Deferral for CO2, 43490-43508 [2011-17256]
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Federal Register / Vol. 76, No. 139 / Wednesday, July 20, 2011 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 51, 52, 70, and 71
[EPA–HQ–OAR–2011–0083; FRL–9431–6]
RIN 2060–AQ79
Deferral for CO2 Emissions From
Bioenergy and Other Biogenic Sources
Under the Prevention of Significant
Deterioration (PSD) and Title V
Programs
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This action defers for a period
of three (3) years the application of the
Prevention of Significant Deterioration
(PSD) and Title V permitting
requirements to biogenic carbon dioxide
(CO2) emissions from bioenergy and
other biogenic stationary sources. This
action is being taken as part of the
process of granting the Petition for
Reconsideration filed by the National
Alliance of Forest Owners (NAFO) on
August 3, 2010, related to the PSD and
Title V Greenhouse Gas Tailoring Rule.
SUMMARY:
The result of this action is that during
this three year period biogenic CO2
emissions are not required to be counted
for applicability purposes under the
PSD and Title V permitting programs.
State, local, and tribal permitting
authorities may adopt the deferral at
their option but the deferral is effective
upon publication for the PSD and Title
V permit programs that are
implemented by EPA.
DATES: This action is effective on July
20, 2011.
ADDRESSES: EPA has established a
docket for this rulemaking under Docket
ID No. EPA–HQ–OAR–2011–0083. All
documents in the docket are listed in
the https://www.regulations.gov index.
Although listed in the index, some
information is not publicly available,
e.g., confidential business information
(CBI) or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, will be publicly
available only in hard copy. Publicly
available docket materials are available
either electronically at https://
www.regulations.gov or in hard copy at
the Air Docket, EPA/DC, EPA West,
Room 3334, 1301 Constitution Ave.,
NW., Washington, DC. This Docket
Facility is open from 8:30 a.m. to 4:30
p.m., Monday through Friday, excluding
Federal holidays. The telephone number
for the Public Reading Room is (202)
566–1744, and the telephone number for
the Air Docket is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT:
Carole Cook, Climate Change Division,
Office of Atmospheric Programs (MC–
6207J), Environmental Protection
Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460; telephone
number: (202) 343–9334; fax number:
(202) 343–2342; e-mail address:
biodeferralPSD@epa.gov.
Regulated
Entities. The Administrator determined
that this action is subject to the
provisions of Clean Air Act (CAA)
section 307(d). See CAA section
307(d)(1)(V) (the provisions of section
307(d) apply to ‘‘such other actions as
the Administrator may determine’’).
These are final amendments to existing
regulations. This action applies to
stationary sources that emit biogenic
CO2.
SUPPLEMENTARY INFORMATION:
TABLE 1—EXAMPLES OF AFFECTED ENTITIES BY CATEGORY
Category
NAICS
Biomass combustion .................................
221
321
322
562213
112
221320
562212
325193
325411
311/312
Municipal solid waste combustion ............
Sources/users of biogas ...........................
Fermentation processes ...........................
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Other .........................................................
Table 1 of this preamble lists the
types of entities that potentially could
be affected by the deferral covered by
this action. This list is not intended to
be exhaustive, but rather provides a
guide for readers regarding facilities
likely to be affected by this action. Note
that this rule does not make or infer any
policy determination on the part of EPA
whether any emissions from any of
these sources may be determined
‘‘fugitive’’ emissions for the purposes of
accounting and applicability under air
permitting requirements. Such
determinations are not within the scope
of this rule and are part of the case-bycase application and review process
established under the regulations
covering these permitting requirements.
If you have questions regarding the
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Examples of affected facilities
Electric utilities burning biomass fuels.
Wood products manufacturing, and wood pellet fuel manufacturing.
Pulp and paper manufacturing.
Solid waste combustors and incinerators.
Animal production manure management operations.
Sewage treatment facilities.
Solid waste landfills.
Ethanol manufacturing.
Medicinal and botanical manufacturing.
Food/Beverage processors burning agricultural biomass residues, using fermentation processes, or producing/using biogas from anaerobic digestion of waste materials.
applicability of this action to a
particular facility, consult the person
listed in the FOR FURTHER INFORMATION
CONTACT section of this preamble.
What is the effective date? The final
rule is effective on July 20, 2011.
Section 553(d) of the Administrative
Procedure Act (APA), 5 U.S.C. Chapter
5, generally provides that rules may not
take effect earlier than 30 days after they
are published in the Federal Register.
EPA is issuing this final rule under
section 307(d)(1) of the Clean Air Act,
which states: ‘‘The provisions of section
553 through 557 *** of Title 5 shall not,
except as expressly provided in this
section, apply to actions to which this
subsection applies.’’ Thus, section
553(d) of the APA does not apply to this
rule. EPA is nevertheless acting
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consistently with the purposes of the
underlying APA section 553(d) in
making this rule effective on July 20,
2011. Section 5 U.S.C. 553(d)(3) allows
an effective date less than 30 days after
publication ‘‘as otherwise provided by
the agency for good cause found and
published with the rule.’’ As explained
below, EPA finds that there is good
cause for this rule to become effective
on July 20, 2011, even through this
results in fewer than 30 days from the
date of publication in the Federal
Register.
EPA announced its intent to
undertake this rulemaking on January
12, 2011, in order to provide the Agency
time to conduct a detailed examination
of the science and technical issues
associated with biogenic CO2 emissions
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from stationary sources. The Agency
intended to complete the rulemaking
before sources would be subject to the
PSD and Title V programs for GHG
emissions because at that time it was
possible that a source could be subject
to those requirements based on biogenic
CO2 emissions. The Agency determined
it could be burdensome for both
permitting authorities and sources to
assess those emissions until our detailed
examination was complete. In a January
12, 2011, letter to several members of
Congress, the Administrator wrote, ‘‘No
source will be subject to the preconstruction permitting requirement
solely because of its greenhouse gas
emissions until after July 1, 2011. With
the approach of July 1 in mind, I am
announcing today that, by that date,
EPA will complete a rulemaking to defer
for three years the application of the
pre-construction permitting requirement
to biomass and other biogenic CO2
emissions.’’
One purpose of the 30-day waiting
period prescribed in 5 U.S.C. 553(d) is
to give affected parties a reasonable time
to adjust their behavior and prepare
before the final rule takes effect.
Whereas here, the affected parties are
anticipating this rule and requesting the
flexibility it provides, and any delay in
its effectiveness will result in
uncertainty in the permitting process. In
order to ensure that the final rule is
available to the public by July 1, 2011,
the final rule will be signed and made
available on the EPA Web site.
Publication may follow one to two
weeks after that date. A shorter effective
date is also consistent with the purposes
of APA section 553(d)(1), which
provides an exception for any action
that grants or recognizes an exemption
or relieves a restriction. Here, this action
relieves a burden because it defers the
applicability of the PSD and Title V
permitting requirements for biogenic
stationary sources for a period of three
years. Accordingly, we find good cause
exists to make this rule effective on July
20, 2011, consistent with the purposes
of 5 U.S.C. 553(d)(1) and (3).
Judicial Review. Under section
307(b)(1) of the CAA, judicial review of
this final rule is available only by filing
a petition for review in the U.S. Court
of Appeals for the District of Columbia
Circuit (the Court) by September 19,
2011. Under CAA section 307(d)(7)(B),
only an objection to this final rule that
was raised with reasonable specificity
during the period for public comment
can be raised during judicial review.
CAA section 307(d)(7)(B) also provides
a mechanism for EPA to convene a
proceeding for reconsideration, ‘‘[i]f the
person raising an objection can
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demonstrate to EPA that it was
impracticable to raise such objection
within [the period for public comment]
or if the grounds for such objection
arose after the period for public
comment (but within the time specified
for judicial review) and if such objection
is of central relevance to the outcome of
the rule.’’ Any person seeking to make
such a demonstration to us should
submit a Petition for Reconsideration to
the Office of the Administrator,
Environmental Protection Agency,
Room 3000, Ariel Rios Building, 1200
Pennsylvania Ave., NW., Washington,
DC 20460, with a copy to the person
listed in the preceding FOR FURTHER
INFORMATION CONTACT section, and the
Associate General Counsel for the Air
and Radiation Law Office, Office of
General Counsel (Mail Code 2344A),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20004. Note, under CAA section
307(b)(2), the requirements established
by this final rule may not be challenged
separately in any civil or criminal
proceedings brought by EPA to enforce
these requirements.
Acronyms and Abbreviations. The
following are acronyms and
abbreviations of terms used in this
preamble.
BACT best available control technology
BAU business as usual
CAA Clean Air Act
CBI confidential business information
CFI Call for Information
CFR Code of Federal Regulations
CH4 methane
CO2 carbon dioxide
CO2e carbon dioxide equivalents
EO Executive Order
EPA U.S. Environmental Protection Agency
FR Federal Register
GHG/GHGs greenhouse gas/greenhouse
gases
GWP global warming potential
LULUCF Land-Use, Land-Use Change and
Forestry
MSW municipal solid waste
NAFO National Alliance of Forest Owners
NAAQS National Ambient Air Quality
Standards
NOX nitrogen oxides
NSPS New Source Performance Standards
NSR New Source Review
NTTAA National Technology Transfer and
Advancement Act of 1995
PSD Prevention of Significant Deterioration
PTE potential to emit
RFA Regulatory Flexibility Act
SAB Science Advisory Board
SILs significant impact levels
SIP State Implementation Plan
SMCs significant monitoring concentrations
tpy tons per year
U.S. United States
UMRA Unfunded Mandates Reform Act
UNFCCC United Nations Framework
Convention on Climate Change
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Outline. The information presented in
this preamble is organized as follows:
I. Background
II. Summary of Final Action
A. Overview of the Final Rule
B. Legal Authority
C. Facilities Permitted During Deferral
D. Mechanism for Deferral and State
Implementation
III. Response to Public Comments
A. Overview of Public Comments
B. Comments on the Deferral
C. Comments on Science, Accounting, and
Economic Issues
D. Comments on PSD, Title V and the
Tailoring Rule
E. Comments on the Interim Guidance
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
(UMRA)
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. Background
On June 3, 2010, EPA published the
final Prevention of Significant
Deterioration (PSD) and Title V
Greenhouse Gas Tailoring Rule (herein
referred to as the Tailoring Rule; 75 FR
31514), setting thresholds for GHG
emissions that define when permits
under these programs are required for
new and existing industrial facilities.
Beginning January 2, 2011, sources
currently subject to PSD or Title V
permitting programs were required to
determine the best available control
technology (BACT) for their GHG
emissions, but only for GHG increases of
75,000 short tons per year (tpy) or more
of total GHGs, on a carbon dioxide
equivalents (CO2e) basis and any
increase on a mass basis. At that time,
no sources would be subject to CAA
permitting requirements due solely to
GHG emissions.
Beginning July 1, 2011, the PSD
permitting requirements will for the first
time cover new construction projects
that will emit GHGs of at least 100,000
tpy on a CO2e basis even if they do not
exceed the permitting thresholds for any
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other pollutant. Modifications at
existing facilities that increase GHG
emissions by at least 75,000 tpy, and
any amount on a mass basis, will be
subject to permitting requirements, even
if they do not significantly increase
emissions of any other pollutant.
Operating permit requirements will, for
the first time, apply to sources based on
their GHG emissions even if they would
not apply based on emissions of any
other pollutant. Facilities that emit at
least 100,000 tpy CO2e will be subject to
Title V permitting requirements.
As discussed in the final Tailoring
Rule, EPA decided not to provide
exemptions from applicability
determinations (major source and major
modification) under PSD and Title V for
certain GHG emission sources,
including biogenic emissions. EPA
decided instead to address the need for
tailoring through a uniform thresholdbased approach, rather than through a
collection of various specific exclusions.
At that time, EPA also noted that it
planned to seek further comment on
how it might address biogenic CO2
emissions under the PSD and Title V
programs through a future action.
On July 15, 2010, EPA published a
Call for Information (CFI) to solicit
information and viewpoints from
interested parties on approaches to
accounting for GHG emissions from
bioenergy and other biogenic sources
(75 FR 41173). The purpose of this CFI
was to request comment on possible
accounting approaches for biogenic CO2
emissions under the PSD and Title V
programs, as well as to receive data
submissions about these sources and
their GHG emissions, general technical
comments on accounting for these
emissions, and comments on the
underlying science that should inform
any such accounting approach.
On August 3, 2010, NAFO petitioned
the EPA to reconsider and stay the
implementation of the PSD and Title V
GHG Tailoring Rule. The petition
alleged that the final Tailoring Rule
declared, for the first time and without
any prior proposal or notice to industry,
that EPA would count CO2 emissions
from combustion of biomass toward the
applicability thresholds established for
the PSD and Title V permitting
programs of the CAA. Petitioners further
alleged that EPA’s proposed rule had
provided for the appropriate and
opposite conclusion: That CO2
emissions from combustion of biomass
should not be counted. Petitioners
stated that there is near-universal
recognition that CO2 emitted from
combustion of fuels derived from
biomass should be excluded from GHG
regulations because production and
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combustion of such fuels do not
increase atmospheric CO2 levels.
Pending reconsideration, petitioners
requested that the application of the
PSD and Title V permitting programs to
emissions of CO2 from biomass be
stayed.
We considered carefully the
petitioners’ assertions and noted that we
also received comments through the CFI
supporting the exclusion of biogenic
CO2 from stationary source permitting
requirements. Through the CFI,
however, EPA also received information
supporting the position that biogenic
CO2 should not be excluded from
permitting programs, and that the use of
certain types of biomass as fuel could
increase atmospheric CO2 levels. Based
on consideration of the petitioners’
arguments, together with the weight of
the comments received through the CFI,
EPA concluded that the issue of
accounting for the net atmospheric
impact of biogenic CO2 emissions is
complex enough that further
consideration of this important issue is
warranted. Therefore, EPA granted the
NAFO petition on January 12, 2011.1
On January 12, 2011, EPA also
announced in letters to Members of
Congress and NAFO its intent to take a
number of steps to address the issues
associated with biogenic CO2 emissions
from stationary sources. Pursuant to this
announcement, on March 21, 2011, EPA
published a notice of proposed
rulemaking to defer for three years the
application of the PSD and Title V
permitting requirements to biogenic CO2
emissions from stationary sources (76
FR 15249). Concurrent with this
rulemaking, EPA also issued interim
guidance entitled, ‘‘Guidance for
Determining Best Available Control
Technology for Reducing Carbon
Dioxide Emissions from Bioenergy
Production’’ to help permitting
authorities establish a basis for
concluding that under the PSD Program
the combustion of biomass fuels can be
considered BACT for biogenic CO2
emissions at stationary sources until
such time as the deferral becomes
effective. During the three-year deferral
period, EPA will conduct a detailed
examination of the science associated
with biogenic CO2 emissions from
stationary sources, including engaging
with Federal partners, technical experts,
and an independent scientific panel to
consider technical issues. Based on the
feedback from the scientific and
technical review, EPA will then
undertake a rulemaking to determine
how biogenic CO2 emissions should be
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treated and accounted for in PSD and
Title V permitting.
On April 27, 2011, EPA’s Science
Advisory Board (SAB) published a
notice soliciting experts for a peer
review of EPA’s science and technical
work on biogenic CO2 emissions. 76 FR
23587. EPA intends to provide its study
that examines the science and technical
issues associated with biogenic CO2
emissions from stationary sources and
accompanying accounting framework to
the SAB for peer review later in 2011.
II. Summary of Final Action
A. Overview of the Final Rule
This action defers for a period of three
(3) years the consideration of CO2
emissions from bioenergy and other
biogenic sources (hereinafter referred to
as ‘‘biogenic CO2 emissions’’) when
determining whether a stationary source
meets the PSD and Title V applicability
thresholds, including those for the
application of BACT. Stationary sources
that combust biomass (or otherwise emit
biogenic CO2 emissions) and construct
or modify during the deferral period
will avoid the application of PSD to the
biogenic CO2 emissions resulting from
those actions. This deferral applies only
to biogenic CO2 emissions and does not
affect non-GHG pollutants or other
GHGs (e.g., methane (CH4) and nitrous
oxide (N2O)) emitted from the
combustion of biomass fuel. Also, this
deferral only pertains to biogenic CO2
emissions in the PSD and Title V
programs and does not pertain to any
other EPA programs such as the GHG
Reporting Program.
EPA recognizes that use of certain
types of biomass can be part of the
national strategy to reduce dependence
on fossil fuels, efforts are underway at
the Federal, State and regional level to
foster the expansion of renewable
resources and promote bioenergy
projects when they are a way to address
climate change, increasing domestic
alternative energy production,
enhancing forest management and
creating related employment
opportunities. We believe part of
fostering this development is to ensure
that those feedstocks with negligible net
atmospheric impact not be subject to
unnecessary regulation. At the same
time, it is important that EPA have time
to conduct its detailed examination of
the science and technical issues related
to accounting for biogenic CO2
emissions and therefore have finalized
this deferral.
This deferral is intended to be a
temporary measure, in effect for no
more than three years, to allow the
Agency time to complete its work and
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determine what, if any, treatment of
biogenic CO2 emissions should be in the
PSD and Title V programs. This is not
EPA’s final determination on the
treatment of biogenic CO2 emissions in
those programs. The Agency plans to
complete its science and technical
review and any follow-on rulemakings
within the three-year deferral period
and further believes that three years is
ample time to complete these tasks. It is
possible that the subsequent
rulemaking, depending on the nature of
EPA’s determinations, would supersede
this rulemaking and become effective in
fewer than three years.
Biogenic CO2 emissions are defined as
emissions of CO2 from a stationary
source directly resulting from the
combustion or decomposition of
biologically-based materials other than
fossil fuels and mineral sources of
carbon. Examples of ‘‘biogenic CO2
emissions’’ include, but are not limited
to:
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• CO2 generated from the biological
decomposition of waste in landfills,
wastewater treatment or manure management
processes;
• CO2 from the combustion of biogas
collected from biological decomposition of
waste in landfills, wastewater treatment or
manure management processes;
• CO2 from fermentation during ethanol
production or other industrial fermentation
processes;
• CO2 from combustion of the biological
fraction of municipal solid waste or
biosolids;
• CO2 from combustion of the biological
fraction of tire-derived fuel; and
• CO2 derived from combustion of
biological material, including all types of
wood and wood waste, forest residue, and
agricultural material.
For stationary sources co-firing fossil
fuel and biologically-based fuel, and/or
combusting mixed fuels (e.g., tirederived fuels, municipal solid waste
(MSW)), the biogenic CO2 emissions
from that combustion are included in
this deferral. However, the fossil CO2
emissions are not. Emissions of CO2
from processing of mineral feedstocks
(e.g., calcium carbonate) are also not
included in this deferral. Various
methods are available to calculate both
the biogenic and fossil portions of CO2
emissions, including those methods
contained in the GHG Reporting
Program (40 CFR Part 98). Consistent
with the other pollutants in PSD and
Title V, there are no requirements to use
a particular method in determining your
biogenic and fossil CO2 emissions.
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B. Legal Authority
1. Applicability of PSD and Title V to
Biogenic CO2 Emissions From Major
Stationary Sources
As currently written, the PSD and
Title V regulations apply to biogenic
CO2 emissions from major sources or
major modifications at such sources
according to the limitation included
under the definition of ‘‘subject to
regulation’’ in the State Implementation
Plan (SIP) regulations at 40 CFR 51.166
and the Title V state program
regulations at 40 CFR 70.2, as well as
the Federal Implementation Plan
requirements at 40 CFR 52.21 and the
Title V Federal program regulations at
40 CFR 71.2. Thus, revisions to these
regulations are necessary to defer
application of the PSD and Title V
programs to such sources of biogenic
CO2.
Stationary sources of air pollutants,
including sources of biogenic CO2
emissions, are currently subject to PSD
requirements if they emit more than 100
or 250 tpy of a regulated NSR pollutant
other than GHGs and have triggered PSD
as a result of these emissions, subject to
the permitting thresholds established in
the Final Tailoring Rule described
below. The 100/250 tpy thresholds
previously described originate from
section 169 of the CAA, which applies
PSD to any ‘‘major emitting facility’’ and
defines the term to include any source
with a potential to emit (PTE) ‘‘any air
pollutant’’ in an amount over 100 or 250
tpy, depending on source category.
EPA’s long-standing regulations limit
the PSD applicability provision that
refers to ‘‘any air pollutant’’ to refer to
any ‘‘regulated NSR pollutant,’’ which
in turn includes any air pollutant
‘‘subject to regulation’’ under the CAA.
Similarly, under sections 165(a)(4) and
169(3) of the CAA, the BACT
requirement applies to ‘‘each pollutant
subject to regulation’’ under the CAA.
As noted in other recent EPA actions,
GHGs are currently ‘‘subject to
regulation’’ under the CAA; subject, for
PSD purposes, to specific limitations
reflected in the definition of that term
that EPA adopted in the Tailoring Rule.
Thus, emissions of GHGs (including
CO2) must be considered in determining
whether a source is a major emitting
facility subject to PSD, as a result of
construction or modification, and
whether the BACT requirement applies
to GHGs (including CO2 as a component
of GHGs). In light of the way these
regulations are currently written, EPA is
unable to exclude biogenic CO2
emissions from PSD review without
amending the regulations.
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With respect to Title V, as noted
previously, Title V applies to sources,
among others, that emit 100 tons per
year of specified quantities of ‘‘any air
pollutant,’’ see CAA section 502(a),
501(2)(B) and 302(g).
2. Tailoring Rule
a. Rationale and Requirements
In the Tailoring Rule, EPA codified its
interpretation that ‘‘subject to
regulation’’ only extends to major
sources of air pollutants subject to a
requirement for actual control of the
quantity of emissions of that pollutant,
and that such a control requirement has
taken effect and is operative to control,
limit or restrict the quantity of
emissions of that pollutant released
from the regulated activity, see 75 FR at
31606–07, and further defined ‘‘subject
to regulation’’ such that GHGs are only
‘‘subject to regulation’’ under certain
circumstances defined in the Tailoring
Rule.
In the Tailoring Rule, EPA recognized
that if the applicability provisions of the
PSD and Title V programs were applied
literally so that PSD and Title V
requirements applied to GHG-emitting
sources at the 100/250 tpy levels
provided in the CAA, then the
permitting authorities would be
overwhelmed by the large numbers of
permittees and many small sources
would be unduly encumbered by the
permitting demands. In light of those
impacts, EPA concluded that, as a legal
matter, Congress did not intend that the
PSD and Title V applicability
requirements be applied literally to all
sources emitting GHGs over the major
source thresholds as of January 2, 2011,
the date by which EPA determined that
GHGs become subject to regulation
under the CAA as a result of the motor
vehicle rule. Instead, EPA concluded
that it is authorized to tailor those
applicability requirements to apply PSD
and Title V to such sources in a phasedin manner, starting with the largest
sources first.
Specifically, in the Tailoring Rule,
EPA has implemented these PSD and
Title V applicability provisions by
applying the familiar two-step
framework for interpreting
administrative statutes recognized by
the Supreme Court in Chevron U.S.A.
Inc. v. NRDC, 467 U.S. 837 (1984),
taking into account certain legal
doctrines. Those doctrines, insofar as
relevant to the Tailoring Rule, are (1) the
‘‘absurd results’’ doctrine, which
authorizes agencies to apply statutory
requirements differently than a literal
reading would indicate, as necessary to
effectuate congressional intent and
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avoid absurd results; (2) the
‘‘administrative necessity’’ doctrine,
which authorizes agencies to apply
statutory requirements in a way that
avoids impossible administrative
burdens; and (3) the ‘‘one-step-at-atime’’ doctrine, which authorizes
agencies to implement a regulatory
scheme in a deliberate, step-wise
fashion. See 75 FR 31541–31579.
Under Chevron, the agency must, at
step 1, determine whether Congress’
intent as to the specific matter at issue
is clear, and, if so, the agency must give
effect to that intent. 467 U.S. at 842. If
congressional intent is not clear, then, at
step 2, the agency has discretion to
fashion an interpretation that is a
reasonable construction of the statute.
467 U.S. at 865. To determine
congressional intent, the agency must
first consider the words of the statutory
requirements, and if their literal
meaning answers the question at hand,
then, in most cases, the agency must
implement those requirements by those
terms.
However, under the ‘‘absurd results’’
doctrine, the literal meaning of statutory
requirements should not be considered
to indicate congressional intent if that
literal meaning would produce a result
that is senseless or that is otherwise
inconsistent with — and especially one
that undermines — underlying
congressional purpose. In these cases, if
congressional intent for how the
requirements apply to the question at
hand is clear, the agency should
implement the statutory requirements
not in accordance with their literal
meaning, but rather in a manner that
most closely effectuates congressional
intent. If congressional intent is not
clear, then an agency may select an
interpretation that is reasonable under
the statute.
Under the ‘‘administrative necessity’’
doctrine, Congress is presumed, at
Chevron step 1, to intend that its
statutory directives to agencies be
administrable, and not to have intended
to have written statutory requirements
that are impossible to administer.
Therefore, under this doctrine, an
agency may depart from statutory
requirements that, by their terms, are
impossible to administer, but the agency
may depart no more than necessary to
render the requirements administrable.
In addition to the ‘‘absurd results’’
and ‘‘administrative necessity’’
doctrines, another judicial doctrine
supports at least part of EPA’s Tailoring
Rule, and that is the doctrine that
agencies may implement statutory
mandates one step at a time, which we
will call the ‘‘one-step-at-a-time’’
doctrine. The U.S. Supreme Court
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recently described the doctrine in
Massachusetts v. EPA, 549 U.S. 497, 524
(2007), as follows: ‘‘Agencies, like
legislatures, do not generally resolve
massive problems in one fell regulatory
swoop;’’ and instead they may
permissibly implement such regulatory
programs over time, ‘‘refining their
preferred approach as circumstances
change and as they develop a more
nuanced understanding of how best to
proceed.’’
In the Tailoring Rule, EPA closely
considered the burdens to the
permitting authorities of applying PSD
and Title V to GHG-emitting sources.
For example, EPA calculated, on a
national basis, the workload that GHG
permit applications would entail, and
compared that to the existing workload
of permitting authorities. EPA
concluded that permitting authorities
would be overwhelmed by permit
applications if the PSD and Title V
applicability thresholds were applied
literally as of January 2, 2011, to the
GHG emissions from stationary sources.
In addition, EPA calculated the cost to
the sources of permitting requirements
and concluded that many small sources
would become subject to unduly high
expenses.
Accordingly, in applying the Chevron
analytical framework, in conjunction
with the absurd results and
administrative necessity doctrines, EPA
concluded that Congress intended that
PSD and Title V apply to the GHG
emissions from stationary sources, but
that, in light of the burdens to the
permitting authority and the costs to the
sources of determining applicability of
permitting requirements by applying the
statutory thresholds to GHG emissions,
the application of the permitting
programs should be phased in, starting
with the largest sources of GHG
emissions first. EPA also concluded that
the calculation for determining which
sources emit the ‘‘largest’’ amount of
GHG emissions should be based on the
amount of GHG pollutant emitted in
tons per year, weighted by the global
warming potential (GWP) of the
particular GHG pollutant.
Accordingly, in the Tailoring Rule,
EPA established two steps to implement
PSD and Title V. At step 1, beginning
January 2, 2011, sources currently
subject to PSD or Title V permitting
programs were required to determine
the BACT for their GHG emissions, but
only for GHG increases of 75,000 short
tons per year (tpy) or more of total
GHGs, on a CO2e basis and any increase
on a mass basis. At that time, no sources
would be subject to CAA permitting
requirements due solely to GHG
emissions. At step 2, beginning July 1,
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2011, the PSD permitting requirements
will for the first time cover new
construction projects that will emit GHG
emissions of at least 100,000 tpy on a
CO2e basis (and 250 tons on a mass
basis) even if they do not exceed the
permitting thresholds for any other
pollutant. Modifications at existing
facilities that emit at that level and
increase GHG emissions by at least
75,000 tpy CO2e and by any amount on
a mass basis will be subject to
permitting requirements, even if they do
not significantly increase emissions of
any other pollutant.
In addition, EPA committed to
promulgate by July 1, 2012, another
rulemaking—in effect, step 3 of the
Tailoring Rule—that would consider
whether to reduce the thresholds
further. EPA also committed to
promulgate another rulemaking after
that, by April 1, 2016, that would
consider still further action. As EPA
stated in the Tailoring Rule, part of the
purpose of the phase-in approach
embodied in the Tailoring Rule is to
allow permitting authorities time to
acquire additional resources and to
allow EPA time to develop streamlining
methods and thereby enable the
application of PSD and Title V to more
sources in subsequent rulemakings.
As noted previously, in the Tailoring
Rule, EPA determined that the amount
of each GHG emitted by a facility should
be calculated by reference to the weight
of the GHG emissions, in tons of CO2e
per year for determining if GHGs were
‘‘subject to regulation’’ for a particular
facility and project. The Tailoring Rule
proposal referenced EPA’s Inventory of
U.S. Greenhouse Gas Emissions and
Sinks (Inventory) 2 submitted annually
to the United Nations Framework
Convention on Climate Change
(UNFCCC), for the applicable GWP
values and guidance on how to calculate
a source’s GHG emissions in tpy CO2e.
75 FR 31514–31608. The Inventory
includes emissions of the six GHGs in
terms of CO2e units. By linking the
calculation of CO2e for GHGs to GWP
values, a facility could evaluate its total
GHG emissions contribution based on a
single metric. We solicited comment on
the benefits and limitations of this
proposed metric.
While we referred to the Inventory for
GWP identification purposes only,
several commenters appeared to
misunderstand our intent, claiming that
the Inventory excludes CO2 emitted
from biomass. These commenters
2 ‘‘Inventory of U.S. Greenhouse Gas Emissions
and Sinks: 1990–2008,’’ U.S. Environmental
Protection Agency, EPA 430–R–10–006 (April 15,
2010). https://www.epa.gov/climatechange/
emissions/usinventoryreport.html.
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requested that, in calculations of
emissions for determining applicability
of PSD and Title V, EPA exempt
emissions from biogenic activities or
biomass combustion or oxidation
activities, including solid waste
landfills, waste-to-energy projects,
fermentation processes, combustion of
renewable fuels, ethanol manufacturing,
biodiesel production, and other
alternative energy production that uses
biomass feedstocks (e.g., crops or trees).
In particular, these commenters urged
that EPA exclude emissions from
biomass combustion in determining the
applicability of PSD to such sources
based on the notion that such
combustion is ‘‘carbon neutral’’ (i.e.,
that combustion or oxidation of such
materials would cause no net increase
in GHG emissions on a lifecycle basis).
b. Treatment of Biogenic Emissions
In response, when finalizing the
Tailoring Rule, we acknowledged the
role that biomass or biogenic fuels and
feedstocks could play in reducing
anthropogenic GHG emissions, and did
not dispute the commenters’
observations that many state, Federal,
and international rules and policies
treat biogenic and fossil sources of CO2
emissions differently (75 FR 31514).
Regarding commenters’ claims that the
Inventory excludes CO2 emissions from
biomass, EPA noted that the Inventory
does not exclude these emissions (see
section II.A.2 of the preamble to the
proposed deferral rule). Rather, they are
included in the Land-Use, Land-Use
Change and Forestry (LULUCF) Sector
rather than the Energy Sector to avoid
double-counting at the national scale.
The narrow reference to the use of the
Inventory’s GWP values for estimating
GHG emissions was provided to offer
consistent guidance on how to calculate
these emissions and not as an
indication, direct or implied, that
biomass emissions would be excluded
from permitting applicability merely by
association with the national inventory,
see 74 FR 55351, under the definition
for ‘‘carbon dioxide equivalent.’’
We determined that our application of
the ‘‘absurd results,’’ ‘‘administrative
necessity,’’ and one-step-at-a-time legal
rationales supporting the Tailoring Rule,
based on the expected overwhelming
permitting burdens in its absence, did
not provide sufficient basis to exclude
emissions of CO2 from biogenic sources
in determining permitting applicability
provisions at that time. We reasoned
that such an exclusion alone, while
reducing burdens for some sources,
would not address the overwhelming
permitting burdens, and a thresholdbased approach would still be needed.
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At that time, we had not examined
burdens with respect to specific source
categories impacted by the rule and thus
had not analyzed the administrative
burden of permitting projects that
specifically involve biogenic CO2
emissions taking account of the
threshold-based approach. Commenters
also did not provide information to
demonstrate that an overwhelming
permitting burden would still exist,
justifying a temporary exclusion for
biomass sources.
In the final Tailoring Rule, we
indicated that the decision not to
provide this type of an exclusion at that
time did not foreclose EPA’s ability to
either (1) provide this type of exclusion
at a later time with additional
information about overwhelming
permitting burdens due to biomass
sources, or (2) provide another type of
exclusion or other treatment based on
some other rationale. Although we did
not take a final position, we noted that
some commenters’ observations about a
different treatment of biomass
combustion warranted further
exploration as a possible rationale.
Therefore, although we did not
establish a permanent exclusion from
PSD or Title V applicability based on
specific characteristics of biogenic CO2,
we indicated our intent to seek further
comment on how we might address
emissions of biogenic CO2 under the
PSD and Title V programs through a
future action.
We further noted that, while not
promulgating an applicability exclusion
for biogenic emissions and biomass
fuels or feedstocks in the final Tailoring
Rule, flexibility exists to apply the
existing regulations and policies
regarding BACT in ways that take into
account their net effects on atmospheric
GHG concentrations. Without
prejudging the outcome of our process
to seek comment on whether and how
we might address emissions of biogenic
carbon under the PSD and Title V
programs through a future action, we
indicated that this issue warranted
further exploration.
As mentioned earlier in the preamble,
in order to explore the issue further
following the promulgation of the
Tailoring Rule, on July 15, 2010, EPA
solicited views from the public through
a CFI on approaches to accounting for
biogenic CO2 emissions, on the means to
estimate and measure CO2 emissions
from a variety of biogenic CO2 sources
and other information on biogenic
sources that may be affected but not
identified in the CFI.
With promulgation of the Tailoring
Rule we committed to issue technical
and policy guidance for permitting of
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43495
GHGs. Subsequently, the information
gathered from stakeholders in response
to the CFI provided diverse perspectives
on treatment of biogenic CO2 emissions
in pre-construction and operating
permit reviews, including many
requests to exclude, either partially or
wholly, biogenic CO2 sources from PSD
applicability determinations and BACT
analyses on the basis of Inventory
results and other considerations. On
November 10, 2010, EPA issued the
draft ‘‘PSD and Title V Permitting
Guidance for Greenhouse Gases’’ which
provides the basic information that
permit writers and applicants need to
address GHG emissions in permits.
Within the November guidance, EPA
acknowledged the numerous
stakeholder comments on biogenic CO2
BACT analyses and provided general
guidance to permitting authorities to
consider environmental, energy, and
economic benefits that may accrue from
the use of certain types of biomass (e.g.,
biogas from landfills for energy
generation), consistent with existing air
quality standards. We also committed to
provide more detailed technical and
policy guidance early in 2011 for
completing step 4 of a ‘‘top-down’’
BACT analysis for GHG emissions from
certain types of biomass sources to
enable permitting authorities to simplify
and streamline BACT determinations for
such sources. EPA provided interim
guidance on this topic in March 2011,
concurrent with the proposal of this rule
to assist permitting authorities before
the deferral becomes effective.3
Noting that a variety of Federal and
state policies have recognized that some
types of biomass can be part of a
national strategy to reduce dependence
on fossil fuels and to reduce emissions
of GHGs, EPA has determined that it is
appropriate for permitting authorities to
account for both existing Federal and
state policies and their underlying
objectives in evaluating the
environmental, energy and economic
benefits of biomass fuel. Based on these
considerations, permitting authorities
might determine that the use of certain
types of biomass alone meets the BACT
requirement for GHGs.
As described in the Background
section of this preamble, NAFO
petitioned the EPA on August 3, 2010 to
reconsider and stay the implementation
of the PSD and Title V GHG Tailoring
Rule. Pending reconsideration,
petitioners requested that the
application of the PSD and Title V
3 ‘‘Guidance for Determining Best Available
Control Technology for Reducing Carbon Dioxide
Emissions from Bioenergy Production,’’ U.S. EPA
Office of Air and Radiation, March 2011. (https://
www.epa.gov/nsr/ghgdocs/bioenergyguidance.pdf)
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permitting programs to emissions of CO2
from biomass be stayed.
Based on consideration of the
petitioners’ arguments, together with the
weight of the comments received on the
CFI, EPA concluded that the issue of
accounting for the net atmospheric
impact of biogenic CO2 emissions is
complex enough that further
consideration of this important issue is
warranted. Therefore, EPA granted the
petition on January 12, 2011.
However, EPA did not grant the
request for an administrative stay of the
Tailoring Rule, because the rule is
critical for making overall
implementation of the PSD program
feasible. Furthermore, an administrative
stay of the statements in the preamble
of the Tailoring Rule that describe EPA’s
initial determination not to exempt
emissions of CO2 from biomass would
not provide the requested relief of
excluding emissions of CO2 from
biomass from the PSD and Title V
permitting programs. The effect of a stay
of this or any other aspect of the
Tailoring Rule would be to return to the
legal regime that existed before EPA’s
issuance of a final Tailoring Rule. As no
exemption for emissions of CO2 from
biomass existed prior to the final rule,
an administrative stay would not result
in an exemption from the requirements
of PSD and Title V.
3. Rationale in Support of Interim
Biomass Deferral
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a. Regulation at This Time Is Not
Justified
Since finalizing the Tailoring Rule,
EPA has gathered additional
information concerning biomass
through the CFI and in response to the
proposal for this rule. The information
collected to this point underscores the
complexity and uncertainty associated
with accounting for biogenic emissions
of CO2 and indicates that at present
attempting to determine the net carbon
cycle impact of particular facilities
combusting particular types of biomass
feedstocks would require extensive
analysis and would therefore entail
extensive workload requirements by
many of the permitting authorities. In
contrast to other sources of GHG
emissions, these uncertainties and
complexities are exacerbated because of
the unique role and impact biogenic
sources of CO2 have in the carbon cycle.
Further, methodologies are not
sufficiently developed to assure that
various permitting authorities would be
able to perform the necessary
calculations reasonably and consistently
to determine the net atmospheric impact
in many, if not all, instances.
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The extensive workload requirements
required to understand the net biogenic
CO2 emissions from bioenergy facilities
and other sources of biogenic CO2
emissions, as part of the PSD and Title
V permit process, including specifically
how to measure and account for
biogenic CO2 emissions, would
unnecessarily strain the resources of the
affected permitting authorities and
result in delays in processing permits
for other applicants. Moreover, at
present, devoting these limited
permitting authority resources to
biomass sources would not be
productive in light of the possibility that
EPA may ultimately determine that the
utilization of some or all biomass
feedstocks for bioenergy has a negligible
(or de minimis), negative, or positive net
impact on the carbon cycle.
Therefore, the information EPA has
collected since promulgating the
Tailoring Rule indicates that it is
consistent with the rationale of the
Tailoring Rule for affected permitting
authorities to defer on a temporary basis
biogenic CO2 emissions from PSD and
Title V applicability. During this
deferral, EPA will conduct a detailed
examination of the science associated
with biogenic CO2 emissions from
stationary sources, which will include a
peer review by the SAB, and resolve
technical issues in order to account for
biogenic CO2 emissions in ways that are
scientifically sound and also
manageable in practice.
As noted previously, EPA based the
Tailoring Rule on the extreme
administrative burdens to permitting
authorities, and undue costs to sources,
that would result from a literal
application of the PSD and Title V 100/
250 tpy statutory thresholds, as of
January 2, 2011, when those
requirements first applied to GHGs. EPA
reasoned that, in accordance with the
Chevron analytical framework for
statutory construction, taking into
account the ‘‘absurd results’’ and
‘‘administrative necessity’’ lines of
cases, Congress did not intend that the
PSD and Title V requirements apply at
the 100/250 tpy statutory thresholds to
GHG-emitting sources as of January 2,
2011, but rather that those requirements
could be limited, at least initially,
through a phase-in approach, to higheremitting sources.
Just as the extensive workload of
processing permit applications from
sources below the Tailoring Rule
thresholds justified exempting those
sources at least from the initial steps in
the Tailoring Rule phase-in program, so
too the extensive workload associated
with analyzing and accounting for
biogenic CO2 emissions as part of
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processing permit applications from
biomass facilities justifies exempting
those sources for a period of time, in the
affected states, pending EPA’s
development of a consistent and
practical framework for determining net
carbon cycle impacts. The three-year
deferral EPA is finalizing in this action
is reasonable to allow time for the
development of the accounting
framework and subsequent rulemaking.
In effect, this deferral is a step back
from the Tailoring Rule’s approach but
the decision to defer the applicability of
PSD and Title V to biogenic CO2
emissions is nonetheless supported, in
part, on the same rationale as EPA used
to justify the Tailoring Rule’s phase-in
approach. This action constitutes a
refinement of the approach EPA has
taken to regulate GHG emissions from
stationary sources through a phased-in
approach, based on an evolving
understanding of the complexities,
uncertainties, and nuances associated
with biogenic emissions.
An alternative way to reduce the
permitting burden would be to apply
PSD and Title V to all facilities with
biogenic CO2 emissions that emit at or
above the Tailoring Rule thresholds, but
without making any effort to take into
account net carbon cycle impacts.
However, we believe that it is
conceivable that as a result of the
scientific examination of biogenic CO2
emissions, we could conclude that the
net carbon cycle impact for some
biomass feedstocks is trivial, negative,
or positive. Accordingly, this could
result in regulation of sources with
trivial or positive impacts on the net
carbon cycle, as previously discussed.
To avoid this outcome, given our
current state of knowledge, we believe
a case-by-case net carbon cycle impact
analysis would be required in the course
of reviewing each permit application.
This burden would be in addition to the
currently existing burden associated
with obtaining a PSD or Title V permit.
In light of the permitting burdens
assessed in the Tailoring Rule, adding to
that burden in many states would
frustrate the goals we sought to
accomplish in the Tailoring Rule to
ensure that the PSD and Title V
programs can be administered in each
state.
Furthermore, given the potential that
the utilization of at least some biomass
feedstocks may have a negligible impact
on the net carbon cycle, engaging in this
type of burdensome analysis may not be
an optimal use of the limited resources
of PSD and Title V permitting
authorities. The additional scientific
examination being undertaken by the
EPA could ultimately conclude that
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such resources could have been more
effectively utilized to target CO2
emissions that clearly have a
detrimental impact on the net carbon
cycle. Establishing a three-year deferral
period for biogenic CO2 emissions will
enable EPA to consider the results of the
detailed examination of the science of
these emissions and undertake a
rulemaking to determine the best way to
account for biogenic CO2 emissions
when determining PSD applicability.
Another important reason for the
three-year deferral period is to allow
sufficient time to consider the unique
characteristics and attributes of biogenic
CO2 feedstocks, as opposed to other
sources of GHG, using the results from
the detailed examination mentioned
previously, within both the state
permitting agencies and affected
facilities. While the interim BACT
guidance described previously will help
alleviate some of this burden before the
deferral becomes effective, we expect
that more and more diverse users of
biomass combustion or other biogenic
CO2 sources are likely to be affected
under step 2 of the Tailoring Rule
because, under step 2, these sources can
trigger permitting requirements based
solely on their GHG emissions with no
prerequisite requirement that they
otherwise trigger PSD or Title V
permitting requirements for a non-GHG
pollutant. We believe, absent the
deferral period and the completion of
EPA’s full analysis of the unique
technical issues associated with these
diverse facilities emitting biogenic CO2,
that it would be particularly challenging
for many of the permitting authorities
and facilities to process permits
involving these emissions. Also, as
described elsewhere in this preamble,
this interim deferral is intended to
temporarily exclude biogenic CO2
emissions from the definition of
‘‘subject to regulation,’’ as that term was
defined for purposes of the Tailoring
Rule, for a period of three years, while
EPA further considers, through notice
and comment rulemaking, the approach
to accounting for these emissions on a
permanent basis.
b. One-Step-at-a-Time Doctrine
EPA relied, in part, on the ‘‘one-stepat-a-time’’ doctrine, which authorizes
agencies to implement statutory
requirements a step at a time, in
finalizing the Tailoring Rule. 75 FR
31514, 31578 (June 3, 2010). As
described in the Tailoring Rule and
earlier in the preamble, the case law
recognizing the ‘‘one-step-at-a-time’’
doctrine, within the Chevron
framework, justifies an agency’s step-bystep approach under the following
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circumstances or conditions: (1) The
agency’s ability to comply with a
statutory directive depends on facts,
policies, or future events that are
uncertain; (2) the agency has estimated
the extent of its remaining obligation;
(3) the agency’s incremental actions are
structured in a manner that is
reasonable in light of the uncertainties;
and (4) the agency is on track to full
compliance with the statutory
requirements.
In the proposed rule, EPA stated in
footnote 13 that the ‘‘one-step-at-a-time’’
doctrine was not relevant to this
rulemaking. This statement was made
without explanation. One commenter
(EPA–HQ–OAR–2011–0083–0084)
stated ‘‘[b]ased on EPA’s statements in
the Tailoring Rule, which does rely on
the ‘one-step-at-a-time’ doctrine, it
appears that the doctrine would apply
equally well to EPA’s decision to delay
regulation of biogenic CO2 emissions
under the PSD and Title V programs.’’
For the reasons stated below, EPA now
agrees that, because of the complexity
and uncertainty of the science
associated with accounting for biogenic
sources of CO2, the interim deferral of
the PSD and Title V program for such
emissions would be a reasonable
exercise of the ‘‘one-step-at-a-time’’
doctrine.
First, as the DC Circuit stated in
National Association of Broadcasters v.
FCC, 740 F.2d 1190, 1210 (DC Cir. 1984)
(‘‘National Association of
Broadcasters’’), incremental agency
action is most readily justifiable
‘‘against a shifting background in which
facts, predictions, and policies are in
flux and in which an agency would be
paralyzed if all the necessary answers
had to be in before any action at all
could be taken.’’ Those circumstances
are present here, and so is the fact that
the task at hand is extraordinarily
demanding. As discussed previously,
EPA is in the process of conducting a
detailed examination of the science
associated with biogenic CO2 emissions
from stationary sources to better
understand their role on the carbon
cycle and to develop an accounting
framework for use by permitting
authorities and sources. This
examination will include discussion
with partners and scientists both inside
and outside the Federal government, as
well as engagement with the Science
Advisory Board, to consider technical
issues that the Agency must resolve in
order to account for biogenic CO2
emissions in ways that are scientifically
sound and also manageable in practice.
Second, as the Court stated in
National Association of Broadcasters,
‘‘the agency [should] ma[k]e some
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43497
estimation, based upon evolving
economic and technological conditions,
as to the nature and magnitude of the
problem it will have to confront when
it comes to [undertake the remaining
steps]’’ and that estimation must be
‘‘plausible and flow from the factual
record compiled.’’ Id. at 1210. Here,
EPA has done this by deferring the
applicability of PSD and Title V to
biogenic emissions of CO2 from
stationary sources for only as long as
necessary for EPA to complete the
needed scientific study of these
emissions, develop an accounting
framework, and as appropriate conduct
rulemaking specific to the unique nature
and characteristics of these emission
sources.
In order to explore the issues further
following the promulgation of the
Tailoring Rule, on July 15, 2010, EPA
solicited views from the public through
the CFI on approaches to accounting for
biogenic CO2 emissions, including
whether some or all of a source’s
biogenic CO2 emissions could be
discounted based on a determination
that they are canceled out by the CO2
absorption associated with growing the
fuel (75 FR 41173). Also, we solicited
information on the means to estimate
and measure CO2 emissions from a
variety of biogenic CO2 sources that
typically have not been part of emission
inventories (e.g., CO2 from landfills,
livestock management, and fermentation
processes), as well as information on
other biogenic sources that may be
affected but which were not identified
specifically in the CFI.
With promulgation of the Tailoring
Rule, we committed to issue technical
and policy guidance for permitting of
GHGs. Subsequently, the information
gathered from stakeholders in response
to the CFI provided diverse perspectives
on treatment of biogenic CO2 emissions
in pre-construction and operating
permit reviews, including many
requests to exclude, either partially or
wholly, biogenic CO2 sources from PSD
applicability determinations and BACT
analyses on the basis of Inventory
results and other considerations.
Third, again as the Court stated in
National Association of Broadcasters, it
must be ‘‘reasonable, in the context of
the decisions made in the proceeding
under review, for the agency to have
deferred the issue to the future. With
respect to that question, postponement
will be most easily justified when an
agency acts against a background of
rapid technical and social change and
when the agency’s initial decision as a
practical matter is reversible should the
future proceedings yield drastically
unexpected results.’’ Id. at 1211. Here,
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our deferral is reasonable in light of the
technical and scientific questions that
are raised by biogenic emissions from
stationary sources, which will be
addressed by EPA’s ongoing study,
development of an accounting
framework, and any subsequent
rulemaking. As explained in the
proposal and elsewhere in the preamble
to this final rule, EPA believes it has the
authority to exclude biogenic CO2
emissions from the PSD and Title V
requirements for the proposed threeyear deferral period and will be
exploring whether a permanent
exemption is appropriate for at least
some and perhaps all types of
feedstocks.
However, the possibility also remains
that more detailed examination of the
science of biogenic CO2 will
demonstrate that the utilization of some
biomass feedstocks for bioenergy
production will have a significant
impact on the net carbon cycle, making
literal application of the PSD program
requirements to such emissions,
consistent with the Tailoring Rule,
necessary to fulfill congressional intent.
Thus, EPA is finalizing only a
temporary, rather than a permanent,
deferral of PSD requirements for such
sources at this time. EPA notes that the
issue of subsequent applicability of the
PSD and Title V programs to facilities
that may be permitted during the
deferral period is discussed in more
detail in section II.C.
Finally, as the DC Circuit stated in
Grand Canyon Air Tour Coalition v.
F.A.A., 154 F.3d 455, 477–78 (DC Cir.
1998), the Courts will accept an initial
step towards full compliance with a
statutory mandate, as long as the agency
is headed towards full compliance, and
we now believe that the doctrine is
applicable here.
As we have described in the CFI, the
preamble to the proposed deferral and
elsewhere in the preamble for this final
rule, there is little question as to the
complexity in accounting for and
understanding the impact of biogenic
CO2 emissions from stationary sources
on net atmospheric CO2 emissions such
that sources and permitting authorities
may not reasonably be expected to
comply with or implement PSD and
Title V applicability requirements in the
near term. As described elsewhere in
this preamble, the deferral is limited to
three years, and EPA may, before the
expiration of the deferral, undertake
additional rulemaking to clarify the
applicability of PSD and Title V
permitting requirements for specific
categories of biogenic emissions as may
be appropriate based on the scientific
record EPA is currently developing. See
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Grand Canyon Air Tour, 891 F.2d at
476–77 (upholding agency action as a
step towards full compliance with
statutory mandate when the agency
expected full compliance to occur some
20 years after the deadline in the
statute).
This rulemaking constitutes an initial
step toward full compliance, and, seen
in that light, is supported by the ‘‘onestep-at-a-time’’ doctrine.
beyond the words to the purpose of the
act where its literal terms lead to
‘absurd or futile results.’ ’’ Id. at 360 n.
89 (citations omitted).
To apply an exclusion based on the de
minimis doctrine, ‘‘the agency will bear
the burden of making the required
showing’’ that a matter is truly de
minimis which naturally will turn on
the assessment of particular
circumstances. Id. The Alabama Power
opinion concluded that ‘‘most
c. EPA Not Required to Regulate Where
regulatory statutes, including the CAA,
Benefits of Regulation Would Be Trivial permit such agency showings in
EPA believes it has the authority to
appropriate cases.’’ Id.
A notable limitation on the de
exclude biogenic CO2 emissions from
minimis doctrine is that it does not
the PSD and Title V requirements, if
scientific analysis supports conclusions authorize the agency to exclude
something on the basis of a cost-benefit
about the nature of biogenic CO2 in
analysis. As the court explained, this
question that in turn support such an
‘‘implied authority is not available for a
exclusion; the agency will be using the
situation where the regulatory function
three-year deferral period to better
does provide benefits, in the sense of
understand the science associated with
furthering the regulatory objectives, but
biogenic CO2 emissions and to explore
the agency concludes that the
whether or not a permanent exemption
acknowledged benefits are exceeded by
is permissible for at least some and
the costs.’’ Id. The court held that any
perhaps all types of feedstocks.
‘‘implied authority to make cost-benefit
Courts have recognized that
decisions must be based not on a
administrative agencies have the
general doctrine but on a fair reading of
implied authority to establish
the specific statute, its aims and
exemptions ‘‘when the burdens of
legislative history.’’ Id.
regulation yield a gain of trivial or no
Since Chevron, several courts have
value.’’ Alabama Power Co. v. Costle,
636 F.2d 323, 360 (DC Cir. 1980). In this recognized de minimis exceptions (1) so
long as they are not contrary to the
decision that specifically addressed the
express terms of the statute and (2) the
requirements of the PSD program, the
agency’s interpretation of the exception
DC Circuit described this principle as
is a permissible reading of the statute.
follows:
See e.g., Ober v. Whitman, 243 F.3d
Categorical exemptions may also be
1190 (9th Cir. 2001); see also Ohio v.
permissible as an exercise of agency power,
EPA, 997 F.2d 1520 (D.C. Cir. 1993).
inherent in most statutory schemes, to
The CAA is not so rigid as to preclude
overlook circumstances that in context may
a de minimis exception. Since the early
fairly be considered de minimis. It is
commonplace, of course, that the law does
years of the PSD program, EPA has
not concern itself with trifling matters, and
applied this de minimis principle to
this principle has often found application in
establish various types of values in the
the administrative context. Courts should be
PSD regulations that may be used to
reluctant to apply the literal terms of a statute
exempt categories of source from all or
to mandate pointless expenditures of effort.
part of the PSD program requirements.
Id. (internal citations omitted).
EPA also relied on the de minimis
In an earlier case cited by the court in
doctrine to establish values that
Alabama Power, the court described the permitting authorities can use to show
doctrine as follows:
that a source that requires a PSD permit
The ‘de minimis’ doctrine that was
meets the necessary criteria to obtain a
developed to prevent trivial items from
permit. Significant impact levels may be
draining the time of the courts has room for
used in particular ways identified in
sound application to administration by the
prior EPA rules and guidance as part of
Government of its regulatory programs.
an assessment of whether a source
* * * The ability, which we describe here,
causes or contributes to a violation of air
to exempt de minimis situations from a
statutory command is not an ability to depart quality standards. Significant
from the statute, but rather a tool to be used
monitoring concentrations may be used
in implementing the legislative design.
to exempt sources from pre-construction
District of Columbia v. Orleans, 406 F.2d 957, monitoring requirements. See 75 FR
959 (1968).
64864, 64890–97 (October 20, 2010).
Due to the complexity and
In this respect, the Alabama Power
uncertainty of the science associated
opinion observed in a footnote that the
de minimis principle ‘‘is a cousin of the with accounting for biogenic CO2
doctrine that, notwithstanding the ‘plain emissions and their impact on the
meaning’ of a statute, a court must look
carbon cycle and net atmospheric CO2
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levels, requiring regulation of biogenic
sources of CO2 at this time may lead to
only trivial environmental benefits
while exacerbating the regulatory
burdens and absurd results the Tailoring
Rule was intended to avoid because the
subsequent scientific study may show
that certain biogenic feedstocks have a
trivial or even positive impact on net
atmospheric CO2 levels.
d. Potential for Some Biomass
Feedstocks To Have a de minimis,
Neutral or Positive Impact on Net CO2
Levels in the Atmosphere
As discussed previously in this
preamble, EPA believes based on
information currently before the Agency
that at least some biomass feedstocks
that may be utilized to produce energy
or other products have a negligible
impact on the net carbon cycle, or
possibly even a positive net effect.
Within the context of the PSD and Title
V programs, the argument for treating
CO2 emissions from bioenergy and
biogenic sources differently from fossilbased CO2 emissions at the facility relies
on the premise that sequestration occurs
offsite, outside the boundaries of the
facility. Such a negligible or positive
impact on the carbon cycle and net
atmospheric CO2 levels should not
count towards the PSD and Title V
applicability requirements. It appears
that the potential may exist for EPA to
determine that other types of biomass
feedstocks would have a negligible
impact on the net carbon cycle impact
after further detailed examination of the
science associated with biogenic CO2
emissions.
Thus, if EPA were to require all
bioenergy facilities or other sources of
biogenic CO2 emissions to limit
emissions of CO2 before this assessment
is complete, it may later determine that
such actions have required regulation of
a trivial amount of emissions or even
potentially of emissions that are
associated with a net CO2 emissions
benefit. To avoid this outcome, and
because of the scientific uncertainty and
administrative burdens associated with
accounting for net biogenic CO2
emissions relative to the carbon cycle,
EPA believes an initial deferral of the
PSD requirements for bioenergy and
other biogenic sources is justified at this
time to conduct the detailed scientific
evaluation described elsewhere in the
preamble. However, the possibility also
remains that EPA’s detailed
examination of the science of biogenic
CO2 will demonstrate that the
utilization of some biomass feedstocks
for bioenergy production will have a
significant impact on the net carbon
cycle, making application of the PSD
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program requirements to such emissions
necessary to fulfill congressional intent.
Thus, EPA is finalizing only a
temporary, rather than a permanent,
deferral of PSD requirements at this
time in order for EPA to conduct a study
of the science surrounding biogenic CO2
emissions and their role in the carbon
cycle and to develop an accounting
framework to help further relieve the
burdens faced by permitting authorities.
EPA is also seeking an independent peer
review of the science and accounting
framework by the Science Advisory
Board to resolve the uncertainties that
have been highlighted by commenters in
response to the CFI and the proposal to
this action.
C. Facilities Permitted During Deferral
The final rule is an interim deferral
for biogenic CO2 emissions only and
does not relieve sources of the
obligation to meet the PSD and Title V
permitting requirements for other
pollutant emissions that are otherwise
applicable to the source during the
deferral period or that may be
applicable to the source at a future date
pending the results of EPA’s study and
subsequent rulemaking action.
This means, for example, that if the
deferral is applicable to biogenic CO2
emissions from a particular source
during the three-year effective period
and the study and future rulemaking do
not provide for a permanent exemption
from PSD and Title V permitting
requirements for the biogenic CO2
emissions from a source with particular
characteristics, then the deferral would
end for that type of source and its
biogenic CO2 emissions would have to
be appropriately considered in any
applicability determinations that the
source may need to conduct for future
stationary source permitting purposes,
consistent with that subsequent
rulemaking and the Final Tailoring Rule
(e.g., a major source determination for
Title V purposes or a major modification
determination for PSD purposes).
EPA also wishes to clarify that we did
not propose and this rule does not
require that a PSD permit issued during
the deferral period be amended or that
any PSD requirements in a PSD permit
existing at the time the deferral takes
effect, such as BACT limitations, be
revised or removed from an effective
PSD permit for any reason related to the
deferral or when the deferral period
expires.
Section 52.21(w) requires that any
PSD permit shall remain in effect,
unless and until it expires or it is
rescinded, under the limited conditions
specified in that provision. Also note
that we did not specifically propose or
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make final any change to these
rescission provisions, nor were they
addressed to any extent in the proposal.
Thus, a PSD permit that is issued to a
source while the deferral was effective
need not be reopened or amended if the
source is no longer eligible to exclude
its biogenic CO2 emissions from PSD
applicability after the deferral expires.
However, if such a source undertakes a
modification that could potentially
require a PSD permit and the source is
not eligible to continue excluding its
biogenic CO2 emissions after the
deferral expires, the source will need to
consider its biogenic CO2 emissions in
assessing whether it needs a PSD permit
to authorize the modification. With
respect to Title V, a source that becomes
a major source subject to an approved
Title V permit program as a result of
biogenic emissions after the deferral
expires would generally have one year
from the date the source became subject
to Title V to apply for an operating
permit.
Any future actions to modify, shorten,
or make permanent the deferral for
biogenic sources are beyond the scope
of this action and will be addressed
through subsequent rulemaking, based
on the scientific study and development
of an accounting framework described
elsewhere in this preamble. At this time,
the results of EPA’s review of the
science related to net atmospheric
impacts of biogenic CO2 and the
framework to properly account for such
emissions in Title V and PSD permitting
programs based on the study are
prospective and unknown. Thus, we are
unable to predict which biogenic CO2
sources, if any, currently subject to the
deferral would be subject to any
permanent exemptions or which
currently deferred sources would be
potentially required to account for their
emissions in the future rulemaking EPA
has committed to undertake for such
purposes in three or fewer years. Only
in that rulemaking can EPA address the
question of extending the deferral or
putting in place requirements that
would have the equivalent effect on
sources covered by this deferral.
To the extent the deferral is not
effective in a particular state at the time
a PSD permit is issued, then the permit
would need to include BACT
limitations for GHGs if the source emits
above levels that make GHGs subject to
regulation under applicable rules. EPA
issued interim guidance entitled,
‘‘Guidance for Determining Best
Available Control Technology for
Reducing Carbon Dioxide Emissions
from Bioenergy Production’’ to help
permitting authorities, during the
interim period before the deferral is
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effective, establish a basis for
concluding that under PSD Programs
the combustion of biomass fuels can be
considered BACT for biogenic CO2
emissions at stationary sources. To be
clear, this guidance would apply during
the deferral period for those permitting
authorities where the deferral was not
effective until EPA revises it or it is
superseded by future guidance or rules.
D. Mechanism for Deferral and State
Implementation
Consistent with the proposed rule,
EPA is implementing the deferral by
amending the definition of ‘‘subject to
regulation’’ in its PSD and Title V
regulations. The adoption of the deferral
for biogenic CO2 emissions from Title V
and PSD permitting programs under 40
CFR part 70 and 40 CFR 51.166 is
optional for any state, local, or tribal
(state) permitting authority, but is
effective immediately upon publication
for Title V and PSD permitting programs
under 40 CFR part 71 and 40 CFR 52.21
that EPA implements.
The proposal did not specifically
require each state to revise its PSD and
Title V permitting programs (required
under parts 51.166 and 70) to impose
the deferral for three years, although it
was clear that the proposal was
intended to revise the permitting
programs that EPA implements
(required under parts 52.21 and part 71)
for this purpose, and it was clear that
EPA intended to implement the deferral
by changing its implementing
regulations. Many state commenters on
the proposal seemed to assume that the
deferral was mandatory for the states
and questioned how they would revise
their SIPs and Title V programs by July
1, 2011, as they read EPA’s proposal to
require.
For the purposes of this final rule,
EPA is clarifying that each state may
decide if it wishes to adopt the deferral
and proceed accordingly, with
appropriate program changes, if needed.
Also, EPA suggests that each state
communicate with its stationary sources
its intent in this regard. Because the
deferral is not required, states that do
not wish to revise their current permit
programs do not need to make any
program changes in response to this
final rule. Also, states that do wish to
adopt the deferral do not need to make
any changes that would otherwise be
necessary by July 1, 2011, the start of
step 2 under the Tailoring Rule.
Although the preamble for the proposal
did discuss the beginning of step 2 of
the Tailoring Rule as a time when more
sources would be subject to permitting,
because sources could be subject to Title
V without a prerequisite that they also
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be subject to PSD and because they
could be subject to PSD for GHGs
without being subject first for another
regulated NSR pollutant, it did not
discuss any requirement for any state
deferral to be effective by July 1, 2011,
and we are not requiring this in this
final rule.
However, although state program
changes are not required under today’s
final rule, EPA sees several reasons that
a state should adopt the deferral in its
state programs and, based on comments
received, EPA expects that many states
will adopt the deferral. Many of these
reasons are the same reasons prompting
EPA to adopt the deferral for the permit
programs we implement. That is, states
that expect to receive permit
applications from a number of biomass
facilities, and, in particular, a number of
different types of biomass facilities, are
likely to need more time to determine
how best to address technical, scientific,
and practical issues related to biogenic
CO2 without disrupting the proper
functioning and timeliness of the
permitting programs. Of course, it is at
least in theory possible that such a state
may, on its own, be able to address
those issues, or may for other reasons
have adequate resources to address
those issues. Even so, we expect that
many states will need to, and therefore
should, adopt the deferral, and
therefore, like the proposal, this final
rule strongly encourages states that wish
to adopt the three-year deferral to
submit SIP revisions or Title V program
revisions. However, like the proposal,
this final rule does not mandate such
submittals, recognizing that some states
may not have any (or may have only a
few) sources that combust biomass, and
may have adequate information and
resources regarding the nature of
biogenic emissions from those sources,
or may for other reasons be able to
conduct permitting of bioenergy sources
without straining their permitting
resources.
Furthermore, the justification that
supports this deferral for including
biogenic CO2 in PSD applicability
determinations is not applicable in the
case of a PSD permit that was issued
before completion of this rule during
step 1 of the phase in of GHG
requirements under the Tailoring Rule.
If a permit has been issued, then the
burden described above has already
been experienced and overcome by the
permitting authority. Furthermore, this
burden will have been experienced in
the context of step 1 of the GHG
permitting phase under the Tailoring
Rule, and thus was easier to
accommodate as part of the more
limited increase in workload that
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permitting authorities have faced in
addressing GHG requirements during
step 1. In the context of step 2 where
permitting authorities will have to
process a greater number of permit
applications, the incremental burden of
evaluating the net atmospheric impacts
of biogenic CO2 has a more significant
impact on the ability of permitting
authorities to administer the permitting
programs. This analysis adds a burden
that EPA had not considered when it
completed the Tailoring Rule.
EPA also issued interim guidance
entitled, ‘‘Guidance for Determining
Best Available Control Technology for
Reducing Carbon Dioxide Emissions
from Bioenergy Production’’ to help
permitting authorities establish a basis
for concluding that under the PSD
Program the combustion of biomass
fuels can be considered BACT for
biogenic CO2 emissions at stationary
sources until such time as the deferral
becomes effective. EPA wishes to clarify
that the guidance is non-binding and
case-by-case BACT determinations
made in accordance with the guidance
may nonetheless be subject to challenge
in each permitting action. Accordingly,
the interim guidance does not provide
the same level of certainty to sources
and decrease in administrative burdens
to permitting authorities and sources
that the deferral does.
EPA developed the interim BACT
guidance primarily for application
during step 1 of the phase of GHG
permitting requirements under the
Tailoring Rule. While the guidance
suggests reasoning that may serve to
reduce the resource demands of
conducting a net carbon cycle analysis
in the context of permitting, it does not
eliminate the need for permitting
authorities to conduct some evaluation
of energy, environmental, and economic
impacts in step 4 of the BACT analysis.
The guidance discusses the
complexities of conducting a net carbon
cycle analysis, but places the emphasis
on showing the economic and energy
benefits of utilizing biomass. Permitting
authorities that apply this approach still
need to identify the specific energy and
economic benefits of utilizing particular
biomass feedstocks to apply this
rationale. To the extent these benefits
cannot be identified or shown to
override other considerations, a
permitting authority may need to
explore the net carbon cycle impact in
more depth to justify the conclusion
that utilization of a biomass feedstock is
BACT by itself. In states that do not
elect to adopt the deferral, the
incremental burden of conducting the
analysis described in the guidance will
have a more significant impact on the
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overall ability to administrate the
permitting program in the context of
step 2 of the GHG permitting than it did
in step 1, in which the overall increase
in workload from incorporating GHG
requirements into PSD permit reviews
was less than it will be in step 2.
This deferral may not be effective in
any jurisdiction before EPA publishes a
final rule and it takes effect. Also, for
any state that found it necessary to
revise its permitting programs to
implement the Final Tailoring Rule,
EPA believes it unlikely that such a
state would be able to implement the
deferral under its state rules without
making additional changes to its
program consistent with the regulatory
changes in this final rule. For any state
that was able to implement the Final
Tailoring Rule through interpretation of
the term ‘‘subject to regulation’’,
consistent with the Final Tailoring Rule,
without making any changes to state
regulations, EPA believes it is likely
they would be able to implement the
deferral under their state rules without
making additional revisions. In either of
these cases, EPA recommends that states
communicate with the stationary
sources under their jurisdiction
regarding whether they intend to adopt
the deferral, and if they do, when it will
become effective.
III. Response to Public Comments
A. Overview of Public Comments
We received a significant number of
public comments on the proposed
deferral. Some of these comments
covered issues such as:
• Content of the Deferral (e.g., pollutants
and sources covered, start and end date,
terminology);
• Implementation of the Deferral; and
• Legal Authority.
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While those comments addressed the
deferral itself, a large number of the
comments actually raised issues outside
the scope of this rulemaking and
covered topics such as:
• Science, accounting, and economic
issues related to biogenic CO2 emissions (e.g.,
carbon cycle dynamics, accounting
methodologies, forest economics and
sustainability);
• PSD, Title V and the Tailoring Rule; and
• The Interim Guidance, ‘‘Guidance For
Determining Best Available Control
Technology for Reducing Carbon Dioxide
Emissions From Bioenergy Production’’
(March 21, 2011).
EPA acknowledges those comments
that are outside the scope of this
rulemaking and notes that many of the
issues raised were similar, if not
identical, to those presented in
comments to the CFI last year. We will
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be considering those topics as part of
the detailed examination of the science
and technical issues associated with
accounting for biogenic CO2 emissions
from stationary sources. We also may
consider the issues in any subsequent
rulemakings we undertake related to the
PSD, Title V and other stationary source
programs. However, we do not respond
to them in this rulemaking.
The sections below contain a brief
summary of the some of the major
comments and responses we received
on the proposal. Responses to the
substantive comments can be found in
the response to comments document
entitled, ‘‘Deferral for CO2 Emissions
from Bioenergy and Other Biogenic
Sources under the Prevention of
Significant Deterioration (PSD) and Title
V Programs, Summary of Public
Comments and Responses,’’ available in
docket EPA–HQ–OAR–2011–0083.
B. Comments on the Deferral
We received comments on different
aspects of the deferral. They fit into
several broad categories as discussed
below.
Terminology. We received several
comments requesting clarity on the
terminology in the deferral, including
the terms biogenic CO2 emissions,
biologically-based material and
examples of the types of sources that
these emissions can come from. As
discussed in section II, we finalized the
terms biogenic CO2 emissions
(described as, emissions of CO2 from a
stationary source directly resulting from
the combustion or decomposition of
biologically-based materials other than
fossil fuels and mineral sources of
carbon (e.g. calcium carbonate)) and
biologically-based material (nonfossilized and biodegradable organic
material originating from plants,
animals or micro-organisms [including
products, by-products, residues and
waste from agriculture, forestry and
related industries as well as the nonfossilized and biodegradable organic
fractions of industrial and municipal
wastes, including gases and liquids
recovered from the decomposition of
non-fossilized and biodegradable
organic material]) with very little
change. We added the clause about
‘‘mineral sources’’ of carbon to biogenic
CO2 emissions in response to requests
for additional clarification on which
sources of CO2 were not included in the
deferral. We also clarified that in the
examples of sources of biogenic CO2
emissions, CO2 from fermentation
includes CO2 from ethanol production
as well as other industrial processes.
Pollutants. We received comments on
which pollutants are covered by the
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deferral, particularly methane (CH4) and
nitrous oxide (N2O). A few comments
requested that CH4 and N2O also be
included in the deferral as they result
when biomass is combusted. While CH4
and N2O are produced when biomass is
combusted, the level of emissions and
resulting impact on atmospheric
concentrations of these gases are
primarily related to the feedstock
handling and combustion conditions at
the specific plant rather than the source
of the feedstocks. We finalized this rule
as proposed and included only biogenic
CO2 emissions for this reason, and note
that emissions of non-CO2 GHGs are
typically a small proportion of the total
GHG emissions from combustion of
biologically based material. Since the
non-CO2 GHGs are so small relative to
CO2, the deferral of biogenic CO2
emissions will ensure the biomass
combustion projects will likely not meet
the applicability thresholds based on
their CH4 and N2O emissions alone.
Duration. We received several
comments on the duration of the
deferral, including its start date and end
date. Specifically, several comments
recommended that EPA remove the
three-year sunset date and make the
deferral permanent until the Agency
completes its study and takes further
action. Others concluded EPA does not
need three years to complete its work
and should shorten the deferral.
EPA is conducting a detailed
examination of the science and
technical issues associated with
biogenic CO2 emissions and is
developing an accounting framework.
Once that work is complete, the Agency
intends to undertake a notice-andcomment rulemaking to establish the
treatment of these emissions in the PSD
and Title V programs. We have
determined that three years will be
required to complete the scientific work
as well as the follow-on rulemaking. As
stated in section II of this preamble, the
deferral is intended to be a temporary
measure to allow the Agency time to
complete its work and determine what,
if any, treatment of biogenic CO2
emissions should be in the PSD and
Title V programs. Therefore, we did not
agree to make the deferral permanent or
to shorten it.
Sources covered by and permitted
during the deferral. We received several
comments requesting clarity on which
sources of biogenic CO2 emissions were
covered by the deferral. This is related
to the comments on definitions
described above, and we provided
clarity on those sources, where
necessary. We also received several
comments on the application of the PSD
and Title V programs during the
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deferral, including the availability of
grandfathering or a permitting
moratorium for sources subject to the
deferral and on the availability of
authority to revise BACT.
The final rule is an interim deferral
for biogenic CO2 emissions only and
does not relieve sources of the
obligation to meet the PSD and Title V
permitting requirements for other
pollutant emissions that are otherwise
applicable to the source during the
deferral period or that may be
applicable to the source at a future date
pending the results of EPA’s study and
subsequent rulemaking action. At this
time, we are unable to predict which
biogenic CO2 sources, if any, currently
subject to the deferral would be subject
to any permanent exemptions or which
currently deferred sources would be
potentially required to account for their
emissions in relation to future
permitting actions as a result of the
future rulemaking EPA has committed
to undertake for such purposes in three
or fewer years. Only in that rulemaking
can EPA address the question of
extending the deferral or putting in
place requirements that would have the
equivalent effect on sources covered by
this deferral.
This means, for example, that if the
deferral is applicable to biogenic CO2
emissions from a particular source
during the three-year effective period
and the study and future rulemaking do
not provide for a permanent exemption
from the PSD and Title V permitting
requirements for the biogenic CO2
emissions from a source with particular
characteristics, then the deferral would
end for that source and those biogenic
CO2 emissions would have to be
appropriately considered in any
applicability determinations that the
source may need to conduct for future
stationary source permitting purposes,
consistent with that subsequent
rulemaking and the Final Tailoring Rule
(e.g., a major source determination for
Title V purposes or a major modification
determination for PSD purposes).
Many commenters on the proposed
deferral asked EPA to provide
grandfathering from permitting
requirements for sources that are
currently not subject to permitting
requirements but that in the future may
be covered by the deferral. In addition,
some commenters asked for the deferral
to be made retroactively effective (e.g.,
during step 1 of the Tailoring Rule or
January 1, 2011 through June 30, 2011)
in states prior to state adoption of any
SIP revision or Title V program change
that may be necessary to revise the
programs to incorporate the deferral, or
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that the deferral permanently apply to
any source subject to it at any time.
As explained in section II.C of this
preamble, EPA has decided to not offer
any kind of grandfathering or
moratorium on future Title V and PSD
permitting for biogenic CO2 sources
subject to the three-year deferral.
EPA wishes to clarify that we did not
propose and this rule does not require
that a PSD permit issued during the
deferral period be amended or that any
PSD requirements in a PSD permit
existing at the time the deferral takes
effect, such as BACT limitations, be
revised or removed from an effective
PSD permit for any reason related to the
deferral or when the deferral period
expires.
Section 52.21(w) requires that any
PSD permit shall remain in effect,
unless and until it expires or it is
rescinded, under the limited conditions
specified in that provision. To the
extent the deferral is not effective in a
particular state at the time a PSD permit
is issued, then the permit would need
to include BACT limitations for GHGs if
the source emits above levels that make
GHGs subject to regulation under
applicable rules.
Thus, a PSD permit that is issued to
a source while the deferral was effective
need not be reopened or amended if the
source is no longer eligible to exclude
its biogenic CO2 emissions from PSD
applicability after the deferral expires.
However, if such a source undertakes a
modification that could potentially
require a PSD permit and the source is
not eligible to continue excluding its
biogenic CO2 emissions after the
deferral expires, the source will need to
consider its biogenic CO2 emissions in
assessing whether it needs a PSD permit
to authorize the modification.
Any future actions to modify, shorten,
or make permanent the deferral for
biogenic sources are beyond the scope
of this action and will be addressed
through subsequent rulemaking, based
on the scientific study and development
of an accounting framework described
elsewhere in this preamble.
Implementation of the Deferral. We
received comments suggesting that
adoption of the deferral must be
mandatory for states, as well as
comments saying that the states should
have flexibility regarding adoption of
the deferral. As explained in section II.
D of this preamble, EPA is not making
adoption of this deferral mandatory.
Each state may decide if it wishes to
adopt the deferral and proceed
accordingly, with appropriate program
changes, if needed. Based on the
comments received, we recognize that
some states may not have any, or may
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have only a few, sources that combust
biomass, and may have adequate
information and resources as to the
nature of biogenic emissions from those
sources. That said, EPA recommends
that each state communicate with its
stationary sources its intent in this
regard and utilize the interim guidance
document as appropriate.
Even though adoption of the deferral
is not mandatory, EPA sees several
reasons why a state might want to adopt
the deferral in its state programs and
many of these reasons are the same
reasons why EPA is adopting the
deferral for the permit programs we
implement (e.g., the need for more time
to determine how to address technical,
scientific, and practical issues related to
biogenic CO2 without disrupting the
proper functioning and timeliness of the
permitting programs).
However, although state program
changes are not required under today’s
final rule, EPA sees several reasons that
a state might want to adopt the deferral
in its state programs; many of these
reasons are the same reasons prompting
EPA to adopt the deferral for the permit
programs we implement (e.g., the need
for more time to determine how best to
address technical, scientific, and
practical issues related to biogenic CO2
without disrupting the proper
functioning and timeliness of the
permitting programs). Also, like the
proposal, this final rule strongly
encourages states that wish to adopt the
three-year deferral to submit SIP
revisions or Title V program revisions,
but does not mandate such submittals,
recognizing that some states may not
have any (or may have only a few)
sources that combust biomass, and may
have adequate information and
resources regarding the nature of
biogenic emissions from those sources.
Furthermore, the justification that
supports this deferral for including
biogenic CO2 in PSD applicability
determinations is not applicable in the
case of a PSD permit that was issued
before completion of this rule during
step 1 of the phase-in of GHG
requirements under the Tailoring Rule.
If a permit has been issued, then the
burden described above has already
been experienced and overcome by the
permitting authority. Furthermore, this
burden will have been experienced in
the context of step 1 of the GHG
permitting phase in under the Tailoring
Rule, and thus was easier to
accommodate as part of the more
limited increase in workload that
permitting authorities have faced in
addressing GHG requirements during
step 1. In the context of step 2 where
permitting authorities will have to
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process a greater number of permit
applications, the incremental burden of
evaluating the net atmospheric impacts
of biogenic CO2 has a more significant
impact on the ability of permitting
authorities to administer the permitting
programs. This analysis adds a burden
that EPA had not considered when it
completed the Tailoring Rule.
As explained in section II.C of the
preamble, EPA also issued interim
guidance entitled, ‘‘Guidance for
Determining Best Available Control
Technology for Reducing Carbon
Dioxide Emissions from Bioenergy
Production’’ to help permitting
authorities establish a basis for
concluding that under PSD Program the
combustion of biomass fuels can be
considered BACT for biogenic CO2
emissions at stationary sources until
such time as the deferral becomes
effective. This guidance may continue to
assist permitting authorities where the
deferral is not effective during the
deferral period until EPA revises it or it
is superseded by future guidance or
rules. It should be noted that the
guidance is non-binding, and case-bycase BACT determinations made in
accordance with the guidance may
nonetheless be subject to challenge in
each permitting action. Accordingly, the
interim guidance does not provide the
same level of certainty to sources and
decrease in administrative burdens to
permitting authorities and sources that
the deferral does.
EPA developed the interim BACT
guidance primarily for application
during step 1 of the phase-in of GHG
permitting requirements under the
Tailoring Rule. While the guidance
suggests reasoning that may serve to
reduce the resource demands of
conducting a net carbon cycle analysis
in the context of permitting, it does not
eliminate the need for permitting
authorities to conduct some evaluation
of energy, environmental, and economic
impacts in step 4 of the BACT analysis.
The guidance discusses the
complexities of conducting a net carbon
cycle analysis, but places the emphasis
on showing the economic and energy
benefits of utilizing biomass. Permitting
authorities that apply this approach still
need to identify the specific energy and
economic benefits of utilizing particular
biomass feedstocks to apply this
rationale. To the extent these benefits
cannot be identified or shown to
override other considerations, a
permitting authority may need to
explore the net carbon cycle impact in
more depth to justify the conclusion
that utilization of a biomass feedstock is
BACT by itself. In states that do not
elect to adopt the deferral, the
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incremental burden of conducting the
analysis described in the guidance will
have a more significant impact on the
overall ability to administrate the
permitting program in the context of
step 2 of the GHG permitting than it did
in step 1, where the overall increase in
workload from incorporating GHG
requirements into PSD permit reviews
was less than it will be in step 2.
Legal Authority. We received several
comments on EPA’s legal authority to
issue the deferral. A number of
commenters expressed the view that
EPA lacked the scientific basis to defer
the applicability of PSD and Title V
permitting requirements to biogenic
emissions of CO2.
A number of commenters argued that
EPA had not demonstrated that the
deferral was necessary to avoid
administrative burden or impossibility,
and that the science surrounding CO2
emissions from biogenic sources and
their role in the carbon cycle is settled
enough to show that use of some or all
biogenic feedstocks and emissions do
have an impact on net atmospheric
concentrations of CO2, or are not de
minimis; therefore, these commenters
argued that such emissions should be
regulated under the PSD and Title V
permitting programs.
EPA disagrees with the commenters’
characterization of the state of the
science and administrative burdens
facing permitting agencies and sources
to account for biogenic sources of CO2
emissions as part of permitting actions.
EPA notes that it also received a number
of comments expressing the opposing
view that a permanent deferral or
exclusion was necessary because
biogenic emissions of CO2 do not have
an impact on atmospheric
concentrations of CO2, or that use of
certain categories of feedstock do not
have such an impact. EPA also received
comments from a number of permitting
authorities and sources expressing the
view that the science surrounding the
accounting of net atmospheric CO2
emissions from biogenic sources, given
the carbon cycle, warranted further
study and development of an
accounting framework to assist them
with their permitting actions.
EPA believes this diversity of views
reflects the complexity of the science
associated with accounting for biogenic
CO2 emissions as part of the PSD and
Title V permitting programs. EPA
agrees, based on information currently
before the Agency, including
information provided in response to the
CFI and the proposal for this rule, that
emissions from certain biomass
feedstocks may have a negligible effect
on atmospheric concentrations of CO2,
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but also believes based on the
complexity of this evidence that the
deferral to allow for further study is
warranted. In addition, EPA is
conducting an independent peer review
by the Science Advisory Board of the
science and accounting framework
associated with biogenic CO2 emissions,
which will benefit permitting
authorities.
While the interim BACT guidance
described elsewhere in the preamble
may help alleviate some of this
uncertainty and burden for permitting
authorities where the deferral is not
effective, we expect that more and more
diverse users of biomass combustion or
other biogenic CO2 sources are likely to
be affected under step 2 of the Tailoring
Rule because, under step 2, these
sources can trigger permitting
requirements based solely on their GHG
emissions with no prerequisite
requirement that they otherwise trigger
PSD or Title V permitting requirements
for a non-GHG pollutant. We believe,
absent the deferral period and the
completion of EPA’s full analysis of the
unique technical issues associated with
these diverse facilities emitting biogenic
CO2, it would be particularly
challenging for permitting authorities
and facilities to process permits
involving these emissions.
A number of commenters challenged
EPA’s authority to amend the regulatory
definition of ‘‘subject to regulation’’ to
exclude biogenic sources of CO2 from
regulation for three years under the
administrative law doctrines and
rationale articulated in the Tailoring
Rule and elsewhere in this preamble. A
number of commenters also expressed
the view that the deferral would lead to
significant development of the biomass
industry during the deferral period and
a permanent exclusion for these sources,
in contradiction to the CAA’s goal of
protecting air quality.
EPA disagrees with these
commenters’ characterization of the
legal authority and rationale in support
of this interim deferral. As described in
Section II.B. of this preamble, this
interim deferral is intended only to
temporarily exclude biogenic CO2
emissions from the definition of
‘‘subject to regulation,’’ as that term was
defined for purposes of the Tailoring
Rule, for a period of three years, while
EPA further considers, through notice
and comment rulemaking, the approach
to accounting for these emissions on a
permanent basis. In response to
commenters who speculate about the
likelihood of significant development of
the biomass industry or increases in the
number of sources emitting biogenic
CO2 during the deferral period, EPA
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notes that a decision to move forward
with development of a facility is based
on many economic and business factors,
not just permitting requirements, that
are beyond the scope of this final action.
This interim deferral represents a
permissible application of wellestablished administrative law
doctrines, necessitated by the scientific
uncertainty surrounding the accounting
of biogenic CO2 emissions, to develop a
regulatory scheme that implements the
CAA consistent with congressional
intent in a step-wise fashion designed to
minimize administrative burdens and
avoid premature regulation of sources of
air pollution whose biogenic CO2
emissions could be shown to have de
minimis impacts on a net carbon cycle
basis after EPA completes further
analysis. EPA notes that the issue of
subsequent applicability of the PSD and
Title V programs to facilities that may
be permitted during the deferral period
is addressed in sections II.C.
EPA’s establishment of this deferral is
permissible and, based upon the
information currently before the
Agency, narrowly tailored to effectuate
congressional intent. It appears that the
potential may exist for EPA to
determine that some other types of
biomass feedstocks would have a
negligible impact on the net carbon
cycle impact after further detailed
examination of the science associated
with biogenic CO2 emissions. Thus, if
EPA were to require all bioenergy
facilities to limit emissions of biogenic
CO2 before this assessment is complete,
it may later determine that such
emissions have trivial impact on the net
carbon cycle. To avoid this outcome,
and because of the administrative
burdens associated with accounting for
net biogenic CO2 emissions relative to
the carbon cycle, EPA believes an initial
deferral of the PSD requirements for
bioenergy and other biogenic sources to
allow for subsequent, phased-in
regulations is justified at this time.
However, the possibility also remains
that EPA’s detailed examination of the
science of biogenic CO2 will
demonstrate that the utilization of some
biomass feedstocks for bioenergy
production will have a significant
impact on the net carbon cycle, making
application of the PSD program
requirements to such emissions
necessary to fulfill congressional intent.
The extensive workload requirements
required to understand the net biogenic
CO2 emissions from bioenergy facilities
and other sources of biogenic CO2
emissions, as part of the PSD and Title
V permit process, including specifically
how to measure and account for
biogenic CO2 emissions, would
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unnecessarily strain the resources of
many permitting authorities and result
in delays in processing permits for other
applicants. Moreover, at present,
devoting these limited permitting
authority resources to biomass would
not be productive in light of the
previously described possibility that
EPA may ultimately determine that the
utilization of some or all biomass
feedstocks for bioenergy has a negligible
or de minimis impact on the net carbon
cycle.
EPA received a comment arguing that
the deferral was also supported under
the ‘‘one-step-at-a-time’’ doctrine, which
authorizes agencies to implement
statutory requirements a step at a time.
EPA also relied, in part, on this doctrine
in finalizing the Tailoring Rule. 75 FR
31514, 31578 (June 3, 2010).
In the proposed rule, EPA stated in
footnote 13 that the ‘‘one-step-at-a-time’’
doctrine was not relevant to this
rulemaking. This statement was made
without explanation. The commenter
stated ‘‘[b]ased on EPA’s statements in
the Tailoring Rule, which does rely on
the ‘one-step-at-a-time’ doctrine, it
appears that the doctrine would apply
equally well to EPA’s decision to delay
regulation of biogenic CO2 emissions
under the PSD and Title V programs.’’
As explained in more detail elsewhere
in the preamble, EPA now agrees that
because of the complexity and
uncertainty of the science associated
with accounting for biogenic sources of
CO2 that the interim deferral of the PSD
and Title V program for such emissions
would be a reasonable exercise of the
‘‘one-step-at-a-time’’ doctrine.
This rulemaking constitutes an initial
step toward full compliance, and, seen
in that light, is supported by the ‘‘onestep-at-a-time’’ doctrine. Even if the
doctrine were found to apply only when
an agency is committed to fully
implementing statutory requirements
according to their literal terms, we
believe that the interim deferral
promulgated in this final rule would be
considered valid under the one-step-ata-time doctrine.
EPA received a number of comments
in favor of expanding the deferral to
CO2e or other GHGs, not just CO2. EPA
disagrees with the commenters seeking
expansion of the deferral to CO2e. As
explained elsewhere in the preamble,
while CH4 and N2O are produced when
biomass is combusted, the level of
emissions and resulting impact on
atmospheric concentrations of these
gases are primarily related to the
feedstock handling and combustion
conditions at the specific plant rather
than the source of the feedstocks. We
finalized this rule as proposed and
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included only biogenic CO2 emissions
for this reason, and note that emissions
of non-CO2 GHG are typically a small
proportion of the total GHG emissions
from combustion of biologically based
material. Since the non-CO2 GHG are so
small relative to CO2, the deferral of
biogenic CO2 emissions will ensure the
biomass combustion projects will likely
not meet the applicability thresholds on
their CH4 and N2O emissions alone.
Subsequent regulations to establish
treatment of specific sources of biogenic
emissions under the PSD and Title V
programs are beyond the scope of this
action.
C. Comments on Science, Accounting,
and Economic Issues
As noted above, we received a large
number of comments that provided the
same or similar information to the
comments received through the CFI last
year. Those comments are summarized
briefly below and also contained in the
response to comments document. While
we did not respond to these comments
as they are outside the scope of this
rulemaking, we will consider many of
them during our ongoing work on
biogenic CO2 emissions.
Carbon cycle dynamics. We received
several comments on the net
atmospheric impact of biomass. Some
commenters supported the conclusion
that biomass has zero net atmospheric
impact based on the premise that
biomass is part of the natural carbon
cycle and does not add additional
carbon to the atmosphere. Conversely,
other commenters supported the
conclusion that biomass combustion
increases the atmospheric carbon load.
Issues raised by commenters, including
the time delays between sequestration
from and release to the atmosphere,
differences between feedstocks,
influences of different spatial scale, and
differences in combustion efficiencies,
are important in the development of
accounting methodologies and will be
considered during the scientific review
that will take place during the threeyear deferral period. EPA will consider
such issues in order to account for
biogenic CO2 emissions from stationary
sources in ways that are scientifically
sound and manageable in practice.
Accounting methodologies used by
other programs. We received several
comments discussing the accounting
methodologies used in international,
U.S. government (including U.S. EPA)
and state regulatory and policy
programs. The accounting approaches
taken by other programs, including
other EPA programs, will be considered
in EPA’s detailed examination of the
scientific and technical issues related to
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emissions at energy projects, while
others supported the inclusion of
biogenic fuels as BACT in the interim
guidance. As stated in the March 2011
interim guidance document, EPA has
not provided a final determination of
BACT for any particular source, since
such determinations can only be made
by individual permitting authorities on
a case-by-case basis after consideration
of the record in each case. Upon
consideration of the record in an
individual case, if a permitting authority
has a reasoned basis to address
particular issues in a different manner
than EPA recommends in the bioenergy
BACT guidance, they have the
discretion to do so. EPA is granting the
deferral of biogenic CO2 emissions from
stationary source permitting
requirements because the issue of
accounting for the net atmospheric
impact of biogenic CO2 emissions is
complex enough that further
consideration of this important issue is
warranted.
D. Comments on PSD, Title V and the
Tailoring Rule
We received some comments on the
PSD and Title V programs and how they
relate to the Tailoring Rule, including
comments about the need to adjust the
thresholds for GHG applicability,
facilities that should or should not be
covered, and the ultimate treatment of
biogenic CO2 in these programs. These
comments are contained in the response
to comments document. The dates,
thresholds and other requirements
established in the Tailoring Rule are not
a subject of this rulemaking and thus
these comments are outside the scope of
this action.
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biogenic CO2 emissions and any
subsequent rulemakings we undertake
during the deferral period.
Components of accounting
methodologies. We received several
comments highlighting the challenges
associated with different components of
biogenic CO2 emissions accounting
methodologies, including using
‘‘business-as-usual’’ (BAU) projections,
employing case-by-case analyses and
considering a feedstock-based
accounting approach. EPA will consider
these topics in our review of the
scientific and technical issues related to
accounting for biogenic CO2 emissions,
as well as in the subsequent rulemaking
to establish the treatment of these
emissions in the PSD and Title V
programs.
Forest economics and sustainability.
We received some comments supporting
forest biomass as an energy feedstock
and discussing the role of bioenergy
markets in sustaining forest
conservation. EPA thanks the
commenters for these comments and
considers these views beyond the scope
of this deferral action.
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
E. Comments on the Interim Guidance
We received some comments on the
interim guidance document released in
March 2011 designed to help permitting
authorities establish a basis for
concluding that under PSD and Title V
Programs the combustion of biomass
fuels can be considered BACT for
biogenic CO2 emissions at stationary
sources before the deferral becomes
effective. These comments are contained
in the response to comments document
and are briefly summarized below.
While these comments are outside the
scope of this rulemaking, we will likely
be considering many of them during our
ongoing work on biogenic CO2
emissions.
Some commenters asserted that
biogenic fuels should not be considered
BACT for controlling biogenic CO2
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IV. Statutory and Executive Order
Review
This action is not a ‘‘significant
regulatory action’’ under the terms of
Executive Order 12866 (58 FR 51735,
October 4, 1993) and is therefore not
subject to review under Executive
Orders 12866 and 13563 (76 FR 3821,
January 21, 2011).
B. Paperwork Reduction Act
This action does not impose any new
information collection burden. Instead,
this action will reduce costs incurred by
any facility with biogenic CO2
emissions, as well as permitting
authorities, relative to the costs that
would be incurred if EPA did not revise
the rule.
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid OMB
control number. The OMB has
previously approved the information
collection requirements contained in the
existing regulations for PSD (see, e.g., 40
CFR 52.21) and Title V (see 40 CFR
parts 70 and 71) under the provisions of
the Paperwork Reduction Act, 44 U.S.C.
3501 et seq. and has assigned OMB
control number 2060–0003 and OMB
control number 2060–0336. The OMB
control numbers for EPA’s regulations
in 40 CFR are listed in 40 CFR part 9.
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C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute, unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of this action on small entities, small
entity is defined as: (1) A small business
as defined by the Small Business
Administration’s regulations at 13 CFR
121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise that is independently owned
and operated and is not dominant in its
field.
After considering the economic
impacts of this final action on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
In determining whether a rule has a
significant economic impact on a
substantial number of small entities, the
impact of concern is any significant
adverse economic impact on small
entities, since the primary purpose of
the regulatory flexibility analyses is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the rule
on small entities.’’ 5 U.S.C. 603 and 604.
Thus, an agency may certify that a rule
will not have a significant economic
impact on a substantial number of small
entities if the rule relieves regulatory
burden, or otherwise has a positive
economic effect on all of the small
entities subject to the rule.
We believe that this final rule will
relieve the necessary analysis and
corresponding workload requirements
for most affected facilities, including
small businesses, subject to the PSD and
Title V programs. As a result, the
program changes provided in this rule
are not expected to result in a
significant economic impact on a
substantial number of small entities. In
addition, EPA determined that the final
rulemaking would not have a significant
impact on small governmental
jurisdictions. The EPA has therefore
concluded that this final action will not
have a significant economic impact on
a substantial number of small entities.
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D. Unfunded Mandates Reform Act
(UMRA)
permits; however, this may change in
the future.
This final rule does not contain a
Federal mandate that may result in
expenditures of $100 million or more
for state, local, and tribal governments,
in the aggregate, or the private sector in
any one year. Only those few states
whose permitting authorities do not
implement the Federal PSD and Title V
rules by reference in their SIPs will have
a small increase in burden. If those
states choose to adopt this deferral, they
will have to amend their corresponding
SIPs to incorporate the amendments
from today’s action, as the deferral that
we finalized will not otherwise apply to
the PSD and Title V programs. Thus,
this rule is not subject to the
requirements of sections 202 or 205 of
the UMRA.
This rule is also not subject to the
requirements of section 203 of UMRA
because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. As
discussed earlier, this rule is expected
to result in an administrative burden
reduction for all affected permitting
authorities and permittees, including
small governments.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
The EPA interprets Executive Order
13045 (62 FR 19885, April 23, 1997) as
applying only to those regulatory
actions that concern health or safety
risks, such that the analysis required
under section 5–501 of the EO has the
potential to influence the regulation.
This action is not subject to Executive
Order 13045 because it does not
establish an environmental standard
intended to mitigate health or safety
risks.
E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects 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, as specified in EO
13132. These amendments will simplify
and reduce the burden of implementing
the PSD and Title V operating permit
programs, by deferral of PSD and Title
V application requirements to biogenic
CO2 emissions at a facility. Thus, EO
13132 does not apply to this action.
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (59 FR
22951, November 6, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
Tribal officials in the development of
regulatory policies that have Tribal
implications.’’
The EPA has concluded that this final
rule may have Tribal implications.
However, it will neither impose
substantial direct compliance costs on
Tribal government, nor preempt Tribal
law. There are no Tribal authorities
currently issuing PSD and Title V
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H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not a ‘‘significant
energy action’’ as defined in EO 13211
(66 FR 28355, May 22, 2001) because it
is not likely to have a significant
adverse effect on the supply,
distribution, or use of energy. Further,
we have concluded that this rule is not
likely to have any adverse energy effects
because this action would not create any
new requirements for sources in the
energy supply, distribution, or use
sectors.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (NTTAA), Public Law 104–
113 (15 U.S.C. 272 note) directs EPA to
use voluntary consensus standards in its
regulatory activities unless to do so
would be inconsistent with applicable
law or otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standards bodies. The NTTAA directs
EPA to provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards.
This action does not involve technical
standards. Therefore, EPA is not
considering the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629,
February 16, 1994) establishes Federal
executive policy on environmental
justice. Its main provision directs
Federal agencies, to the greatest extent
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practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the U.S.
The EPA has determined that this rule
will not have disproportionately high
and adverse human health or
environmental effects on minority or
low-income populations because it does
not affect the level of protection
provided to human health or the
environment, as any impacts that it will
have will be global in nature and will
not affect local communities or
populations in a manner that adversely
affects the level of protection provided
to human health or the environment.
K. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996 (SBREFA),
generally provides that before a rule
may take effect, the agency
promulgating the rule must submit a
rule report, which includes a copy of
the rule, to each House of the Congress
and to the Comptroller General of the
United States. EPA will submit a report
containing this rule and other required
information to the U.S. Senate, the U.S.
House of Representatives, and the
Comptroller General of the U.S. prior to
publication of the rule in the Federal
Register. A major rule cannot take effect
until 60 days after it is published in the
Federal Register. This action is not a
‘‘major rule’’ as defined by 5 U.S.C.
804(2). This rule will be effective on
July 20, 2011.
List of Subjects
40 CFR Part 51
Environmental protection,
Administrative practice and procedure,
Air pollution control, Carbon dioxide,
Carbon dioxide equivalents, Greenhouse
gases, Incorporation by reference,
Intergovernmental relations, Methane,
Nitrous oxide.
40 CFR Part 52
Environmental protection,
Administrative practice and procedure,
Air pollution control, Carbon dioxide,
Carbon dioxide equivalents, Greenhouse
gases, Incorporation by reference,
Intergovernmental relations, Methane,
Nitrous oxide.
40 CFR Part 70
Environmental protection,
Administrative practice and procedure,
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Federal Register / Vol. 76, No. 139 / Wednesday, July 20, 2011 / Rules and Regulations
Air pollution control, Carbon dioxide,
Carbon dioxide equivalents, Greenhouse
gases, Intergovernmental relations,
Methane, Nitrous oxide.
PART 52—[AMENDED]
3. The authority citation for part 52
continues to read as follows:
■
Authority: 42 U.S.C. 7401, et seq.
40 CFR Part 71
Environmental protection,
Administrative practice and procedure,
Air pollution control, Carbon dioxide,
Carbon dioxide equivalents, Greenhouse
gases, Intergovernmental relations,
Methane, Nitrous oxide.
Dated: July 1, 2011.
Lisa P. Jackson,
Administrator.
PART 51—[AMENDED]
1. The authority citation for part 51
continues to read as follows:
■
Authority: 23 U.S.C. 101; 42 U.S.C. 7401–
7671q.
Subpart I—[Amended]
2. Section 51.166 is amended by
revising paragraph (b)(48)(ii)(a) to read
as follows:
■
§ 51.166 Prevention of significant
deterioration of air quality.
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*
*
*
*
*
(b) * * *
(48) * * *
(ii) * * *
(a) Multiplying the mass amount of
emissions (tpy), for each of the six
greenhouse gases in the pollutant GHGs,
by the gas’s associated global warming
potential published at Table A–1 to
subpart A of part 98 of this chapter—
Global Warming Potentials. For
purposes of this paragraph (b)(48)(ii)(a),
prior to July 21, 2014, the mass of the
greenhouse gas carbon dioxide shall not
include carbon dioxide emissions
resulting from the combustion or
decomposition of non-fossilized and
biodegradable organic material
originating from plants, animals, or
micro-organisms (including products,
by-products, residues and waste from
agriculture, forestry and related
industries as well as the non-fossilized
and biodegradable organic fractions of
industrial and municipal wastes,
including gases and liquids recovered
from the decomposition of nonfossilized and biodegradable organic
material).
*
*
*
*
*
18:41 Jul 19, 2011
4. Section 52.21 is amended by
revising paragraph (b)(49)(ii)(a) to read
as follows:
■
§ 52.21 Prevention of significant
deterioration of air quality.
*
For the reasons stated in the
preamble, Title 40, chapter I, of the
Code of Federal Regulations is amended
as follows:
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*
*
*
*
(b) * * *
(49) * * *
(ii) * * *
(a) Multiplying the mass amount of
emissions (tpy), for each of the six
greenhouse gases in the pollutant GHGs,
by the gas’s associated global warming
potential published at Table A–1 to
subpart A of part 98 of this chapter—
Global Warming Potentials. For
purposes of this paragraph, prior to July
21, 2014, the mass of the greenhouse gas
carbon dioxide shall not include carbon
dioxide emissions resulting from the
combustion or decomposition of nonfossilized and biodegradable organic
material originating from plants,
animals, or micro-organisms (including
products, by-products, residues and
waste from agriculture, forestry and
related industries as well as the nonfossilized and biodegradable organic
fractions of industrial and municipal
wastes, including gases and liquids
recovered from the decomposition of
non-fossilized and biodegradable
organic material).
*
*
*
*
*
PART 70—[AMENDED]
5. The authority citation for part 70
continues to read as follows:
■
Authority: 42 U.S.C. 7401, et seq.
6. Section 70.2 is amended by revising
paragraph (2) of the definition of
‘‘Subject to regulation’’ to read as
follows:
■
§ 70.2
*
Definitions.
*
*
*
*
Subject to Regulation
*
*
*
*
*
(2) The term tpy CO2 equivalent
emissions (CO2e) shall represent an
amount of GHGs emitted, and shall be
computed by multiplying the mass
amount of emissions (tpy), for each of
the six greenhouse gases in the pollutant
GHGs, by the gas’s associated global
warming potential published at Table
A–1 to subpart A of part 98 of this
chapter—Global Warming Potentials,
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43507
and summing the resultant value for
each to compute a tpy CO2e. For
purposes of this paragraph, prior to July
21, 2014, the mass of the greenhouse gas
carbon dioxide shall not include carbon
dioxide emissions resulting from the
combustion or decomposition of nonfossilized and biodegradable organic
material originating from plants,
animals, or micro-organisms (including
products, by-products, residues and
waste from agriculture, forestry and
related industries as well as the nonfossilized and biodegradable organic
fractions of industrial and municipal
wastes, including gases and liquids
recovered from the decomposition of
non-fossilized and biodegradable
organic material).
*
*
*
*
*
PART 71—[AMENDED]
7. The authority citation for part 71
continues to read as follows:
■
Authority: 42 U.S.C. 7401, et seq.
Subpart A—[Amended]
8. Section 71.2 is amended by revising
paragraph (2) of the definition of
‘‘Subject to regulation’’ to read as
follows:
■
§ 71.2
*
Definitions.
*
*
*
*
Subject to Regulation
*
*
*
*
*
(2) The term tpy CO2 equivalent
emissions (CO2e) shall represent an
amount of GHGs emitted, and shall be
computed by multiplying the mass
amount of emissions (tpy), for each of
the six greenhouse gases in the pollutant
GHGs, by the gas’s associated global
warming potential published at Table
A–1 to subpart A of part 98 of this
chapter—Global Warming Potentials,
and summing the resultant value for
each to compute a tpy CO2e. For
purposes of this paragraph, prior to July
21, 2014, the mass of the greenhouse gas
carbon dioxide shall not include carbon
dioxide emissions resulting from the
combustion or decomposition of nonfossilized and biodegradable organic
material originating from plants,
animals, or micro-organisms (including
products, by-products, residues and
waste from agriculture, forestry and
related industries as well as the nonfossilized and biodegradable organic
fractions of industrial and municipal
wastes, including gases and liquids
recovered from the decomposition of
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Federal Register / Vol. 76, No. 139 / Wednesday, July 20, 2011 / Rules and Regulations
non-fossilized and biodegradable
organic material).
*
*
*
*
*
[FR Doc. 2011–17256 Filed 7–19–11; 8:45 am]
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Agencies
[Federal Register Volume 76, Number 139 (Wednesday, July 20, 2011)]
[Rules and Regulations]
[Pages 43490-43508]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-17256]
[[Page 43489]]
Vol. 76
Wednesday,
No. 139
July 20, 2011
Part IV
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Parts 51, 52, 70, et al.
Deferral for CO2 Emissions From Bioenergy and Other Biogenic
Sources Under the Prevention of Significant Deterioration (PSD) and
Title V Programs; Final Rule
Federal Register / Vol. 76, No. 139 / Wednesday, July 20, 2011 /
Rules and Regulations
[[Page 43490]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 51, 52, 70, and 71
[EPA-HQ-OAR-2011-0083; FRL-9431-6]
RIN 2060-AQ79
Deferral for CO2 Emissions From Bioenergy and Other
Biogenic Sources Under the Prevention of Significant Deterioration
(PSD) and Title V Programs
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This action defers for a period of three (3) years the
application of the Prevention of Significant Deterioration (PSD) and
Title V permitting requirements to biogenic carbon dioxide
(CO2) emissions from bioenergy and other biogenic stationary
sources. This action is being taken as part of the process of granting
the Petition for Reconsideration filed by the National Alliance of
Forest Owners (NAFO) on August 3, 2010, related to the PSD and Title V
Greenhouse Gas Tailoring Rule. The result of this action is that during
this three year period biogenic CO2 emissions are not
required to be counted for applicability purposes under the PSD and
Title V permitting programs. State, local, and tribal permitting
authorities may adopt the deferral at their option but the deferral is
effective upon publication for the PSD and Title V permit programs that
are implemented by EPA.
DATES: This action is effective on July 20, 2011.
ADDRESSES: EPA has established a docket for this rulemaking under
Docket ID No. EPA-HQ-OAR-2011-0083. All documents in the docket are
listed in the https://www.regulations.gov index. Although listed in the
index, some information is not publicly available, e.g., confidential
business information (CBI) or other information whose disclosure is
restricted by statute. Certain other material, such as copyrighted
material, will be publicly available only in hard copy. Publicly
available docket materials are available either electronically at
https://www.regulations.gov or in hard copy at the Air Docket, EPA/DC,
EPA West, Room 3334, 1301 Constitution Ave., NW., Washington, DC. This
Docket Facility is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding Federal holidays. The telephone number for the Public
Reading Room is (202) 566-1744, and the telephone number for the Air
Docket is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Carole Cook, Climate Change Division,
Office of Atmospheric Programs (MC-6207J), Environmental Protection
Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460; telephone
number: (202) 343-9334; fax number: (202) 343-2342; e-mail address:
biodeferralPSD@epa.gov.
SUPPLEMENTARY INFORMATION: Regulated Entities. The Administrator
determined that this action is subject to the provisions of Clean Air
Act (CAA) section 307(d). See CAA section 307(d)(1)(V) (the provisions
of section 307(d) apply to ``such other actions as the Administrator
may determine''). These are final amendments to existing regulations.
This action applies to stationary sources that emit biogenic
CO2.
Table 1--Examples of Affected Entities by Category
------------------------------------------------------------------------
Examples of affected
Category NAICS facilities
------------------------------------------------------------------------
Biomass combustion............. 221 Electric utilities
burning biomass fuels.
321 Wood products
manufacturing, and
wood pellet fuel
manufacturing.
322 Pulp and paper
manufacturing.
Municipal solid waste 562213 Solid waste combustors
combustion. and incinerators.
Sources/users of biogas........ 112 Animal production
manure management
operations.
221320 Sewage treatment
facilities.
562212 Solid waste landfills.
Fermentation processes......... 325193 Ethanol manufacturing.
325411 Medicinal and botanical
manufacturing.
Other.......................... 311/312 Food/Beverage
processors burning
agricultural biomass
residues, using
fermentation
processes, or
producing/using biogas
from anaerobic
digestion of waste
materials.
------------------------------------------------------------------------
Table 1 of this preamble lists the types of entities that
potentially could be affected by the deferral covered by this action.
This list is not intended to be exhaustive, but rather provides a guide
for readers regarding facilities likely to be affected by this action.
Note that this rule does not make or infer any policy determination on
the part of EPA whether any emissions from any of these sources may be
determined ``fugitive'' emissions for the purposes of accounting and
applicability under air permitting requirements. Such determinations
are not within the scope of this rule and are part of the case-by-case
application and review process established under the regulations
covering these permitting requirements. If you have questions regarding
the applicability of this action to a particular facility, consult the
person listed in the FOR FURTHER INFORMATION CONTACT section of this
preamble.
What is the effective date? The final rule is effective on July 20,
2011. Section 553(d) of the Administrative Procedure Act (APA), 5
U.S.C. Chapter 5, generally provides that rules may not take effect
earlier than 30 days after they are published in the Federal Register.
EPA is issuing this final rule under section 307(d)(1) of the Clean Air
Act, which states: ``The provisions of section 553 through 557 *** of
Title 5 shall not, except as expressly provided in this section, apply
to actions to which this subsection applies.'' Thus, section 553(d) of
the APA does not apply to this rule. EPA is nevertheless acting
consistently with the purposes of the underlying APA section 553(d) in
making this rule effective on July 20, 2011. Section 5 U.S.C. 553(d)(3)
allows an effective date less than 30 days after publication ``as
otherwise provided by the agency for good cause found and published
with the rule.'' As explained below, EPA finds that there is good cause
for this rule to become effective on July 20, 2011, even through this
results in fewer than 30 days from the date of publication in the
Federal Register.
EPA announced its intent to undertake this rulemaking on January
12, 2011, in order to provide the Agency time to conduct a detailed
examination of the science and technical issues associated with
biogenic CO2 emissions
[[Page 43491]]
from stationary sources. The Agency intended to complete the rulemaking
before sources would be subject to the PSD and Title V programs for GHG
emissions because at that time it was possible that a source could be
subject to those requirements based on biogenic CO2
emissions. The Agency determined it could be burdensome for both
permitting authorities and sources to assess those emissions until our
detailed examination was complete. In a January 12, 2011, letter to
several members of Congress, the Administrator wrote, ``No source will
be subject to the pre-construction permitting requirement solely
because of its greenhouse gas emissions until after July 1, 2011. With
the approach of July 1 in mind, I am announcing today that, by that
date, EPA will complete a rulemaking to defer for three years the
application of the pre-construction permitting requirement to biomass
and other biogenic CO2 emissions.''
One purpose of the 30-day waiting period prescribed in 5 U.S.C.
553(d) is to give affected parties a reasonable time to adjust their
behavior and prepare before the final rule takes effect. Whereas here,
the affected parties are anticipating this rule and requesting the
flexibility it provides, and any delay in its effectiveness will result
in uncertainty in the permitting process. In order to ensure that the
final rule is available to the public by July 1, 2011, the final rule
will be signed and made available on the EPA Web site. Publication may
follow one to two weeks after that date. A shorter effective date is
also consistent with the purposes of APA section 553(d)(1), which
provides an exception for any action that grants or recognizes an
exemption or relieves a restriction. Here, this action relieves a
burden because it defers the applicability of the PSD and Title V
permitting requirements for biogenic stationary sources for a period of
three years. Accordingly, we find good cause exists to make this rule
effective on July 20, 2011, consistent with the purposes of 5 U.S.C.
553(d)(1) and (3).
Judicial Review. Under section 307(b)(1) of the CAA, judicial
review of this final rule is available only by filing a petition for
review in the U.S. Court of Appeals for the District of Columbia
Circuit (the Court) by September 19, 2011. Under CAA section
307(d)(7)(B), only an objection to this final rule that was raised with
reasonable specificity during the period for public comment can be
raised during judicial review. CAA section 307(d)(7)(B) also provides a
mechanism for EPA to convene a proceeding for reconsideration, ``[i]f
the person raising an objection can demonstrate to EPA that it was
impracticable to raise such objection within [the period for public
comment] or if the grounds for such objection arose after the period
for public comment (but within the time specified for judicial review)
and if such objection is of central relevance to the outcome of the
rule.'' Any person seeking to make such a demonstration to us should
submit a Petition for Reconsideration to the Office of the
Administrator, Environmental Protection Agency, Room 3000, Ariel Rios
Building, 1200 Pennsylvania Ave., NW., Washington, DC 20460, with a
copy to the person listed in the preceding FOR FURTHER INFORMATION
CONTACT section, and the Associate General Counsel for the Air and
Radiation Law Office, Office of General Counsel (Mail Code 2344A),
Environmental Protection Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20004. Note, under CAA section 307(b)(2), the
requirements established by this final rule may not be challenged
separately in any civil or criminal proceedings brought by EPA to
enforce these requirements.
Acronyms and Abbreviations. The following are acronyms and
abbreviations of terms used in this preamble.
BACT best available control technology
BAU business as usual
CAA Clean Air Act
CBI confidential business information
CFI Call for Information
CFR Code of Federal Regulations
CH4 methane
CO2 carbon dioxide
CO2e carbon dioxide equivalents
EO Executive Order
EPA U.S. Environmental Protection Agency
FR Federal Register
GHG/GHGs greenhouse gas/greenhouse gases
GWP global warming potential
LULUCF Land-Use, Land-Use Change and Forestry
MSW municipal solid waste
NAFO National Alliance of Forest Owners
NAAQS National Ambient Air Quality Standards
NOX nitrogen oxides
NSPS New Source Performance Standards
NSR New Source Review
NTTAA National Technology Transfer and Advancement Act of 1995
PSD Prevention of Significant Deterioration
PTE potential to emit
RFA Regulatory Flexibility Act
SAB Science Advisory Board
SILs significant impact levels
SIP State Implementation Plan
SMCs significant monitoring concentrations
tpy tons per year
U.S. United States
UMRA Unfunded Mandates Reform Act
UNFCCC United Nations Framework Convention on Climate Change
Outline. The information presented in this preamble is organized as
follows:
I. Background
II. Summary of Final Action
A. Overview of the Final Rule
B. Legal Authority
C. Facilities Permitted During Deferral
D. Mechanism for Deferral and State Implementation
III. Response to Public Comments
A. Overview of Public Comments
B. Comments on the Deferral
C. Comments on Science, Accounting, and Economic Issues
D. Comments on PSD, Title V and the Tailoring Rule
E. Comments on the Interim Guidance
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act (UMRA)
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. Background
On June 3, 2010, EPA published the final Prevention of Significant
Deterioration (PSD) and Title V Greenhouse Gas Tailoring Rule (herein
referred to as the Tailoring Rule; 75 FR 31514), setting thresholds for
GHG emissions that define when permits under these programs are
required for new and existing industrial facilities. Beginning January
2, 2011, sources currently subject to PSD or Title V permitting
programs were required to determine the best available control
technology (BACT) for their GHG emissions, but only for GHG increases
of 75,000 short tons per year (tpy) or more of total GHGs, on a carbon
dioxide equivalents (CO2e) basis and any increase on a mass
basis. At that time, no sources would be subject to CAA permitting
requirements due solely to GHG emissions.
Beginning July 1, 2011, the PSD permitting requirements will for
the first time cover new construction projects that will emit GHGs of
at least 100,000 tpy on a CO2e basis even if they do not
exceed the permitting thresholds for any
[[Page 43492]]
other pollutant. Modifications at existing facilities that increase GHG
emissions by at least 75,000 tpy, and any amount on a mass basis, will
be subject to permitting requirements, even if they do not
significantly increase emissions of any other pollutant. Operating
permit requirements will, for the first time, apply to sources based on
their GHG emissions even if they would not apply based on emissions of
any other pollutant. Facilities that emit at least 100,000 tpy
CO2e will be subject to Title V permitting requirements.
As discussed in the final Tailoring Rule, EPA decided not to
provide exemptions from applicability determinations (major source and
major modification) under PSD and Title V for certain GHG emission
sources, including biogenic emissions. EPA decided instead to address
the need for tailoring through a uniform threshold-based approach,
rather than through a collection of various specific exclusions. At
that time, EPA also noted that it planned to seek further comment on
how it might address biogenic CO2 emissions under the PSD
and Title V programs through a future action.
On July 15, 2010, EPA published a Call for Information (CFI) to
solicit information and viewpoints from interested parties on
approaches to accounting for GHG emissions from bioenergy and other
biogenic sources (75 FR 41173). The purpose of this CFI was to request
comment on possible accounting approaches for biogenic CO2
emissions under the PSD and Title V programs, as well as to receive
data submissions about these sources and their GHG emissions, general
technical comments on accounting for these emissions, and comments on
the underlying science that should inform any such accounting approach.
On August 3, 2010, NAFO petitioned the EPA to reconsider and stay
the implementation of the PSD and Title V GHG Tailoring Rule. The
petition alleged that the final Tailoring Rule declared, for the first
time and without any prior proposal or notice to industry, that EPA
would count CO2 emissions from combustion of biomass toward
the applicability thresholds established for the PSD and Title V
permitting programs of the CAA. Petitioners further alleged that EPA's
proposed rule had provided for the appropriate and opposite conclusion:
That CO2 emissions from combustion of biomass should not be
counted. Petitioners stated that there is near-universal recognition
that CO2 emitted from combustion of fuels derived from
biomass should be excluded from GHG regulations because production and
combustion of such fuels do not increase atmospheric CO2
levels. Pending reconsideration, petitioners requested that the
application of the PSD and Title V permitting programs to emissions of
CO2 from biomass be stayed.
We considered carefully the petitioners' assertions and noted that
we also received comments through the CFI supporting the exclusion of
biogenic CO2 from stationary source permitting requirements.
Through the CFI, however, EPA also received information supporting the
position that biogenic CO2 should not be excluded from
permitting programs, and that the use of certain types of biomass as
fuel could increase atmospheric CO2 levels. Based on
consideration of the petitioners' arguments, together with the weight
of the comments received through the CFI, EPA concluded that the issue
of accounting for the net atmospheric impact of biogenic CO2
emissions is complex enough that further consideration of this
important issue is warranted. Therefore, EPA granted the NAFO petition
on January 12, 2011.\1\
---------------------------------------------------------------------------
\1\ https://www.epa.gov/NSR/actions.html#mar11.
---------------------------------------------------------------------------
On January 12, 2011, EPA also announced in letters to Members of
Congress and NAFO its intent to take a number of steps to address the
issues associated with biogenic CO2 emissions from
stationary sources. Pursuant to this announcement, on March 21, 2011,
EPA published a notice of proposed rulemaking to defer for three years
the application of the PSD and Title V permitting requirements to
biogenic CO2 emissions from stationary sources (76 FR
15249). Concurrent with this rulemaking, EPA also issued interim
guidance entitled, ``Guidance for Determining Best Available Control
Technology for Reducing Carbon Dioxide Emissions from Bioenergy
Production'' to help permitting authorities establish a basis for
concluding that under the PSD Program the combustion of biomass fuels
can be considered BACT for biogenic CO2 emissions at
stationary sources until such time as the deferral becomes effective.
During the three-year deferral period, EPA will conduct a detailed
examination of the science associated with biogenic CO2
emissions from stationary sources, including engaging with Federal
partners, technical experts, and an independent scientific panel to
consider technical issues. Based on the feedback from the scientific
and technical review, EPA will then undertake a rulemaking to determine
how biogenic CO2 emissions should be treated and accounted
for in PSD and Title V permitting.
On April 27, 2011, EPA's Science Advisory Board (SAB) published a
notice soliciting experts for a peer review of EPA's science and
technical work on biogenic CO2 emissions. 76 FR 23587. EPA
intends to provide its study that examines the science and technical
issues associated with biogenic CO2 emissions from
stationary sources and accompanying accounting framework to the SAB for
peer review later in 2011.
II. Summary of Final Action
A. Overview of the Final Rule
This action defers for a period of three (3) years the
consideration of CO2 emissions from bioenergy and other
biogenic sources (hereinafter referred to as ``biogenic CO2
emissions'') when determining whether a stationary source meets the PSD
and Title V applicability thresholds, including those for the
application of BACT. Stationary sources that combust biomass (or
otherwise emit biogenic CO2 emissions) and construct or
modify during the deferral period will avoid the application of PSD to
the biogenic CO2 emissions resulting from those actions.
This deferral applies only to biogenic CO2 emissions and
does not affect non-GHG pollutants or other GHGs (e.g., methane
(CH4) and nitrous oxide (N2O)) emitted from the
combustion of biomass fuel. Also, this deferral only pertains to
biogenic CO2 emissions in the PSD and Title V programs and
does not pertain to any other EPA programs such as the GHG Reporting
Program.
EPA recognizes that use of certain types of biomass can be part of
the national strategy to reduce dependence on fossil fuels, efforts are
underway at the Federal, State and regional level to foster the
expansion of renewable resources and promote bioenergy projects when
they are a way to address climate change, increasing domestic
alternative energy production, enhancing forest management and creating
related employment opportunities. We believe part of fostering this
development is to ensure that those feedstocks with negligible net
atmospheric impact not be subject to unnecessary regulation. At the
same time, it is important that EPA have time to conduct its detailed
examination of the science and technical issues related to accounting
for biogenic CO2 emissions and therefore have finalized this
deferral.
This deferral is intended to be a temporary measure, in effect for
no more than three years, to allow the Agency time to complete its work
and
[[Page 43493]]
determine what, if any, treatment of biogenic CO2 emissions
should be in the PSD and Title V programs. This is not EPA's final
determination on the treatment of biogenic CO2 emissions in
those programs. The Agency plans to complete its science and technical
review and any follow-on rulemakings within the three-year deferral
period and further believes that three years is ample time to complete
these tasks. It is possible that the subsequent rulemaking, depending
on the nature of EPA's determinations, would supersede this rulemaking
and become effective in fewer than three years.
Biogenic CO2 emissions are defined as emissions of
CO2 from a stationary source directly resulting from the
combustion or decomposition of biologically-based materials other than
fossil fuels and mineral sources of carbon. Examples of ``biogenic
CO2 emissions'' include, but are not limited to:
CO2 generated from the biological
decomposition of waste in landfills, wastewater treatment or manure
management processes;
CO2 from the combustion of biogas collected
from biological decomposition of waste in landfills, wastewater
treatment or manure management processes;
CO2 from fermentation during ethanol
production or other industrial fermentation processes;
CO2 from combustion of the biological
fraction of municipal solid waste or biosolids;
CO2 from combustion of the biological
fraction of tire-derived fuel; and
CO2 derived from combustion of biological
material, including all types of wood and wood waste, forest
residue, and agricultural material.
For stationary sources co-firing fossil fuel and biologically-based
fuel, and/or combusting mixed fuels (e.g., tire-derived fuels,
municipal solid waste (MSW)), the biogenic CO2 emissions
from that combustion are included in this deferral. However, the fossil
CO2 emissions are not. Emissions of CO2 from
processing of mineral feedstocks (e.g., calcium carbonate) are also not
included in this deferral. Various methods are available to calculate
both the biogenic and fossil portions of CO2 emissions,
including those methods contained in the GHG Reporting Program (40 CFR
Part 98). Consistent with the other pollutants in PSD and Title V,
there are no requirements to use a particular method in determining
your biogenic and fossil CO2 emissions.
B. Legal Authority
1. Applicability of PSD and Title V to Biogenic CO2
Emissions From Major Stationary Sources
As currently written, the PSD and Title V regulations apply to
biogenic CO2 emissions from major sources or major
modifications at such sources according to the limitation included
under the definition of ``subject to regulation'' in the State
Implementation Plan (SIP) regulations at 40 CFR 51.166 and the Title V
state program regulations at 40 CFR 70.2, as well as the Federal
Implementation Plan requirements at 40 CFR 52.21 and the Title V
Federal program regulations at 40 CFR 71.2. Thus, revisions to these
regulations are necessary to defer application of the PSD and Title V
programs to such sources of biogenic CO2.
Stationary sources of air pollutants, including sources of biogenic
CO2 emissions, are currently subject to PSD requirements if
they emit more than 100 or 250 tpy of a regulated NSR pollutant other
than GHGs and have triggered PSD as a result of these emissions,
subject to the permitting thresholds established in the Final Tailoring
Rule described below. The 100/250 tpy thresholds previously described
originate from section 169 of the CAA, which applies PSD to any ``major
emitting facility'' and defines the term to include any source with a
potential to emit (PTE) ``any air pollutant'' in an amount over 100 or
250 tpy, depending on source category.
EPA's long-standing regulations limit the PSD applicability
provision that refers to ``any air pollutant'' to refer to any
``regulated NSR pollutant,'' which in turn includes any air pollutant
``subject to regulation'' under the CAA. Similarly, under sections
165(a)(4) and 169(3) of the CAA, the BACT requirement applies to ``each
pollutant subject to regulation'' under the CAA. As noted in other
recent EPA actions, GHGs are currently ``subject to regulation'' under
the CAA; subject, for PSD purposes, to specific limitations reflected
in the definition of that term that EPA adopted in the Tailoring Rule.
Thus, emissions of GHGs (including CO2) must be considered
in determining whether a source is a major emitting facility subject to
PSD, as a result of construction or modification, and whether the BACT
requirement applies to GHGs (including CO2 as a component of
GHGs). In light of the way these regulations are currently written, EPA
is unable to exclude biogenic CO2 emissions from PSD review
without amending the regulations.
With respect to Title V, as noted previously, Title V applies to
sources, among others, that emit 100 tons per year of specified
quantities of ``any air pollutant,'' see CAA section 502(a), 501(2)(B)
and 302(g).
2. Tailoring Rule
a. Rationale and Requirements
In the Tailoring Rule, EPA codified its interpretation that
``subject to regulation'' only extends to major sources of air
pollutants subject to a requirement for actual control of the quantity
of emissions of that pollutant, and that such a control requirement has
taken effect and is operative to control, limit or restrict the
quantity of emissions of that pollutant released from the regulated
activity, see 75 FR at 31606-07, and further defined ``subject to
regulation'' such that GHGs are only ``subject to regulation'' under
certain circumstances defined in the Tailoring Rule.
In the Tailoring Rule, EPA recognized that if the applicability
provisions of the PSD and Title V programs were applied literally so
that PSD and Title V requirements applied to GHG-emitting sources at
the 100/250 tpy levels provided in the CAA, then the permitting
authorities would be overwhelmed by the large numbers of permittees and
many small sources would be unduly encumbered by the permitting
demands. In light of those impacts, EPA concluded that, as a legal
matter, Congress did not intend that the PSD and Title V applicability
requirements be applied literally to all sources emitting GHGs over the
major source thresholds as of January 2, 2011, the date by which EPA
determined that GHGs become subject to regulation under the CAA as a
result of the motor vehicle rule. Instead, EPA concluded that it is
authorized to tailor those applicability requirements to apply PSD and
Title V to such sources in a phased-in manner, starting with the
largest sources first.
Specifically, in the Tailoring Rule, EPA has implemented these PSD
and Title V applicability provisions by applying the familiar two-step
framework for interpreting administrative statutes recognized by the
Supreme Court in Chevron U.S.A. Inc. v. NRDC, 467 U.S. 837 (1984),
taking into account certain legal doctrines. Those doctrines, insofar
as relevant to the Tailoring Rule, are (1) the ``absurd results''
doctrine, which authorizes agencies to apply statutory requirements
differently than a literal reading would indicate, as necessary to
effectuate congressional intent and
[[Page 43494]]
avoid absurd results; (2) the ``administrative necessity'' doctrine,
which authorizes agencies to apply statutory requirements in a way that
avoids impossible administrative burdens; and (3) the ``one-step-at-a-
time'' doctrine, which authorizes agencies to implement a regulatory
scheme in a deliberate, step-wise fashion. See 75 FR 31541-31579.
Under Chevron, the agency must, at step 1, determine whether
Congress' intent as to the specific matter at issue is clear, and, if
so, the agency must give effect to that intent. 467 U.S. at 842. If
congressional intent is not clear, then, at step 2, the agency has
discretion to fashion an interpretation that is a reasonable
construction of the statute. 467 U.S. at 865. To determine
congressional intent, the agency must first consider the words of the
statutory requirements, and if their literal meaning answers the
question at hand, then, in most cases, the agency must implement those
requirements by those terms.
However, under the ``absurd results'' doctrine, the literal meaning
of statutory requirements should not be considered to indicate
congressional intent if that literal meaning would produce a result
that is senseless or that is otherwise inconsistent with -- and
especially one that undermines -- underlying congressional purpose. In
these cases, if congressional intent for how the requirements apply to
the question at hand is clear, the agency should implement the
statutory requirements not in accordance with their literal meaning,
but rather in a manner that most closely effectuates congressional
intent. If congressional intent is not clear, then an agency may select
an interpretation that is reasonable under the statute.
Under the ``administrative necessity'' doctrine, Congress is
presumed, at Chevron step 1, to intend that its statutory directives to
agencies be administrable, and not to have intended to have written
statutory requirements that are impossible to administer. Therefore,
under this doctrine, an agency may depart from statutory requirements
that, by their terms, are impossible to administer, but the agency may
depart no more than necessary to render the requirements administrable.
In addition to the ``absurd results'' and ``administrative
necessity'' doctrines, another judicial doctrine supports at least part
of EPA's Tailoring Rule, and that is the doctrine that agencies may
implement statutory mandates one step at a time, which we will call the
``one-step-at-a-time'' doctrine. The U.S. Supreme Court recently
described the doctrine in Massachusetts v. EPA, 549 U.S. 497, 524
(2007), as follows: ``Agencies, like legislatures, do not generally
resolve massive problems in one fell regulatory swoop;'' and instead
they may permissibly implement such regulatory programs over time,
``refining their preferred approach as circumstances change and as they
develop a more nuanced understanding of how best to proceed.''
In the Tailoring Rule, EPA closely considered the burdens to the
permitting authorities of applying PSD and Title V to GHG-emitting
sources. For example, EPA calculated, on a national basis, the workload
that GHG permit applications would entail, and compared that to the
existing workload of permitting authorities. EPA concluded that
permitting authorities would be overwhelmed by permit applications if
the PSD and Title V applicability thresholds were applied literally as
of January 2, 2011, to the GHG emissions from stationary sources. In
addition, EPA calculated the cost to the sources of permitting
requirements and concluded that many small sources would become subject
to unduly high expenses.
Accordingly, in applying the Chevron analytical framework, in
conjunction with the absurd results and administrative necessity
doctrines, EPA concluded that Congress intended that PSD and Title V
apply to the GHG emissions from stationary sources, but that, in light
of the burdens to the permitting authority and the costs to the sources
of determining applicability of permitting requirements by applying the
statutory thresholds to GHG emissions, the application of the
permitting programs should be phased in, starting with the largest
sources of GHG emissions first. EPA also concluded that the calculation
for determining which sources emit the ``largest'' amount of GHG
emissions should be based on the amount of GHG pollutant emitted in
tons per year, weighted by the global warming potential (GWP) of the
particular GHG pollutant.
Accordingly, in the Tailoring Rule, EPA established two steps to
implement PSD and Title V. At step 1, beginning January 2, 2011,
sources currently subject to PSD or Title V permitting programs were
required to determine the BACT for their GHG emissions, but only for
GHG increases of 75,000 short tons per year (tpy) or more of total
GHGs, on a CO2e basis and any increase on a mass basis. At
that time, no sources would be subject to CAA permitting requirements
due solely to GHG emissions. At step 2, beginning July 1, 2011, the PSD
permitting requirements will for the first time cover new construction
projects that will emit GHG emissions of at least 100,000 tpy on a
CO2e basis (and 250 tons on a mass basis) even if they do
not exceed the permitting thresholds for any other pollutant.
Modifications at existing facilities that emit at that level and
increase GHG emissions by at least 75,000 tpy CO2e and by any amount on
a mass basis will be subject to permitting requirements, even if they
do not significantly increase emissions of any other pollutant.
In addition, EPA committed to promulgate by July 1, 2012, another
rulemaking--in effect, step 3 of the Tailoring Rule--that would
consider whether to reduce the thresholds further. EPA also committed
to promulgate another rulemaking after that, by April 1, 2016, that
would consider still further action. As EPA stated in the Tailoring
Rule, part of the purpose of the phase-in approach embodied in the
Tailoring Rule is to allow permitting authorities time to acquire
additional resources and to allow EPA time to develop streamlining
methods and thereby enable the application of PSD and Title V to more
sources in subsequent rulemakings.
As noted previously, in the Tailoring Rule, EPA determined that the
amount of each GHG emitted by a facility should be calculated by
reference to the weight of the GHG emissions, in tons of
CO2e per year for determining if GHGs were ``subject to
regulation'' for a particular facility and project. The Tailoring Rule
proposal referenced EPA's Inventory of U.S. Greenhouse Gas Emissions
and Sinks (Inventory) \2\ submitted annually to the United Nations
Framework Convention on Climate Change (UNFCCC), for the applicable GWP
values and guidance on how to calculate a source's GHG emissions in tpy
CO2e. 75 FR 31514-31608. The Inventory includes emissions of
the six GHGs in terms of CO2e units. By linking the
calculation of CO2e for GHGs to GWP values, a facility could
evaluate its total GHG emissions contribution based on a single metric.
We solicited comment on the benefits and limitations of this proposed
metric.
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\2\ ``Inventory of U.S. Greenhouse Gas Emissions and Sinks:
1990-2008,'' U.S. Environmental Protection Agency, EPA 430-R-10-006
(April 15, 2010). https://www.epa.gov/climatechange/emissions/usinventoryreport.html.
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While we referred to the Inventory for GWP identification purposes
only, several commenters appeared to misunderstand our intent, claiming
that the Inventory excludes CO2 emitted from biomass. These
commenters
[[Page 43495]]
requested that, in calculations of emissions for determining
applicability of PSD and Title V, EPA exempt emissions from biogenic
activities or biomass combustion or oxidation activities, including
solid waste landfills, waste-to-energy projects, fermentation
processes, combustion of renewable fuels, ethanol manufacturing,
biodiesel production, and other alternative energy production that uses
biomass feedstocks (e.g., crops or trees). In particular, these
commenters urged that EPA exclude emissions from biomass combustion in
determining the applicability of PSD to such sources based on the
notion that such combustion is ``carbon neutral'' (i.e., that
combustion or oxidation of such materials would cause no net increase
in GHG emissions on a lifecycle basis).
b. Treatment of Biogenic Emissions
In response, when finalizing the Tailoring Rule, we acknowledged
the role that biomass or biogenic fuels and feedstocks could play in
reducing anthropogenic GHG emissions, and did not dispute the
commenters' observations that many state, Federal, and international
rules and policies treat biogenic and fossil sources of CO2
emissions differently (75 FR 31514). Regarding commenters' claims that
the Inventory excludes CO2 emissions from biomass, EPA noted
that the Inventory does not exclude these emissions (see section II.A.2
of the preamble to the proposed deferral rule). Rather, they are
included in the Land-Use, Land-Use Change and Forestry (LULUCF) Sector
rather than the Energy Sector to avoid double-counting at the national
scale. The narrow reference to the use of the Inventory's GWP values
for estimating GHG emissions was provided to offer consistent guidance
on how to calculate these emissions and not as an indication, direct or
implied, that biomass emissions would be excluded from permitting
applicability merely by association with the national inventory, see 74
FR 55351, under the definition for ``carbon dioxide equivalent.''
We determined that our application of the ``absurd results,''
``administrative necessity,'' and one-step-at-a-time legal rationales
supporting the Tailoring Rule, based on the expected overwhelming
permitting burdens in its absence, did not provide sufficient basis to
exclude emissions of CO2 from biogenic sources in
determining permitting applicability provisions at that time. We
reasoned that such an exclusion alone, while reducing burdens for some
sources, would not address the overwhelming permitting burdens, and a
threshold-based approach would still be needed. At that time, we had
not examined burdens with respect to specific source categories
impacted by the rule and thus had not analyzed the administrative
burden of permitting projects that specifically involve biogenic
CO2 emissions taking account of the threshold-based
approach. Commenters also did not provide information to demonstrate
that an overwhelming permitting burden would still exist, justifying a
temporary exclusion for biomass sources.
In the final Tailoring Rule, we indicated that the decision not to
provide this type of an exclusion at that time did not foreclose EPA's
ability to either (1) provide this type of exclusion at a later time
with additional information about overwhelming permitting burdens due
to biomass sources, or (2) provide another type of exclusion or other
treatment based on some other rationale. Although we did not take a
final position, we noted that some commenters' observations about a
different treatment of biomass combustion warranted further exploration
as a possible rationale.
Therefore, although we did not establish a permanent exclusion from
PSD or Title V applicability based on specific characteristics of
biogenic CO2, we indicated our intent to seek further
comment on how we might address emissions of biogenic CO2
under the PSD and Title V programs through a future action.
We further noted that, while not promulgating an applicability
exclusion for biogenic emissions and biomass fuels or feedstocks in the
final Tailoring Rule, flexibility exists to apply the existing
regulations and policies regarding BACT in ways that take into account
their net effects on atmospheric GHG concentrations. Without prejudging
the outcome of our process to seek comment on whether and how we might
address emissions of biogenic carbon under the PSD and Title V programs
through a future action, we indicated that this issue warranted further
exploration.
As mentioned earlier in the preamble, in order to explore the issue
further following the promulgation of the Tailoring Rule, on July 15,
2010, EPA solicited views from the public through a CFI on approaches
to accounting for biogenic CO2 emissions, on the means to
estimate and measure CO2 emissions from a variety of
biogenic CO2 sources and other information on biogenic
sources that may be affected but not identified in the CFI.
With promulgation of the Tailoring Rule we committed to issue
technical and policy guidance for permitting of GHGs. Subsequently, the
information gathered from stakeholders in response to the CFI provided
diverse perspectives on treatment of biogenic CO2 emissions
in pre-construction and operating permit reviews, including many
requests to exclude, either partially or wholly, biogenic
CO2 sources from PSD applicability determinations and BACT
analyses on the basis of Inventory results and other considerations. On
November 10, 2010, EPA issued the draft ``PSD and Title V Permitting
Guidance for Greenhouse Gases'' which provides the basic information
that permit writers and applicants need to address GHG emissions in
permits. Within the November guidance, EPA acknowledged the numerous
stakeholder comments on biogenic CO2 BACT analyses and
provided general guidance to permitting authorities to consider
environmental, energy, and economic benefits that may accrue from the
use of certain types of biomass (e.g., biogas from landfills for energy
generation), consistent with existing air quality standards. We also
committed to provide more detailed technical and policy guidance early
in 2011 for completing step 4 of a ``top-down'' BACT analysis for GHG
emissions from certain types of biomass sources to enable permitting
authorities to simplify and streamline BACT determinations for such
sources. EPA provided interim guidance on this topic in March 2011,
concurrent with the proposal of this rule to assist permitting
authorities before the deferral becomes effective.\3\
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\3\ ``Guidance for Determining Best Available Control Technology
for Reducing Carbon Dioxide Emissions from Bioenergy Production,''
U.S. EPA Office of Air and Radiation, March 2011. (https://www.epa.gov/nsr/ghgdocs/bioenergyguidance.pdf)
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Noting that a variety of Federal and state policies have recognized
that some types of biomass can be part of a national strategy to reduce
dependence on fossil fuels and to reduce emissions of GHGs, EPA has
determined that it is appropriate for permitting authorities to account
for both existing Federal and state policies and their underlying
objectives in evaluating the environmental, energy and economic
benefits of biomass fuel. Based on these considerations, permitting
authorities might determine that the use of certain types of biomass
alone meets the BACT requirement for GHGs.
As described in the Background section of this preamble, NAFO
petitioned the EPA on August 3, 2010 to reconsider and stay the
implementation of the PSD and Title V GHG Tailoring Rule. Pending
reconsideration, petitioners requested that the application of the PSD
and Title V
[[Page 43496]]
permitting programs to emissions of CO2 from biomass be
stayed.
Based on consideration of the petitioners' arguments, together with
the weight of the comments received on the CFI, EPA concluded that the
issue of accounting for the net atmospheric impact of biogenic
CO2 emissions is complex enough that further consideration
of this important issue is warranted. Therefore, EPA granted the
petition on January 12, 2011.
However, EPA did not grant the request for an administrative stay
of the Tailoring Rule, because the rule is critical for making overall
implementation of the PSD program feasible. Furthermore, an
administrative stay of the statements in the preamble of the Tailoring
Rule that describe EPA's initial determination not to exempt emissions
of CO2 from biomass would not provide the requested relief
of excluding emissions of CO2 from biomass from the PSD and
Title V permitting programs. The effect of a stay of this or any other
aspect of the Tailoring Rule would be to return to the legal regime
that existed before EPA's issuance of a final Tailoring Rule. As no
exemption for emissions of CO2 from biomass existed prior to
the final rule, an administrative stay would not result in an exemption
from the requirements of PSD and Title V.
3. Rationale in Support of Interim Biomass Deferral
a. Regulation at This Time Is Not Justified
Since finalizing the Tailoring Rule, EPA has gathered additional
information concerning biomass through the CFI and in response to the
proposal for this rule. The information collected to this point
underscores the complexity and uncertainty associated with accounting
for biogenic emissions of CO2 and indicates that at present
attempting to determine the net carbon cycle impact of particular
facilities combusting particular types of biomass feedstocks would
require extensive analysis and would therefore entail extensive
workload requirements by many of the permitting authorities. In
contrast to other sources of GHG emissions, these uncertainties and
complexities are exacerbated because of the unique role and impact
biogenic sources of CO2 have in the carbon cycle. Further,
methodologies are not sufficiently developed to assure that various
permitting authorities would be able to perform the necessary
calculations reasonably and consistently to determine the net
atmospheric impact in many, if not all, instances.
The extensive workload requirements required to understand the net
biogenic CO2 emissions from bioenergy facilities and other
sources of biogenic CO2 emissions, as part of the PSD and
Title V permit process, including specifically how to measure and
account for biogenic CO2 emissions, would unnecessarily
strain the resources of the affected permitting authorities and result
in delays in processing permits for other applicants. Moreover, at
present, devoting these limited permitting authority resources to
biomass sources would not be productive in light of the possibility
that EPA may ultimately determine that the utilization of some or all
biomass feedstocks for bioenergy has a negligible (or de minimis),
negative, or positive net impact on the carbon cycle.
Therefore, the information EPA has collected since promulgating the
Tailoring Rule indicates that it is consistent with the rationale of
the Tailoring Rule for affected permitting authorities to defer on a
temporary basis biogenic CO2 emissions from PSD and Title V
applicability. During this deferral, EPA will conduct a detailed
examination of the science associated with biogenic CO2
emissions from stationary sources, which will include a peer review by
the SAB, and resolve technical issues in order to account for biogenic
CO2 emissions in ways that are scientifically sound and also
manageable in practice.
As noted previously, EPA based the Tailoring Rule on the extreme
administrative burdens to permitting authorities, and undue costs to
sources, that would result from a literal application of the PSD and
Title V 100/250 tpy statutory thresholds, as of January 2, 2011, when
those requirements first applied to GHGs. EPA reasoned that, in
accordance with the Chevron analytical framework for statutory
construction, taking into account the ``absurd results'' and
``administrative necessity'' lines of cases, Congress did not intend
that the PSD and Title V requirements apply at the 100/250 tpy
statutory thresholds to GHG-emitting sources as of January 2, 2011, but
rather that those requirements could be limited, at least initially,
through a phase-in approach, to higher-emitting sources.
Just as the extensive workload of processing permit applications
from sources below the Tailoring Rule thresholds justified exempting
those sources at least from the initial steps in the Tailoring Rule
phase-in program, so too the extensive workload associated with
analyzing and accounting for biogenic CO2 emissions as part
of processing permit applications from biomass facilities justifies
exempting those sources for a period of time, in the affected states,
pending EPA's development of a consistent and practical framework for
determining net carbon cycle impacts. The three-year deferral EPA is
finalizing in this action is reasonable to allow time for the
development of the accounting framework and subsequent rulemaking.
In effect, this deferral is a step back from the Tailoring Rule's
approach but the decision to defer the applicability of PSD and Title V
to biogenic CO2 emissions is nonetheless supported, in part,
on the same rationale as EPA used to justify the Tailoring Rule's
phase-in approach. This action constitutes a refinement of the approach
EPA has taken to regulate GHG emissions from stationary sources through
a phased-in approach, based on an evolving understanding of the
complexities, uncertainties, and nuances associated with biogenic
emissions.
An alternative way to reduce the permitting burden would be to
apply PSD and Title V to all facilities with biogenic CO2
emissions that emit at or above the Tailoring Rule thresholds, but
without making any effort to take into account net carbon cycle
impacts. However, we believe that it is conceivable that as a result of
the scientific examination of biogenic CO2 emissions, we
could conclude that the net carbon cycle impact for some biomass
feedstocks is trivial, negative, or positive. Accordingly, this could
result in regulation of sources with trivial or positive impacts on the
net carbon cycle, as previously discussed. To avoid this outcome, given
our current state of knowledge, we believe a case-by-case net carbon
cycle impact analysis would be required in the course of reviewing each
permit application. This burden would be in addition to the currently
existing burden associated with obtaining a PSD or Title V permit. In
light of the permitting burdens assessed in the Tailoring Rule, adding
to that burden in many states would frustrate the goals we sought to
accomplish in the Tailoring Rule to ensure that the PSD and Title V
programs can be administered in each state.
Furthermore, given the potential that the utilization of at least
some biomass feedstocks may have a negligible impact on the net carbon
cycle, engaging in this type of burdensome analysis may not be an
optimal use of the limited resources of PSD and Title V permitting
authorities. The additional scientific examination being undertaken by
the EPA could ultimately conclude that
[[Page 43497]]
such resources could have been more effectively utilized to target
CO2 emissions that clearly have a detrimental impact on the
net carbon cycle. Establishing a three-year deferral period for
biogenic CO2 emissions will enable EPA to consider the
results of the detailed examination of the science of these emissions
and undertake a rulemaking to determine the best way to account for
biogenic CO2 emissions when determining PSD applicability.
Another important reason for the three-year deferral period is to
allow sufficient time to consider the unique characteristics and
attributes of biogenic CO2 feedstocks, as opposed to other
sources of GHG, using the results from the detailed examination
mentioned previously, within both the state permitting agencies and
affected facilities. While the interim BACT guidance described
previously will help alleviate some of this burden before the deferral
becomes effective, we expect that more and more diverse users of
biomass combustion or other biogenic CO2 sources are likely
to be affected under step 2 of the Tailoring Rule because, under step
2, these sources can trigger permitting requirements based solely on
their GHG emissions with no prerequisite requirement that they
otherwise trigger PSD or Title V permitting requirements for a non-GHG
pollutant. We believe, absent the deferral period and the completion of
EPA's full analysis of the unique technical issues associated with
these diverse facilities emitting biogenic CO2, that it
would be particularly challenging for many of the permitting
authorities and facilities to process permits involving these
emissions. Also, as described elsewhere in this preamble, this interim
deferral is intended to temporarily exclude biogenic CO2
emissions from the definition of ``subject to regulation,'' as that
term was defined for purposes of the Tailoring Rule, for a period of
three years, while EPA further considers, through notice and comment
rulemaking, the approach to accounting for these emissions on a
permanent basis.
b. One-Step-at-a-Time Doctrine
EPA relied, in part, on the ``one-step-at-a-time'' doctrine, which
authorizes agencies to implement statutory requirements a step at a
time, in finalizing the Tailoring Rule. 75 FR 31514, 31578 (June 3,
2010). As described in the Tailoring Rule and earlier in the preamble,
the case law recognizing the ``one-step-at-a-time'' doctrine, within
the Chevron framework, justifies an agency's step-by-step approach
under the following circumstances or conditions: (1) The agency's
ability to comply with a statutory directive depends on facts,
policies, or future events that are uncertain; (2) the agency has
estimated the extent of its remaining obligation; (3) the agency's
incremental actions are structured in a manner that is reasonable in
light of the uncertainties; and (4) the agency is on track to full
compliance with the statutory requirements.
In the proposed rule, EPA stated in footnote 13 that the ``one-
step-at-a-time'' doctrine was not relevant to this rulemaking. This
statement was made without explanation. One commenter (EPA-HQ-OAR-2011-
0083-0084) stated ``[b]ased on EPA's statements in the Tailoring Rule,
which does rely on the `one-step-at-a-time' doctrine, it appears that
the doctrine would apply equally well to EPA's decision to delay
regulation of biogenic CO2 emissions under the PSD and Title
V programs.'' For the reasons stated below, EPA now agrees that,
because of the complexity and uncertainty of the science associated
with accounting for biogenic sources of CO2, the interim
deferral of the PSD and Title V program for such emissions would be a
reasonable exercise of the ``one-step-at-a-time'' doctrine.
First, as the DC Circuit stated in National Association of
Broadcasters v. FCC, 740 F.2d 1190, 1210 (DC Cir. 1984) (``National
Association of Broadcasters''), incremental agency action is most
readily justifiable ``against a shifting background in which facts,
predictions, and policies are in flux and in which an agency would be
paralyzed if all the necessary answers had to be in before any action
at all could be taken.'' Those circumstances are present here, and so
is the fact that the task at hand is extraordinarily demanding. As
discussed previously, EPA is in the process of conducting a detailed
examination of the science associated with biogenic CO2
emissions from stationary sources to better understand their role on
the carbon cycle and to develop an accounting framework for use by
permitting authorities and sources. This examination will include
discussion with partners and scientists both inside and outside the
Federal government, as well as engagement with the Science Advisory
Board, to consider technical issues that the Agency must resolve in
order to account for biogenic CO2 emissions in ways that are
scientifically sound and also manageable in practice.
Second, as the Court stated in National Association of
Broadcasters, ``the agency [should] ma[k]e some estimation, based upon
evolving economic and technological conditions, as to the nature and
magnitude of the problem it will have to confront when it comes to
[undertake the remaining steps]'' and that estimation must be
``plausible and flow from the factual record compiled.'' Id. at 1210.
Here, EPA has done this by deferring the applicability of PSD and Title
V to biogenic emissions of CO2 from stationary sources for
only as long as necessary for EPA to complete the needed scientific
study of these emissions, develop an accounting framework, and as
appropriate conduct rulemaking specific to the unique nature and
characteristics of these emission sources.
In order to explore the issues further following the promulgation
of the Tailoring Rule, on July 15, 2010, EPA solicited views from the
public through the CFI on approaches to accounting for biogenic
CO2 emissions, including whether some or all of a source's
biogenic CO2 emissions could be discounted based on a
determination that they are canceled out by the CO2
absorption associated with growing the fuel (75 FR 41173). Also, we
solicited information on the means to estimate and measure
CO2 emissions from a variety of biogenic CO2
sources that typically have not been part of emission inventories
(e.g., CO2 from landfills, livestock management, and
fermentation processes), as well as information on other biogenic
sources that may be affected but which were not identified specifically
in the CFI.
With promulgation of the Tailoring Rule, we committed to issue
technical and policy guidance for permitting of GHGs. Subsequently, the
information gathered from stakeholders in response to the CFI provided
diverse perspectives on treatment of biogenic CO2 emissions
in pre-construction and operating permit reviews, including many
requests to exclude, either partially or wholly, biogenic
CO2 sources from PSD applicability determinations and BACT
analyses on the basis of Inventory results and other considerations.
Third, again as the Court stated in National Association of
Broadcasters, it must be ``reasonable, in the context of the decisions
made in the proceeding under review, for the agency to have deferred
the issue to the future. With respect to that question, postponement
will be most easily justified when an agency acts against a background
of rapid technical and social change and when the agency's initial
decision as a practical matter is reversible should the future
proceedings yield drastically unexpected results.'' Id. at 1211. Here,
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our deferral is reasonable in light of the technical and scientific
questions that are raised by biogenic emissions from stationary
sources, which will be addressed by EPA's ongoing study, development of
an accounting framework, and any subsequent rulemaking. As explained in
the proposal and elsewhere in the preamble to this final rule, EPA
believes it has the authority to exclude biogenic CO2
emissions from the PSD and Title V requirements for the proposed three-
year deferral period and will be exploring whether a permanent
exemption is appropriate for at least some and perhaps all types of
feedstocks.
However, the possibility also remains that more detailed
examination of the science of biogenic CO2 will demonstrate
that the utilization of some biomass feedstocks for bioenergy
production will have a significant impact on the net carbon cycle,
making literal application of the PSD program requirements to such
emissions, consistent with the Tailoring Rule, necessary to fulfill
congressional intent. Thus, EPA is finalizing only a temporary, rather
than a permanent, deferral of PSD requirements for such sources at this
time. EPA notes that the issue of subsequent applicability of the PSD
and Title V programs to facilities that may be permitted during the
deferral period is discussed in more detail in section II.C.
Finally, as the DC Circuit stated in Grand Canyon Air Tour
Coalition v. F.A.A., 154 F.3d 455, 477-78 (DC Cir. 1998), the Courts
will accept an initial step towards full compliance with a statutory
mandate, as long as the agency is headed towards full compliance, and
we now believe that the doctrine is applicable here.
As we have described in the CFI, the preamble to the proposed
deferral and elsewhere in the preamble for this final rule, there is
little question as to the complexity in accounting for and
understanding the impact of biogenic CO2