are not required;
(2) Any emission reductions reported
or registered by the entity that were
achieved by another entity (other than a
very small emitter that participated in a
demand-side management or other
program) are included in the entity’s
report only if:
(i) The other entity does not intend to
report or register theses reductions
directly;
(ii) There exists a written agreement
with each other entity providing that the
reporting entity is the entity entitled to
report or register these emission
reductions; and
(iii) The information reported on the
other entity would meet the
requirements of this part if the entity
were reporting directly to DOE;
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(3) None of the emissions, emission
reductions, or sequestration reported
were produced by shifting emissions to
other entities or to non-reporting parts
of the entity;
(4) None of any reported changes in
avoided emissions associated with the
sale of electricity, steam, hot or chilled
water generated from non-emitting or
low-emitting sources are attributable to
the acquisition of a generating facility
that has been previously operated,
unless the entity’s base period includes
generation values from the acquiring
facility’s operation prior to its
acquisition;
(5) The entity maintains records
documenting the analysis and
calculations underpinning the data
reported on this form and records
documenting the analysis and
calculations underpinning the base
values used in calculating annual
reductions are maintained in
accordance with § 300.9(d) of this part;
and
(6) The entity has, or has not,
obtained independent verification of the
report, as described in § 300.11.
§ 300.11
Independent verification.
(a) General. Entities are encouraged to
have their annual reports reviewed by
independent and qualified auditors, as
described in paragraphs (b), (c), and (f)
of this section.
(b) Qualifications of verifiers. (1) DOE
envisions that independent verification
will be performed by professional
verifiers (i.e., individuals or companies
that provide verification or ‘‘attestation’’
services). EIA will consider a report to
the program to be independently
verified if:
(i) The lead individual verifier and
other members of the verification team
are accredited by one or more
independent and nationally-recognized
accreditation programs, described in
paragraph (c) of this section, for the
types of professionals needed to
determine compliance with DOE’s
1605(b) guidelines;
(ii) The lead verifier has experience
managing an auditing or verification
process, including the recruitment and
allocation of other individual verifiers,
and has been empowered to make
decisions relevant to the provision of a
verification statement; and
(iii) All members of a verification
team have education, training and/or
professional experience that matches
the tasks performed by the individual
verifiers, as deemed necessary by the
verifier accreditation program.
(2) As further guidance, all members
of the verification team should be
familiar with:
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(i) The subject matter covered by the
scope of the verification;
(ii) The requirements of this part;
(iii) Greenhouse gas emission and
emission reduction quantification;
(iv) Data and information auditing
sampling methods; and
(v) Risk assessment and
methodologies and materiality analysis
procedures outlined by other domestic
and international standards.
(3) An individual verifier should have
a professional degree or accreditation in
engineering (environmental, industrial,
chemical), accounting, economics, or a
related field, supplemented by specific
training and/or experience in emissions
reporting and accounting, and should
have his or her qualifications and
continuing education periodically
reviewed by an accreditation program.
The skills required for verification are
often cross-disciplinary. For example,
an individual verifier reviewing a coal
electric utility should be knowledgeable
about mass balance calculations, fuel
purchasing accounting, flows and stocks
of coals, coal-fired boiler operation, and
issues of entity definition.
(4) Companies that provide
verification services must use
professionals that possess the necessary
skills and proficiency levels for the
types of entities for which they provide
verification services. Continuing
training may be required to ensure all
individuals have up-to-date knowledge
regarding the tasks they perform.
(c) Qualifications of organizations
accrediting verifiers. Organizations that
accredit individual verifiers must be
nationally recognized certification
programs. They may include, but are not
limited to the: American Institute of
Certified Public Accountants; American
National Standards Institute’s Registrar
Accreditation Board program for
Environmental Management System
auditors (ANSI–RAB–EMS); Board of
Environmental, Health and Safety
Auditor Certification: California Climate
Action Registry; Clean Development
Mechanism Executive Board; and the
United Kingdom Accreditation Scheme.
(d) Scope of verification. (1) As part
of any independent verification,
qualified verifiers must use their
expertise and professional judgment to
verify for accuracy, completeness and
consistency with DOE’s guidelines of:
(i) The content of entity statements,
annual reports and the supporting
records maintained by the entity;
(ii) The representation in entity
statements (or lack thereof) of any
significant changes in entity boundaries,
products, or processes;
(iii) The procedures and methods
used to collect emissions and output
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data, and calculate emission reductions
(for entities with widely dispersed
operations, this process should include
on-site reviews of a sample of the
facilities);
(iv) Relevant personnel training and
management systems; and
(v) Relevant quality assurance/quality
control procedures.
(2) DOE expects qualified verifiers to
refer to the growing body of literature on
methods of evaluating the elements
listed in paragraph (d)(1) of this section,
such as the California Climate Action
Registry Certification Protocol, the
Climate Leaders Inventory Management
Plan Checklist, and the draft ISO
14064.3 Protocol for Validation,
Verification and Certification.
(e) Verification statement. Both the
verifier and, if relevant, an officer of the
company providing the verification
service must sign the verification
statement. The verification statement
shall attest to the following:
(1) The verifier has examined all
components listed in paragraph (d) of
this section;
(2) The information reported in the
verified entity report and this
verification statement is accurate and
complete;
(3) The information reported by the
entity has been compiled in accordance
with this part;
(4) The information reported on the
entity report is consistent with
information submitted in prior years, if
any, or any inconsistencies with prior
year’s information are documented and
explained in the entity statement;
(5) The verifier used due diligence to
assure that direct emissions, emission
reductions, and/or sequestration
reported are not reported by any other
entity;
(6) Any emissions, emission
reductions, or sequestration that were
achieved by a third-party entity are
included in this report only if there
exists a written agreement with each
third party indicating that they have
agreed that the reporting entity should
be recognized as the entity entitled to
report these emissions, emission
reductions, or sequestration;
(7) None of the emissions, emission
reductions, or sequestration reported
was produced by shifting emissions to
other entities or to non-reporting parts
of the entity;
(8) No reported changes in avoided
emissions associated with the sale of
electricity, steam, hot or chilled water
generated from non-emitting or lowemitting sources are attributable to the
acquisition of a generating facility that
has been previously operated, unless the
base year generation values are derived
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from records of the facility’s operation
prior to its acquisition;
(9) The verifying entity has
procedures in place for the maintenance
of records that are sufficient to
document the analysis and calculations
underpinning this verification. The
verifying entity shall maintain such
records related to base period data
submitted by the reporting entity for the
duration of the reporting entity’s
participation in the 1605(b) program
and records related to all other verified
data for a period of no less than three
years; and
(10) The independent verifier is not
owned in whole or part by the reporting
entity, nor provides any ongoing
operational or support services to the
entity, except services consistent with
independent financial accounting or
independent certification of compliance
with government or private standards.
(f) Qualifying as an independent
verifier. An independent verifier may
not be owned in whole or part by the
reporting entity, nor may it provide any
ongoing operational or support services
to the entity, except services consistent
with independent financial accounting
or independent certification of
compliance with government or private
standards.
§ 300.12 Acceptance of reports and
registration of entity emission reductions.
(a) Acceptance of reports. EIA will
review all reports to ensure they are
consistent with this part and with the
Technical Guidelines (incorporated by
reference, see § 300.13). EIA will also
review all reports for completeness,
internal consistency, arithmetic
accuracy and plausibility. Subject to the
availability of adequate resources, EIA
intends to notify entities of the
acceptance or rejection of any report
within six months of its receipt.
(b) Registration of emission
reductions. EIA will review each
accepted report to determine if emission
reductions were calculated using an
acceptable base period (usually ending
no earlier than 2002), and to confirm
that the report complies with the other
provisions of this part. EIA will also
review its records to verify that the
reporting entity has submitted accepted
annual reports for each year between the
establishment of its base period and the
year covered by the current report. EIA
will notify the entity that reductions
meeting these requirements have been
credited to the entity as ‘‘registered
reductions’’ which can be held by the
reporting entity for use (including
transfer to other entities) in the event a
future program that recognizes such
reductions is enacted into law.
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(c) Rejection of reports. If EIA does
not accept a report or if it determines
that emission reductions intended for
registration do not qualify, EIA will
return the report to the sender with an
explanation of its inadequacies. The
reporting entity may resubmit a
modified report for further
consideration at any time.
(d) EIA database and summary
reports. The Administrator of EIA will
establish a publicly accessible database
composed of all reports that meet the
definitional, measurement, calculation,
and certification requirements of these
guidelines. EIA will maintain separate
subtotals of direct emissions, indirect
emissions and carbon fluxes. A portion
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of the database will provide summary
information on the emissions and
registered emission reductions of each
reporting entity.
§ 300.13
Incorporation by reference.
The Technical Guidelines for the
Voluntary Reporting of Greenhouse
Gases Program (March 2006), referred to
throughout this part as the ‘‘Technical
Guidelines,’’ have been approved for
incorporation by reference by the
Director of the Federal Register in
accordance with 5 U.S.C. 552(a) and 1
CFR part 51. You may obtain a copy of
the Technical Guidelines from the
Office of Policy and International
Affairs, U.S. Department of Energy, 1000
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20817
Independence Ave., SW., Washington,
DC 20585, or by visiting the following
Web site: https://www.policy.energy.gov/
enhancingGHGregistry/
technicalguidelines/. The Technical
Guidelines also are available for
inspection at the National Archives and
Record Administration (NARA). For
more information on the availability of
this material at NARA, call 202–741–
6030, or go to: https://www.archives.gov/
federal_register/
code_of_federal_regulations/
ibr_locations.html.
[FR Doc. 06–3745 Filed 4–20–06; 8:45 am]
BILLING CODE 6450–01–P
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Agencies
[Federal Register Volume 71, Number 77 (Friday, April 21, 2006)]
[Rules and Regulations]
[Pages 20784-20817]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-3745]
[[Page 20783]]
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Part III
Department of Energy
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10 CFR Part 300
Guidelines for Voluntary Greenhouse Gas Reporting; Final Rule
Federal Register / Vol. 71, No. 77 / Friday, April 21, 2006 / Rules
and Regulations
[[Page 20784]]
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DEPARTMENT OF ENERGY
10 CFR Part 300
RIN 1901-AB11
Guidelines for Voluntary Greenhouse Gas Reporting
AGENCY: Office of Policy and International Affairs, U.S. Department of
Energy.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: Section 1605(b) of the Energy Policy Act of 1992 directed the
Department of Energy (DOE) to issue guidelines establishing a voluntary
greenhouse gas reporting program. On February 14, 2002, the President
directed DOE, together with other involved Federal agencies, to
recommend reforms to enhance the Voluntary Reporting of Greenhouse
Gases Program established by DOE in 1994. DOE issued interim final
General Guidelines on March 24, 2005, and also on that date published a
notice of availability inviting public comment on draft Technical
Guidelines needed to fully implement the revised Voluntary Reporting of
Greenhouse Gases Program. This notice of final rulemaking responds to
public comments on the interim final General Guidelines and draft
Technical Guidelines; sets forth the final General Guidelines; and
announces the availability of the final Technical Guidelines.
DATES: Effective Date: The final General Guidelines and Technical
Guidelines are effective June 1, 2006. The incorporation by reference
of the Technical Guidelines is approved by the Director of the Federal
Register as of June 1, 2006.
FOR FURTHER INFORMATION CONTACT: Mark Friedrichs, PI-40, Office of
Policy and International Affairs, U.S. Department of Energy, 1000
Independence Ave., SW., Washington, DC 20585, or e-mail:
1605bguidelines.comments@hq.doe.gov
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
A. Background
B. Process for Implementing the Guidelines
II. Overview of Major Changes Made in Response to Comments
III. Discussion of Public Comments and the Final Revised Guidelines
A. Implementation Schedule
B. Process for Updating or Amending the Guidelines
C. Distinction Between Reporting Under the Program and
Registering Reductions
1. Reporting Under the Program
2. Registration Requirements
D. Entity Definitions, Boundaries and Statements
1. Entity Definition
2. Entity Boundaries--General
3. Entity Boundaries--U.S. and Non-U.S. Emissions
4. Entity Statements
E. Large v. Small Emitters
F. Aggregators
G. Other Definitions
H. Start Year and First Reduction Year
I. Electricity Dactors and Benchmarks
J. Inventories
1. Requirement for Entity-Wide Inventories With a Quality Rating
of at Least 3.0
2. De minimis Exclusion From Entity-Wide Emission Inventories
3. Ratings for Estimation Methods Using Default Values
4. References to Continuous Emissions Monitoring Systems (CEMS)
5. Citations of Protocols and Emission Factors Developed by
Other Organizations
6. Options for Simplifying Emission Reports
7. Eliminate Requirements To Report Emissions From Biogenic
Sources and To Report Certain Non-Fuel Uses of Fossil Fuels
8. Treatment of Agriculture and Forestry
9. Stationary Source Combustion
10. Mobile Sources
11. Industrial Processes
12. Indirect Emissions
13. Geologic Sequestration
K. Reductions
1. Selecting Appropriate Reduction Calculation Methods
2. Base Periods and Base Values
3. Enabling Reporters To Choose More Stringent Base Values
4. Emissions Intensity
5. Absolute Emissions
6. Changes in Carbon Stocks
7. Avoided Emissions
8. Action-Specific Methods
9. Estimating Reductions From Energy Generation and Distribution
L. Offset Reductions
M. Certification and Verification
1. Certification
2. Independent Verification
N. Reporting and Recordkeeping
O. Report Review and Acceptance Process
P. Publication of General Guidelines in the Code of Federal
Regulations
IV. Regulatory Review and Procedural Requirements
A. Review Under Executive Order 12866
B. Review Under the Regulatory Flexibility Act
C. Review Under the Paperwork Reduction Act
D. Review Under the National Environmental Policy Act
E. Review Under Executive Order 13132
F. Review Under the Treasury and General Government
Appropriations Act, 2001
G. Review Under Executive Order 12988
H. Review Under the Unfunded Mandates Reform Act of 1995
I. Review Under the Treasury and General Government
Appropriations Act, 1999
J. Review Under Executive Order 13211
K. Congressional Review
I. Introduction
A. Background
Section 1605(b) of the Energy Policy Act of 1992 (EPACT) directs
the Department of Energy, with the Energy Information Administration
(EIA), to establish a voluntary reporting program and database on
emissions of greenhouse gases, reductions of these gases, and carbon
sequestration activities (42 U.S.C. 13385(b)). Section 1605(b) requires
that DOE's guidelines provide for the ``accurate'' and ``voluntary''
reporting of information on: (1) Greenhouse gas emission levels for a
baseline period (1987-1990) and thereafter, annually; (2) greenhouse
gas emission reductions and carbon sequestration, regardless of the
specific method used to achieve them; (3) greenhouse gas emission
reductions achieved because of voluntary efforts, plant closings, or
state or federal requirements; and (4) the aggregate calculation of
greenhouse gas emissions by each reporting entity (42 U.S.C.
13385(b)(1)(A)-(D)). Section 1605(b) contemplates a program whereby
voluntary efforts to reduce greenhouse gas emissions can be recorded,
with the specific purpose that this record can be used ``by the
reporting entity to demonstrate achieved reductions of greenhouse
gases'' (42 U.S.C. 13385(b)(4)).
In 1994, after notice and public comment, DOE issued General
Guidelines and sector-specific guidelines that established the
Voluntary Reporting of Greenhouse Gases Program for recording
voluntarily submitted data and information on greenhouse gas emissions
and the results of actions to reduce, avoid or sequester greenhouse gas
emissions. The 1994 General Guidelines and supporting documents may be
accessed at https://www.eia.doe.gov/oiaf/1605/guidelns.html. The
Guidelines were intentionally flexible to encourage the broadest
possible participation. They permit participants to decide which
greenhouse gases to report, and allow for a range of reporting options,
including reporting of total emissions or emissions reductions or
reporting of just a single activity undertaken to reduce part of their
emissions. From its establishment in 1995 through the 2004 reporting
year, 417 entities, including utilities, manufacturers, coal mine
operators, landfill operators and others, have reported their
greenhouse gas emissions and/or their emission reductions to EIA.
On February 14, 2002, the President directed the Secretary of
Energy, in consultation with the Secretary of
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Commerce, the Secretary of Agriculture, and the Administrator of the
Environmental Protection Agency, to propose improvements to the current
section 1605(b) Voluntary Reporting of Greenhouse Gases Program. These
improvements are to enhance measurement accuracy, reliability, and
verifiability, working with and taking into account emerging domestic
and international approaches.
On May 6, 2002, DOE published a Notice of Inquiry soliciting public
comments on how best to improve the Voluntary Reporting of Greenhouse
Gases Program (67 FR 30370). Written comments were received from
electric utilities; representatives of energy, manufacturing and
agricultural sectors; Federal and State legislators; State agencies;
waste management companies; and environmental and other non-profit
research and advocacy organizations. DOE held public workshops in
Washington, DC, Chicago, San Francisco and Houston during November and
December of 2002 to receive information and hear the views of
interested persons. In addition, the U.S. Department of Agriculture
sponsored two workshops in January 2003 to solicit input on the
accounting rules and guidelines for reporting greenhouse gas emissions
in the forestry and agriculture sectors. These workshops explored in
greater depth many of the issues raised in the Notice of Inquiry and
addressed in the written comments.
On December 5, 2003, DOE proposed revised General Guidelines (68 FR
68204). A public workshop was held on January 12, 2004, to discuss that
proposal and to receive public comment. Approximately 200 persons
attended the workshop. In addition, over 300 written comments were
received by the close of the public comment period on February 17,
2004.
DOE published interim final revised General Guidelines on March 24,
2005 (70 FR 15169), and, in a notice published in the Federal Register
on the same day, made available for public comment the draft Technical
Guidelines necessary to fully implement the revisions to the Voluntary
Program (70 FR 15164). DOE sponsored a public workshop on these revised
guidelines on April 26 and 27, 2005, and USDA and DOE co-sponsored
another workshop on May 5, 2005. In response to public comments, DOE
extended the period for comments on the revised guidelines by 30 days
to June 22, 2005. Ultimately, DOE received over 90 written comments,
totaling over 1000 pages. All written comments and transcripts of the
public workshops are available on the Web and can be accessed at:
https://www.pi.energy.gov/enhancingGHGregistry/. On September 19, 2005,
DOE published a notice in the Federal Register delaying the effective
date of the interim final guidelines until June 1, 2006 (70 FR 54835).
DOE now publishes final General Guidelines and announces the
availability of final Technical Guidelines that are incorporated by
reference in the General Guidelines. The revised General and Technical
Guidelines are designed to enhance the measurement accuracy,
reliability and verifiability of information reported under the 1605(b)
program and to contribute to the President's climate change goals. The
key elements of the revised guidelines remain the same as those present
in the interim final General Guidelines:
Enable larger emitters to register reductions if they
provide entity-wide emissions data and can demonstrate they achieved
entity-wide emission reductions that contribute to the President's goal
of reducing the greenhouse gas emissions of the U.S. economy.
Provide for simplified procedures for small emitters to
report and to register reductions.
Provide for simplified reports from entities that do not
want to register their reductions.
Encourage companies and other reporting entities to report
at the highest level.
Require participants to ensure the accuracy and
completeness of their reports, and encourage independent verification.
Allow participants to report and register reductions
achieved internationally.
Based on the framework set forth by the interim final guidelines
and the various improvements made in response to the public comments
received, today's final revised guidelines will enhance:
Measurement accuracy by creating a ranking system for
methods to calculate emissions, incorporating the best available
inventory methods, and enabling more sources to be covered;
Reliability by creating a more systematic approach to
reporting, stressing inventories and entity-wide reporting; and
Verifiability by creating a more transparent reporting
system for emissions and reductions, requiring recordkeeping and
encouraging independent verification.
The Secretary of Energy has approved issuance of this final rule.
B. Process for Implementing the Guidelines
The General Guidelines set forth in this notice and the Technical
Guidelines incorporated by reference will go into effect on June 1,
2006. In the near future, EIA intends to make available for public
review and comment draft forms for collecting the data covered by these
guidelines, including the Simplified Emissions Inventory Tool (SEIT)
referenced in the guidelines. After taking into account any public
comments it receives and complying with the requirements of the
Paperwork Reduction Act of 1995, EIA anticipates that final forms will
be issued before the end of 2006. In addition, EIA will be developing
the software necessary to permit electronic reporting and the creation
of an automated and widely accessible data base. EIA does not
anticipate completing the necessary software until mid-2007. If time
and resources permit, EIA may conduct cognitive testing of beta
versions of the reporting software. Should EIA conduct such testing,
EIA will solicit potential participants via a public notice, postings
to its website, or some other means. According to the forms and
software schedule currently anticipated by EIA, the revised guidelines
will be used to govern the 2007 reporting cycle. Until then, entities
interested in reporting under the program during the 2006 reporting
cycle should use the existing guidelines and forms.
II. Overview of Major Changes Made in Response to Comments
The public comments received by DOE expressed considerable support
for the emphasis of the revised guidelines on entity-wide reporting on
all greenhouse gas emissions, including the added requirements imposed
on entities that are seeking to register reductions. There was also
substantial support for DOE's efforts to enhance the quality,
consistency and credibility of the emission inventories and reductions
being reported. The comments, however, raised a number of concerns
regarding the potential burdens of reporting under the revised
guidelines, possible incompatibilities with various existing reporting
programs or protocols, and the limitations on reporting certain types
of emission reductions, especially those occurring outside the
boundaries of the reporting entity. While the basic framework of the
guidelines remains the same, DOE has made a number of changes designed
to address these concerns, and has adopted many of the specific
recommendations made during the comment period.
[[Page 20786]]
To reduce the potential burdens of reporting under the revised
guidelines, DOE's final guidelines:
Enable entities that have their reports independently
verified or that certify their use of higher quality inventory methods
to file less detailed reports;
Increase the ratings of some commonly used methods for
estimating emissions;
Enable reports on non-U.S. emissions to be consolidated
regionally or globally (as long as U.S. data is kept separate); and
Clarify the flexibility available to reporters that wish
to avoid or minimize the complexities of accounting for changes in
carbon stock or other provisions.
To increase the compatibility of the revised guidelines with
various existing reporting programs and protocols, DOE's final
guidelines update its references to existing protocols and update the
emission factors drawn from such protocols; provide an exception in
section 300.5(b) for participants in EPA's Climate Leaders or DOE's
Climate VISION who may wish to use base periods that end as early as
2000; and attempt to increase the alignment of various definitions and
methods with those used by other existing programs.
To expand the opportunities for reporting offset emission
reductions, DOE's final guidelines, among other things: (1) Add new
action-specific methods for demand-side management programs, the
substitution of fly ash for cement by concrete mixers, and anaerobic
digestion of waste at agricultural facilities and wastewater treatment
plants; (2) enable multiple reporting entities to register portions of
the offset reductions achieved by a single other entity, as long as the
other entity complies with all of the requirements for registration and
has entered into an agreement with each of the reporting entities; and
(3) permit the accelerated reporting of carbon stock increases expected
to occur on land that is being reforested, restored and permanently
protected.
DOE has not adopted the recommendation of commenters who advocated
that DOE mandate participation in the 1605(b) program because such a
mandate is beyond the statutory authority of DOE.
III. Discussion of Public Comments and the Final Revised Guidelines
This section of the Supplementary Information discusses the issues
raised by the public comments on the interim final General Guidelines
and the draft Technical Guidelines and any changes to the guidelines
that DOE has made in response to the comments.
A. Implementation Schedule
A few comments suggested that DOE consider a delay in the start of
the revised program or a phased implementation of the new requirements.
DOE does not consider either a delayed or phased implementation of the
revised guidelines to be necessary or practical. Starting the program
in calendar year 2007 should give most reporters sufficient time to
prepare to meet the requirements of the new program. If individual
reporters require additional time, they may delay their own
participation. Entities that are unable to meet all of the requirements
for registration may simply choose to meet only the requirements for
reporting under the program until such time as they are prepared to
meet all of the requirements for registration. Another available option
would be to take more time to complete the entity's first or second
annual reports. For example, an entity could decide to submit its
report on 2006 emissions during 2008, rather than by the 2007 deadline
for reports that are to be included in EIA's first public report on
2006 emissions (likely to be issued in late 2007 or early 2008).
Entities may submit reports on prior year emissions and emission
reductions at any time.
B. Process for Updating or Amending the Guidelines
DOE intends to review and, if necessary, update the guidelines
approximately every three years, although exceptional circumstances may
require amendment of the guidelines at other times. Modifications to
either the General Guidelines or the Technical Guidelines will be
subject to public notice and comment. Some commenters noted that this
public process might be too cumbersome and time consuming for the
adoption of routine updates to the many emission factors and protocols
cited by the guidelines. To address this concern, DOE has modified some
provisions of the Technical Guidelines to direct reporters to use the
most current version of certain government-sponsored or consensus-based
factors, methods and protocols.
C. Distinction Between Reporting Under the Program and Registering
Reductions
The revised guidelines set forth the requirements for all reporters
under the 1605(b) program as well as requirements that must be met by
only those reporters that are seeking to register emission reductions
(see section 300.1(b) and (c) of this rule for a description of the
requirements for reporting and registering emissions and reductions).
More specifically, while some new requirements are imposed on all
reporters by the revised guidelines, the requirements for entity-wide
reports and use of high quality emission inventory and reduction
methods are imposed only on those entities that are seeking to register
reductions. The distinct requirements for reporting under the program
and for registering reductions are key to achieving DOE's objective of
enhancing the overall quality and credibility of the reductions
documented by the program, while at the same time preserving most of
the flexibility available to reporters under the original program
guidelines.
Some commenters recommended that the distinction between reporting
under the program and registering emission reductions be eliminated,
which would enable all reporters to receive the same level of
recognition, regardless of whether or not they met the entity-wide
reporting requirements. DOE believes that the elimination of this
distinction would significantly diminish the incentive for large
emitters to improve the overall quality of their reports by undertaking
the more costly activities associated with emission inventories and
entity-wide assessments of reductions, which are required for
registration.
In addition to objecting on policy grounds to the distinction
between reported registered reductions and other reported reductions,
one commenter argued that in the absence of express authorization,
there is no legal basis in section 1605(b) for changing from a unitary
system of reporting to a two-tier system that distinguishes between two
types of reported emissions and reductions. Other commenters contended
that because section 1605(b) expressly includes reductions from plant
closings among the information that entities may report under the
program, DOE may not exclude such reductions from the reductions that
can be registered under the revised guidelines.
DOE rejects the comments arguing that DOE may not distinguish among
different types of reported emissions and reductions within EIA's
database because there is no express authority for such differentiation
in section 1605(b). Section 1605(b) broadly charges DOE with issuing
guidelines, after opportunity for public comment, for the ``voluntary
collection and reporting of information on sources of greenhouse
[[Page 20787]]
gases.'' 42 U.S.C. 13385(b)(1). Further, the guidelines must include:
Procedures for the accurate voluntary reporting of information on--
(A) greenhouse gas emissions [starting with a statutorily-prescribed
baseline period and annually thereafter]; (B) annual reductions of
greenhouse gas emissions and carbon fixation achieved through any
measures, including [a list of such measures]; (C) reductions in
greenhouse gas emissions achieved as a result of--(i) voluntary
reductions; (ii) plant or facility closings; and (iii) State or
Federal requirements; and (D) an aggregate calculation of greenhouse
gas emissions by each reporting entity.
42 U.S.C. 133385(b)(1)(A)-(D) (emphasis added).
Nothing in the statute limits the information on sources of
greenhouse gases reported under the program to that described in
section 1605(b)(1)(A)-(D). Rather, the information described in (A)
through (D) is the minimum information that may be reported under DOE's
procedures. While the text of section 1605(b) does not specifically
address the question of whether DOE may create categories of reported
greenhouse gas information within the EIA database, DOE's procedures
must provide for the accurate voluntary reporting of information. One
of the goals of registration under the final revised guidelines is to
enhance the accuracy and reliability of greenhouse gas emissions and
reductions information. Thus, the text of section 1605(b), read in its
entirety, supports DOE's view that establishment of a category of
registered emissions for emissions and reductions that meet certain
requirements for entity-wide reporting is implicitly authorized by the
statute.
DOE also rejects the comment that because section 1605(b) expressly
includes reductions from plant and facility closings among the
information that entities may report under DOE's procedures, DOE may
only establish categories of reported information that include
reductions from plant and facility closings. DOE's textual analysis
stated above in rejecting the argument that DOE may not establish a
two-tiered reporting system applies here as well. Nothing in the
statute limits DOE's authority to go beyond the minimum information
categories in section 1605(b)(1)(A)-(D), and the requirement that DOE's
procedures provide for the accurate voluntary reporting of information
is implicit authorization for DOE to establish a system of registration
that enhances the accuracy and reliability of information reported on
an entity-wide basis.
Several commenters suggested that the revised program guidelines
should include a summary of the guidelines' requirements for reporting
and for registering emissions and reductions. In response, DOE is
providing a summary of the requirements in section 300.1 of today's
General Guidelines. The requirements for reporting and registering
emissions and reductions are described in the following sections of
this Supplementary Information.
1. Reporting Under the Program
Each reporter under the program must be an ``entity,'' as defined
in the guidelines and must file an entity statement. Reporters not
intending to register emission reductions must, at minimum, meet the
entity statement, record keeping, and certification requirements set
forth in sections 300.5(f), 300.9, and 300.10, respectively. They may
choose to report their emissions and/or their emission reductions on an
entity-wide basis or for selected elements of their entities, selected
gases or selected sources. Emission inventories for any year back to
1990 may be reported, and emission reductions may be reported for any
year back to 1991, relative to base periods of one to four years,
ending no earlier than 1990. All reporting entities, whether or not
they intend to register reductions, must use the emission inventory and
emission reduction calculation methods specified in the Technical
Guidelines. For example, as discussed in section III.K.8. of this
Supplementary Information, the guidelines now provide for the reporting
of the emissions and reductions associated with chlorofluorocarbons
(CFCs), although such reductions are not eligible for registration. In
the future, DOE may revise the guidelines to add methods that permit
the reporting and, in some cases, the registration of reductions
associated with other gases. While entities that do not intend to
register reductions need not ensure that their emission inventories
achieve a weighted average quality rating of 3.0 or higher (a
requirement that is discussed in section III.J.1 below), they must
calculate and report the weighted average quality rating of any
emission inventories they do report. In most situations, entities not
registering reductions may choose an emissions intensity, absolute
emissions or generic action-specific method to calculate the emission
reductions they report. However, in those situations where a special
calculation method is provided, such as sequestration, the sale of
distributed energy, or an action-specific method, the entity must use
the appropriate method provided in the Technical Guidelines. Entities
not intending to register reductions may also report (but not register)
offset reductions achieved by third parties outside their boundaries as
long as such reductions are reported separately and calculated in
accordance with methods specified in the guidelines. The third party
that achieved these reductions must agree to their being reported as
offset reductions, and must also meet all of the other minimum
requirements of reporting under the program, including the provision of
an entity statement, the maintenance of records, and necessary
certifications as stipulated in Sec. Sec. 300.9 and 300.10.
2. Registration Requirements
Entities that intend to register reductions must meet a number of
additional requirements, although these requirements differ depending
on whether the entity is a large or small emitter.
To be eligible for registration, a reduction must have been
calculated using a base period ending no later than 2002, unless the
entity has committed under the Climate Leaders or Climate VISION
programs to reduce its entity-wide emissions relative to a base period
that ends earlier than 2002, but no earlier than 2000.
In order to register reductions, large emitters must submit entity-
wide emission inventories that meet or exceed the minimum quality
requirements specified in Sec. 300.6(b) and the Technical Guidelines.
Any registered reductions must be based on entity-wide assessments of
annual changes in net emissions, determined in accordance with
Sec. Sec. 300.7 and 300.8 and the Technical Guidelines. They must also
meet the entity statement and certification requirements specified in
Sec. Sec. 300.5 and 300.10.
Small emitters must also submit emission inventories that meet
minimum quality requirements and base their registered reductions on
assessments of annual changes in net emissions, but small emitters may
restrict these inventories and assessments to a single type of
activity, such as forest management, building operations or
agricultural tillage, rather than covering all of their entity's
emissions. Small emitters must also submit entity statements, certify
the accuracy of their reports and meet other requirements of reporting
and registering.
Both large emitters and small emitters that have met the
requirements for registering their own reductions may also register
offset reductions achieved by other entities, as long as they have an
agreement with the third party to do
[[Page 20788]]
so and these third parties have met all of the requirements for
registration. Small emitters that serve as aggregators may register
offset reductions without reporting on their own emissions. Entities
that report offset reductions achieved by very small emitters (those
typically emitting less than 500 metric tons of CO2
equivalent emissions per year) as a result of demand management or
other programs that reduce greenhouse gas emissions, may register such
reductions as long as they are calculated in accordance with the
action-specific method identified in section 300.8(h)(5).
D. Entity Definitions, Boundaries and Statements
Most of the comments on these provisions of the interim final
guidelines were generally supportive, although a few significant
concerns were raised and a number of specific changes were recommended.
1. Entity Definition
Several commenters urged DOE to require entities to report at their
highest level of aggregation within the United States, while other
commenters urged DOE to provide entities even more flexibility in how
they define themselves for the purpose of reporting under the program.
The final guidelines retain the basic approach put forward in the
interim final General Guidelines: entities must have a legal basis and
are encouraged--but not required--to report at their highest level of
aggregation within the United States. If an entity chooses to report at
a lower level of aggregation, the reporting entity must have a legal
basis and must be defined in a way that is consistent with the
management structure of the parent company or organization.
Section 300.2 of the interim final rule defines ``entity or
reporting entity'' as the whole or part of any business, institution,
organization or household that is recognized as an entity under any
U.S. Federal, State or local law that applies to it; is located, at
least in part, in the United States; and whose operations affect U.S.
emissions of greenhouse gases. Some commenters argued that the
``legally distinct entity'' test is too inflexible and urged DOE to
abandon the test. One stated that electricity providers may have
different reporting options due to differences in State regulation or
the absence of such regulation. The commenter recommended revising the
definition to allow an entity to consist of a set of corporate business
and other organizational units that comprise a single business
activity, even though they may not be legally distinct. Another
commenter stated that the definition of ``entity'' would pose a problem
for global corporations that are legally structured by product line,
rather than by country. A large industry association did not criticize
the substance of DOE's definition of ``entity or reporting entity,''
but rather offered drafting guidance that it considered would better
accomplish DOE's intent. It also suggested a separate definition of
``reporting entity.''
After considering the comments, DOE has retained the requirement
that an entity that reports under the 1605(b) program must be
recognized as an entity under a U.S. Federal, State or local law. In
light of changes to the provisions for reporting non-U.S. emissions
(discussed elsewhere in this Supplementary Information), DOE does not
believe the definition of ``entity'' in the final guidelines will pose
a problem for global corporations. While not necessarily agreeing with
many of the criticisms of the interim final guideline definition of
``entity or reporting entity,'' DOE found the suggested drafting
improvements to be helpful and has included several of them in revised
definitions for the terms ``entity'' and ``reporting entity.'' These
changes include increased emphasis on the coverage of government
bodies, agencies or other institutions, which DOE always intended to be
encompassed by the broad definition of entity included in the
guidelines.
2. Entity Boundaries--General
The organizational boundaries of reporting entities largely
determine which emissions and sources are covered by the entity's
reports. DOE's interim final General Guidelines encourage entities to
use financial control as the primary basis for determining the
organizational boundaries of the reporting entity. While the interim
guidelines encourage the use of financial control as the basis for
setting organizational boundaries, they permit entities to use other
methods, such as equity share or operational control, as long as they
are explained.
Boundary definitions are important because they determine what
emission and emission reductions a particular reporting entity may
assume responsibility for when reporting under the program. As a
voluntary reporting program, however, 1605(b) boundaries do not
determine the legal rights of reporting entities to emissions or
emission reductions. They are used only as the basis for DOE
recognition of any registered reductions reported under the program.
The comments received by DOE on these provisions of the guidelines were
generally supportive of DOE's approach, although some encouraged even
more flexibility. No changes have been made to the provisions included
in the interim final guidelines.
Financial control encompasses all buildings, facilities, lands,
vehicles and equipment that are wholly owned by the entity or in which
the entity has a controlling financial interest. Conversely, it usually
does not include buildings, facilities, lands, vehicles and equipment
that are wholly owned by a different entity or in which another entity
has a controlling financial interest. However, financial control would
exist if an entity has a long-term lease or other long-term agreement
that gives it effective control over capital investment and operational
decisions.
An alternative method for determining entity boundaries is equity
share, where more than one entity has a financial interest in a
particular facility or emission source, and each of the entities takes
responsibility for reporting only a portion of the facilities emissions
and reductions. Operational control, where an entity controls the day-
to-day operations of facility or source, but does not exercise long
term financial control might also be an option under certain
circumstances. If either equity share or operational control is chosen
as the method for determining boundaries, the reporting entity must
inform the other entities that share responsibility for particular
sources of its intention to report under the 1605(b) in order to ensure
that the sources emissions or reductions are not double-counted under
the program. Finally, the General Guidelines have been modified to
provide further guidance regarding the coverage of partially-owned or
leased sources, and sources that are neither owned nor leased by the
reporting entity.
3. Entity Boundaries--U.S. and Non-U.S. Emissions
The interim final guidelines permit entities to define their entity
so as to include operations, and their associated emissions, located
outside of the United States. They also permit certain non-U.S.
entities to be the source of offset emission reductions, as long as
they meet all of the requirements of the revised guidelines. The
interim final General Guidelines would allow entities to both report
and register emissions and emission reductions occurring outside of the
United States, subject to certain requirements. One of these
requirements is that non-U.S. emissions
[[Page 20789]]
and reductions must be reported separately from U.S. emissions and
reductions. DOE has clarified the guidelines to indicate that this does
not mean that the U.S. and non-U.S. emissions and reductions must be
submitted in separate reports. Under the final guidelines, non-U.S.
emissions and reductions must be included in one or more distinct
subentities identified in the entity's report to EIA and must be
separately sub-totaled before being considered as part of the entity's
net emission reductions qualifying for registration. Unless
specifically identified by the report, EIA will presume that all non-
U.S. reductions are governed, at least in part, by national or
international greenhouse gas regulations, and that such reductions
might be eligible for transfer or trading to other entities. However,
reporters will not be able to register emission reductions that do not
meet the requirements of these guidelines, whether or not they are
eligible for transfer or trading under a foreign national or multi-
national scheme.
In allowing entities to both report and register emissions and
emission reductions occurring outside of the United States, the interim
final General Guidelines require that emissions and reductions for each
country be segregated in the report submitted to EIA. One stakeholder,
a large multinational corporation, argued that this would place an
undue burden on companies having operations in numerous countries,
particularly where business units that provide an appropriate level of
aggregation (i.e., as separate subentities) cross national borders. In
the final guidelines, DOE encourages entities that wish to report or
register non-U.S. activities to segregate emissions and reductions from
each country in a separate subentity. However, reporters are permitted
to aggregate non-U.S. emissions and reductions at regional and even
non-U.S. global levels, as long as they identify each of the countries
covered and the country-specific factors used to generate their
reports.
4. Entity Statements
DOE's interim final guidelines include a number of specific
requirements for the contents of the entity statements to be submitted
by all reporters, although the specific requirements vary somewhat
depending on whether the reporter is a large or small emitter
interested in registering reductions, or a reporter that is not
intending to register reductions. Very few comments were received on
the requirements and no significant changes have been made to the
provisions concerning the entity statement.
E. Large v. Small Emitters
Under the interim final guidelines, ``small emitters'' are a
special category of reporters that are exempted from certain
requirements for the registration of reductions, including entity-wide
emission inventories and entity-wide assessments of reductions. DOE
received a substantial number of comments on these provisions. Several
of these comments were critical of the exemptions and argued that small
emitters deserve no special treatment. These were countered by a number
of other comments that argued that the burdens on small emitters under
the interim final guidelines are too onerous, and the exemptions should
be expanded. After considering these comments, DOE believes that the
provisions in the interim final guidelines strike the proper balance
between relieving the burden on small emitters and requiring the
submission of emissions information for registration. Consequently, DOE
has not significantly altered these provisions of the guidelines. It
should be noted that small emitters seeking to register reductions are
only required to report on the emissions and reductions associated with
a single, chosen ``activity,'' rather than all of the entity's
activities. Finally, the guidelines continue to permit entities to use
a Simplified Emissions Inventory Tool (SEIT), to be provided by the
Energy Information Administration, to estimate their emissions for
purposes of determining whether the entity is a small or large emitter,
and for estimating the quantity of emissions excluded as de minimis.
The guidelines now clearly state that the SEIT may not be used for the
preparation of emission inventories.
F. Aggregators
In the interim final guidelines, DOE provides some special guidance
for entities that register reductions on behalf of other entities, so-
called ``aggregators.'' Large emitters that serve as aggregators must
meet all of the requirements for registration, including submission of
entity-wide emission inventories and entity-wide assessment of their
emission reductions. However, entities that are small emitters can
register the offset reductions of other entities and not report on any
of their own emissions or reductions, although such small emitters
would have to submit an entity-statement and an estimate of their total
emissions indicating that they qualified as a small emitter. While
aggregators can be either small or large emitters, DOE believes that
most are likely to be small organizations or companies that would
qualify as small emitters. Some aggregators, such as trade
associations, might report on behalf of large emitters, but the
potential benefits of such indirect reporting by large emitters are
limited because essentially the same data and certifications would have
to be provided to DOE, whether the entity reported directly or through
an aggregator. DOE received some requests for clarification of these
requirements, but none of the comments suggested major changes.
G. Other Definitions
The interim final General Guidelines, and the Glossary accompanying
the draft Technical Guidelines, define terms used in the guidelines.
These definitions were the focus of considerable comment, and many
comments offered specific suggestions for changes. Others recommended
the addition of new definitions of terms or, in some cases, the
transfer of a definition that appeared in the Glossary to the
definition section of the General Guidelines. A few comments noted
differences between terms and definitions used in the DOE guidelines
and comparable terms and definitions used in other protocols for the
reporting of greenhouse gas emissions. While DOE has attempted to
minimize such differences, DOE has concluded that in some situations,
it is necessary to use a new term or define a term in a way that
differs from the usage or definition of the term used by other
programs. For this reason, DOE urges reporters and other users to
carefully review the definitions contained in both the final General
Guidelines and the final Technical Guidelines.
The following sections summarize the comments received on
definitions and DOE's response to the comments.
Activity of a small emitter. This term is used to define the
minimum scope of reports by small emitters interested in registering
reductions. It has been modified slightly to more clearly indicate that
it applies to anthropogenic actions that result in emissions or
sequestration.
Anthropogenic. This definition has been moved from the Glossary to
the General Guidelines and has been modified to more closely parallel
the definition of this term under the Climate Leaders and Climate
VISION programs.
Avoided emissions. The definition of this term has been modified to
enable it to encompass more types of ``avoided emissions'' in the
future. Its practical scope is still strictly limited by the reduction
calculation methods
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specifically identified and permitted under the guidelines. As
modified, the term encompasses any emission reduction that occurs
outside an entity's boundary that results from changes in the activity
of an entity, but in practice avoided emissions is still strictly
limited to the emissions displaced by increases in the distribution of
various types of energy that have been derived from renewable, nuclear
or other low or non-emitting sources.
Carbon dioxide equivalent. A definition for this term has been
added to the General Guidelines.
Carbon stocks. The definition of this term has been slightly
modified to clarify its scope in the context of these guidelines, as
suggested by public comment.
Climate Leaders and Climate VISION. The definitions of these
programs have been modified and moved to the General Guidelines.
Direct emissions. The definition has been modified to link such
emissions to sources within the organizational boundaries of reporting
entities.
Distributed energy. A definition for this term has been added to
the General Guidelines. The term ``exported energy,'' sometimes used in
the interim final guidelines, is no longer used.
The definition for ``entity-level reporting,'' which previously
appeared in the Glossary, has been deleted.
The definition of ``entity statements'' that appears in the
Glossary has been deleted. The meaning of the term ``Entity
Statements'' is fully described in section 300.5(d) and (e).
Greenhouse gases. The definition has been modified to more clearly
identify the gases that may be the subject of reports under the
guidelines.
Incidental lands. A definition for this term has been added to the
General Guidelines.
Indirect emissions. The definition for this term has been modified
to parallel similar modifications made to the definition of ``direct
emissions.'' The definition of ``emission, indirect'', which appears in
the Glossary, is repetitive and has been deleted. While the indirect
emissions are currently limited to those associated with the generation
of energy by another entity that is ultimately used by the reporting
entity, the definition leaves open the possibility that other types of
indirect emissions may be added in the future.
Intergovernmental Panel on Climate Change (IPCC). The definition
for the IPCC that appears in the Glossary has been modified in response
to comments received.
Net emission reductions. This refers to the sum of all reductions
in a given year that qualify for consideration as registered
reductions. It has been only slightly modified to improve its clarity.
Offset. The definition has been modified to improve its clarity.
Registration. A definition for this term has been added to the
General Guidelines.
Reporting entity. A definition for this term has been added to the
General Guidelines.
Sequestration. The definition has been simplified, but its intended
scope remains broad.
Source. The definition has been slightly expanded to emphasize its
broad scope.
Small emitter and large emitter. Definitions for both of these
terms have been added to the General Guidelines.
Start year. The definition has been simplified to improve its
clarity, as suggested by public comments.
Total emissions. The definition has been modified to correct an
error, as suggested by public comments.
H. Start Year and First Reduction Year
The interim final General Guidelines provide that reporters not
intending to register reductions can establish base periods as early as
the 1987-1990 timeframe identified in section 1605(b) and can report
reductions beginning as early as 1991. However, the interim final
guidelines provide that entities intent on registering reductions must
establish base periods of no more than four years that end no earlier
than 2002, and may not register reductions that were achieved prior to
2003.
DOE received a number of comments on these provisions of the
interim final guidelines, most of which recommended that entities be
allowed to report emissions and emission reductions that occurred prior
to 2002/2003. Some commenters indicated that they had made commitments
under the Climate Leaders or Climate VISION programs that used base
periods that ended prior to 2002 and that they were able to report the
progress made toward the achievement of these commitments prior to
2003. In response to these comments, DOE has modified the guidelines to
permit entities that have made a commitment to reduce entity-wide
emissions under the Climate Leaders or Climate VISION to establish base
periods that end as early as 2000. This exception would permit most,
but not all participants in these programs to use the same base periods
used in such voluntary programs in their reports to DOE under the 1605b
program.
DOE believes that even with this exception, the program will
continue to be focused on recent and future efforts to reduce
greenhouse gas emissions and consistent with providing an indication of
the reporting entities' contributions to the President's goal of
reducing greenhouse gas emissions intensity of the U.S. economy by 18
percent between 2002 and 2012. The revised General Guidelines still
permit reporting of historical activity, however, and therefore fully
comply with the statutory requirements of section 1605(b).
I. Electricity Factors and Benchmarks
The interim final guidelines establish several different kinds of
emission factors and benchmarks intended to approximate the emissions
associated with electricity use, the emissions avoided as a result of
reduced electricity demand, or the emissions avoided by increasing
generation from non-emitting or low-emitting sources. For emission
inventories, the interim final guidelines provide that entities should
convert their electricity demand to emissions using factors supplied by
DOE that would be based on the regional averages of electric sector
emissions intensities. DOE stated that entities should use factors that
were derived from the national average emissions intensity of the
electric sector as a whole for calculating reductions associated with
reduced electricity demand or increased generation from non-emitting or
low-emitting sources. DOE indicated that the national average emissions
intensity was considered to be a better indicator of the actual
emissions likely to be displaced by reduced demand or increased
generation.
Many commenters recommended making the factors used for inventories
and for calculating reductions the same, although some supported the
DOE's rationale for proposing different factors. Some advocated
regional factors as better indicators of the emissions and reductions
associated with specific sources. Others advocated national factors as
good indicators of actual emissions and reductions, and as a way of
simplifying the reporting burden of entities that operated in multiple
regions. Some utilities recommended that the benchmark used for
estimating avoided emissions be based on the regional averages of
fossil-fired generating plants, which they argued would be a better
indictor of the emissions being displaced. Other utilities recommended
that entities be permitted to choose either a system-specific
benchmark, based on the emissions intensity of marginal plants, or a
regional average.
After careful consideration of the comments, DOE has adopted the
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recommendation of some utilities to base the factors used to estimate
the emissions avoided by reduced electricity demand or increased
generation from non-emitting or low-emitting sources on the regional
average emissions intensities of fossil-fired generating plants, with
the proviso that no regional value may exceed 0.9 metric tons of
CO2 per megawatt hour (MWH). The maximum value of 0.9 metric
tons per MWH is designed to ensure that all utilities have a clear
incentive to build new capacity that is at least as efficient as the
most efficient coal-fired generating plants. DOE chose not to provide
generators with the flexibility to choose national or regional values,
or to develop their own, system-specific values in order to avoid the
significant self-selection bias that would result from such
flexibility.
The definition of the U.S. regions to be used in calculating the
indirect emissions associated with electricity use and avoided emission
benchmarks is an important technical issue. In the draft Technical
Guidelines, DOE indicated its intent to use North American Electric
Reliability Council (NERC) regions as the basis for the indirect
emission factors used in preparing emission inventories. Some comments
suggested that NERC subregions, especially for the western United
States would be more appropriate. Others urged DOE to consider the use
of EPA's eGRID regions. In choosing among these and other options, DOE
considered whether: (1) It would be possible to provide meaningful
values for all possible reporting years (the earliest possible
reporting year is 1987) based on readily available public data; (2)
reporters would be able to readily determine which factor applied to
specific facilities or operations; and (3) the resulting factors would
provide a good approximation of the indirect emissions associated with
electricity use or demand reductions in a particular region. After
careful consideration, DOE concluded that basing indirect emission
factors on either NERC or eGRID regions would not achieve one or more
of these three objectives. For example, because the NERC and eGRID
regions cut across state lines, it will likely be difficult for
reporters to determine which region is applicable to a specific
facility.
Consequently, DOE decided to base these factors on the electric
sector emission intensities of state-based regions that approximate the
most current NERC regions and, in the case of the western United
States, appropriate subregions. The purpose of these state-based
regions is to approximate the actual emissions associated with the
electricity supplied to users, while also utilizing data that is
readily available for all reporting years and boundaries that are well
recognized by potential reporters. EIA will determine the most
appropriate State groupings for the development of the indirect and
avoided emission factors based on NERC regions and applicable
subregions, as defined in June 2006. Generally, those states that are
split among two or more NERC regions or subregions should be assigned
to the state grouping that contains most of the state's population. One
possible grouping that will be considered by EIA is: (1) New York,
Connecticut, Rhode Island, Massachusetts, Vermont, New Hampshire and
Maine; (2) New Jersey, Delaware, Pennsylvania, Maryland, West Virginia,
Ohio, Indiana and Michigan; (3) Illinois and Wisconsin; (4) Missouri,
Kentucky, Virginia, Arkansas, Tennessee, North Carolina, South
Carolina, Louisiana, Mississippi, Alabama and Georgia; (5) Florida; (6)
Texas; (7) Oklahoma and Kansas; (8) North Dakota, South Dakota,
Nebraska, Minnesota and Iowa; (9) Colorado, Utah, Nevada, Wyoming and
Montana; (10) New Mexico and Arizona; (11) Oregon, Washington and
Idaho; (12) California; (13) Hawaii; and (14) Alaska. EIA will provide
factors for 1999 and subsequent data years and will periodically (e.g.,
every three to five years) update these factors to reflect what they
determine to be significant and lasting changes in the electric sector
emissions intensity of the established state groupings. EIA will also
provide a set of values to be used for all data years prior to 1999.
Several comments focused on the treatment of transmission and
distribution (T&D) losses in the calculation of the factors used to
represent the emissions associated with electricity demand (to be
included in emission inventories) and reductions in electricity demand
(to be included in emission reduction calculations). Some noted that
T&D losses were not included in the emission factors widely used by the
Climate Leaders program. Others favored the inclusion of such T&D
losses in the factors representing emissions associated with
electricity demand and reductions. DOE decided to continue to include
such losses in the factors used to estimate both the inventories and
reductions associated with electricity use. By including such losses,
these factors will provide a better indicator of the emissions
resulting from electricity demand. Entities that wish to include both
generation and T&D losses in their reporting of indirect emissions to
the Climate Leaders program may do so, as long as they note that their
reports include both types of losses, based on the factors provided by
DOE.
J. Inventories
The interim final guidelines provide detailed guidelines for the
conduct of emission inventories. DOE received a large number of
comments that touched on emission inventory guidelines in some way.
Most comments were generally supportive of the framework for emission
inventories set forth in the General Guidelines and the more detailed
provisions of the draft Technical Guidelines. However, some commenters
raised concerns regarding the start year and de minimis requirements of
the interim final guidelines, while others suggested various
improvements to the methods cited or the quality ratings assigned to
these methods.
In the final guidelines, an emissions inventory is an accounting of
an entity's actual emissions (direct, indirect and sequestered) during
a specified year. An emissions inventory provides, by itself, a useful
record of an entity's actual emissions over time, but it also serves as
one of the inputs necessary for the calculation of the base values used
in determining emission reductions. For this reason, an emissions
inventory is usually a major element of an entity's first report under
the program.
Since emission inventories are a critical part of calculating
emission reductions, all reports under the revised program should
include some kind of inventory. Entities that do not intend to register
reductions and small emitters may restrict their inventory data to
those sources or activities that will be the focus of future emission
reduction calculations. However, large emitters that intend to register
reductions must submit entity-wide emission inventories and may exclude
from such inventories only de minimis emissions. Any entity that wishes
to register reductions must ensure that its annual inventories meet the
minimum quality requirements specified in the guidelines.
The following sections summarize the major comments that addressed
the emission inventory requirements of the interim final guidelines and
DOE's responses to the comments.
1. Requirement for Entity-Wide Inventories With a Quality Rating of at
Least 3.0
The interim final guidelines established a quality rating system
for emission inventories. Reporters could choose among a range of
different methods for measuring or estimating the emissions from
specific sources. Each
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different method was assigned a rating of A, B, C or D and each of
these ratings was assigned a numerical value from 4.0 (for A rated
methods) to 1.0 (for D rated methods). Entities that were intent on
registering reductions would be required to complete emission
inventories that had a quantity-weighted quality rating of at least
3.0.
Most comments received by DOE supported the emphasis of the interim
final guidelines on quality entity-wide inventories. The final rule
retains the requirement for a 3.0 quality rating for the emissions
inventories that large emitters must submit as a prerequisite for
registering reductions. DOE believes that methods given an A or B
rating are sufficiently accurate to serve as the basis for entity-wide
reporting, while methods given a C or D rating should be used only for
those gases or sources that represent a small share of the reporting
entity's total emissions. Several commenters suggested that the A and B
methods available for specific sources or industrial sectors are too
burdensome and will make it difficult for some entities to prepare
inventories that meet the 3.0 quality rating. DOE has made some
modifications to the ratings for the available methods to ensure that a
cost-effective and practical A- or B-rated method is available for
every emissions source.
As the table below demonstrates, three very different companies
with diverse emission profiles could meet the 3.0 quality rating
threshold using an inventory approach specific to their company.
Company A is a large electric utility, with a vast preponderance of
emissions attributable to stationary fossil fuel combustion. As a
result, this company may use lower rated (and lower cost) methods for
estimating emissions from its smaller sources, such as fleet vehicles
and sulfur hexafluoride used as an insulator on transmission lines.
Similarly, a landfill operator could achieve the quality-rating
threshold by ensuring that it uses ``B'' or better-rated methods for
estimating methane emissions from the landfill. Company C, a large
Federal defense contractor, is able to offset its lower rated estimates
of emissions from mobile sources with higher rated methods for
estimating emissions from stationary combustion at its lone
manufacturing facility.
----------------------------------------------------------------------------------------------------------------
Emissions
Source metric tons Method Emissions weighted grade
CO2e grade
----------------------------------------------------------------------------------------------------------------
Company A (Large Utility)
Direct Emissions:
Stationary Combustion............................... 300,000 A = 4 300,000*4 = 1,200,000
Fleet Vehicles...................................... 10,000 C = 2 10,000*2 = 20,000
Sulfur Hexafluoride on T&D System................... 500 C = 2 500*2 = 1,000
Indirect Emissions:
Electricity in Commercial Offices................... 1,000 B = 3 1,000*3 = 3,000
-------------------------------------------------------
Total........................................... 311,500 3.92 1,224,000/311,500 = 3.92
=======================================================
Company B (Landfill Operator)
Direct Emissions:
Methane from Decomposition.......................... 50,000 B = 3 50,000*3 = 150,000
Heavy Duty Vehicle Fuel Use......................... 200 B = 3 200*3 = 600
Indirect Emissions:
Electricity Consumption............................. 50 A = 4 50*4 = 200
-------------------------------------------------------
Total........................................... 50,250 3.00 150,800/50,250 = 3.00
=======================================================
Company C (Large Federal Defense Contractor)
Direct Emissions:
Vehicle Fuel Use.................................... 500 C = 2 500*2 = 1,000
Stationary Combustion at Manufacturing Facility..... 800 A = 4 800*4 = 3,200
Indirect Emissions:
Electricity in Commercial Offices................... 9,000 B = 3