Prevention of Significant Deterioration and Title V Greenhouse Gas Tailoring Rule, 55292-55365 [E9-24163]
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Federal Register / Vol. 74, No. 206 / Tuesday, October 27, 2009 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 51, 52, 70, and 71
[EPA–HQ–OAR–2009–0517; FRL–8966–7]
RIN 2060–AP86
Prevention of Significant Deterioration
and Title V Greenhouse Gas Tailoring
Rule
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AGENCY: Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
SUMMARY: EPA is proposing to tailor the
major source applicability thresholds for
greenhouse gas (GHG) emissions under
the Prevention of Significant
Deterioration (PSD) and title V programs
of the Clean Air Act (CAA or Act) and
to set a PSD significance level for GHG
emissions. This proposal is necessary
because EPA expects soon to
promulgate regulations under the CAA
to control GHG emissions and, as a
result, trigger PSD and title V
applicability requirements for GHG
emissions. If PSD and title V
requirements apply at the applicability
levels provided under the CAA, State
permitting authorities would be
paralyzed by permit applications in
numbers that are orders of magnitude
greater than their current administrative
resources could accommodate. On the
basis of the legal doctrines of ‘‘absurd
results’’ and ‘‘administrative necessity,’’
this proposed rule would phase in the
applicability thresholds for both the
PSD and title V programs for sources of
GHG emissions. The first phase, which
would last 6 years, would establish a
temporary level for the PSD and title V
applicability thresholds at 25,000 tons
per year (tpy), on a ‘‘carbon dioxide
equivalent’’ (CO2e) basis, and a
temporary PSD significance level for
GHG emissions of between 10,000 and
25,000 tpy CO2e. EPA would also take
other streamlining actions during this
time. Within 5 years of the final version
of this rule, EPA would conduct a study
to assess the administrability issues.
Then, EPA would conduct another
rulemaking, to be completed by the end
of the sixth year, that would
promulgate, as the second phase,
revised applicability and significance
level thresholds and other streamlining
techniques, as appropriate.
DATES: Comments. Comments must be
received on or before December 28,
2009. Under the Paperwork Reduction
Act, comments on the information
collection provisions are best assured of
having full effect if the Office of
Management and Budget (OMB)
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receives a copy of your comments on or
before November 27, 2009.
Public Hearing: If anyone contacts us
requesting to speak at a public hearing
on or before November 16, 2009, we will
hold a public hearing approximately 30
days after date of publication in the
Federal Register.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2009–0517 by one of the following
methods:
• https://www.regulations.gov. Follow
the online instructions for submitting
comments. Attention Docket ID No.
EPA–HQ–OAR–2009–0517.
• E-mail: a-and-r-docket@epa.gov.
Attention Docket ID No. EPA–HQ–
OAR–2009–0517.
• Fax: (202) 566–9744. Attention
Docket ID No. EPA–HQ–OAR–2009–
0517.
• Mail: EPA Docket Center, EPA West
(Air Docket), Attention Docket ID No.
EPA–HQ–OAR–2009–0517, U.S.
Environmental Protection Agency,
Mailcode: 2822T, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460.
Please include a total of 2 copies. In
addition, please mail a copy of your
comments on the information collection
provisions to the Office of Information
and Regulatory Affairs, Office of
Management and Budget (OMB), Attn:
Desk Officer for EPA, 725 17th Street,
NW., Washington, DC 20503.
• Hand Delivery: U.S. Environmental
Protection Agency, EPA West (Air
Docket), 1301 Constitution Avenue,
Northwest, Room 3334, Washington, DC
20004, Attention Docket ID No. EPA–
HQ–OAR–2009–0517. Such deliveries
are only accepted during the Docket’s
normal hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions. Direct your comments to
Docket ID No. EPA–HQ–OAR–2009–
0517. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or e-mail. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an e-mail comment directly
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to EPA without going through https://
www.regulations.gov, your e-mail
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
made available on the Internet. If you
submit an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD–ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, avoid any form of
encryption, and be free of any defects or
viruses. For additional information
about EPA’s public docket, visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets.htm.
Docket. 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., 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 in https://
www.regulations.gov or in hard copy at
the Air and Radiation Docket and
Information Center, EPA/DC, EPA West
Building, Room 3334, 1301 Constitution
Ave., NW., Washington, DC. The Public
Reading Room is open from 8:30 a.m. to
4:30 p.m., Monday through Friday,
excluding legal 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: Mr.
Joseph Mangino, Air Quality Policy
Division, Office of Air Quality Planning
and Standards (C504–03),
Environmental Protection Agency,
Research Triangle Park, NC 27711;
telephone number: (919) 541–9778; fax
number: (919) 541–5509; e-mail address:
mangino.joseph@epa.gov.
To request a public hearing, please
contact Pam Long, Air Quality Planning
Division, Office of Air Quality Planning
and Standards (C504–03),
Environmental Protection Agency,
Research Triangle Park, NC 27711;
telephone number: (919) 541–0641; fax
number: (919) 541–5509 no later than
November 16, 2009 to request a hearing.
SUPPLEMENTARY INFORMATION:
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I. Preamble Glossary of Terms and
Abbreviations
The following are abbreviations of
terms used in the preamble.
APA Administrative Procedure Act
ANPR Advance Notice of Proposed
Rulemaking
APA Administrative Procedure Act
AQRV Air Quality Related Value
BACT Best Available Control Technology
CAA Clean Air Act
CAM Compliance Assurance Monitoring
CBI Confidential Business Information
CFR Code of Federal Regulations
CH4 Methane
CO2 Carbon Dioxide
CO2e Carbon Dioxide Equivalent
CO Carbon Monoxide
EG Emission Guidelines
EPA U.S. Environmental Protection Agency
FERC Federal Energy Regulatory
Commission
FIP Federal Implementation Plan
FLM Federal Land Manager
FTC Federal Trade Commission
FTE Full-Time Equivalent
GHG Greenhouse Gas
GWP Global Warming Potential
HAP Hazardous Air Pollutant
HFC Hydrofluorocarbon
HFE Hydrofluorinated Ether
ICR Information Collection Request
IPCC Intergovernmental Panel on Climate
Change
MWCs Municipal Waste Combustion
Facilities
NAAQS National Ambient Air Quality
Standard
NESHAP National Emission Standards for
Hazardous Air Pollutants
NOD Notice of Deficiency
NOX Nitrogen Oxides
NSPS New Source Performance Standard
NSR New Source Review
OMB Office of Management and Budget
OTAQ Office of Transportation and Air
Quality
PFC Perfluorocarbon
ppm Parts Per Million
PSD Prevention of Significant Deterioration
PTE Potential to Emit
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RIA Regulatory Impact Analysis
SBA Small Business Administration
SO2 Sulfur Dioxide
SF6 Sulfur Hexafluoride
SIP State Implementation Plan
Tg Teragrams
TIP Tribal Implementation Plan
tpy Tons Per Year
UNFCCC United Nations Framework
Convention on Climate Change
II. General Information
A. Does this action apply to me?
Entities affected by this proposed
action include sources in all sectors of
the economy, including commercial and
residential sources. Entities potentially
affected by this proposed action also
include States, local permitting
authorities, and tribal authorities. The
majority of categories and entities
potentially affected by this action are
expected to be in the following groups:
Industry Group
NAICSa
Agriculture, fishing, and hunting ...............................................................
Mining .......................................................................................................
Utilities (electric, natural gas, other systems) ..........................................
Manufacturing (food, beverages, tobacco, textiles, leather) ....................
Wood product, paper manufacturing ........................................................
Petroleum and coal products manufacturing ...........................................
Chemical manufacturing ...........................................................................
Rubber product manufacturing .................................................................
Miscellaneous chemical products .............................................................
Nonmetallic mineral product manufacturing .............................................
Primary and fabricated metal manufacturing ...........................................
11.
21.
2211, 2212, 2213.
311, 312, 313, 314, 315, 316.
321, 322.
32411, 32412, 32419.
3251, 3252, 3253, 3254, 3255, 3256, 3259.
3261, 3262.
32552, 32592, 32591, 325182, 32551.
3271, 3272, 3273, 3274, 3279.
3311, 3312, 3313, 3314, 3315, 3321, 3322, 3323, 3324, 3325, 3326,
3327, 3328, 3329.
3331, 3332, 3333, 3334, 3335, 3336, 3339.
3341, 3342, 3343, 3344, 3345, 4446.
3351, 3352, 3353, 3359.
3361, 3362, 3363, 3364, 3365, 3366, 3369.
3371, 3372, 3379.
3391, 3399.
5622, 5629.
6221, 6231, 6232, 6233, 6239.
8122, 8123.
8141.
Not available. Codes only exist for private households, construction
and leasing/sales industries.
Machinery manufacturing .........................................................................
Computer and electronic products manufacturing ...................................
Electrical equipment, appliance, and component manufacturing ............
Transportation equipment manufacturing .................................................
Furniture and related product manufacturing ...........................................
Miscellaneous manufacturing ...................................................................
Waste management and remediation ......................................................
Hospitals/Nursing and residential care facilities .......................................
Personal and laundry services .................................................................
Residential/private households .................................................................
Non-Residential (Commercial) .................................................................
a North
American Industry Classification System.
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B. Where can I get a copy of this
document and other related
information?
In addition to being available in the
docket, an electronic copy of this
proposal will also be available on the
World Wide Web. Following signature
by the EPA Administrator, a copy of this
action will be posted on the EPA’s New
Source Review (NSR) Web site, under
Regulations & Standards, at https://
www.epa.gov/nsr.
C. What should I consider as I prepare
my comments for EPA?
1. Submitting CBI. Do not submit this
information to EPA through https://
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www.regulations.gov or e-mail. Clearly
mark the part or all of the information
that you claim to be CBI. For CBI
information in a disk or CD ROM that
you mail to EPA, mark the outside of the
disk or CD ROM as CBI and then
identify electronically within the disk or
CD ROM the specific information that is
claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed except in
accordance with procedures set forth in
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40 CFR part 2. Send or deliver
information identified as CBI only to the
following address: Roberto Morales,
OAQPS Document Control Officer
(C404–02), U.S. EPA, Research Triangle
Park, NC 27711, Attention Docket ID
No. EPA–HQ–OAR–2009–0517.
2. Tips for preparing your comments.
When submitting comments, remember
to:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
• Follow directions—The agency may
ask you to respond to specific questions
or organize comments by referencing a
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Code of Federal Regulations (CFR) part
or section number.
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns, and suggest
alternatives.
• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline identified.
D. How can I find information about a
possible public hearing?
People interested in presenting oral
testimony or inquiring if a hearing is to
be held should contact Ms. Pamela S.
Long, New Source Review Group, Air
Quality Policy Division (C504–03), U.S.
EPA, Research Triangle Park, NC 27711,
telephone number (919) 541–0641. If a
hearing is to be held, persons interested
in presenting oral testimony should
notify Ms. Long at least 2 days in
advance of the public hearing. Persons
interested in attending the public
hearing should also contact Ms. Long to
verify the time, date, and location of the
hearing. The public hearing will provide
interested parties the opportunity to
present data, views, or arguments
concerning these proposed rules.
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E. How is the preamble organized?
The information presented in this
preamble is organized as follows:
I. Preamble Glossary of Terms and
Abbreviations
II. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document
and other related information?
C. What should I consider as I prepare my
comments for EPA?
D. How can I find information about a
possible public hearing?
E. How Is the preamble organized?
III. Overview of Proposed Rule
IV. Background
A. What are greenhouse gases and their
sources?
B. What are the general requirements of the
PSD program?
C. What are the general requirements of the
title V operating permits program?
D. What is the current treatment of GHG
emissions under the title V and PSD
programs and what future actions may
change that treatment?
V. What would be the administrative burdens
of implementing PSD and title V at the
current permitting thresholds?
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A. PSD Implications
B. Title V Implications
C. ANPR Comments
VI. What is the legal rationale for this
proposed Action?
A. ‘‘Absurd Results’’ Doctrine
B. ‘‘Administrative Necessity’’ Doctrine
C. Step-by-Step Process
D. What were the ANPR comments
received on GHG tailoring options for
regulating GHG emissions under PSD
and title V?
VII. Streamlining options and tools To
address the administrative burdens of
PSD and title V for GHGs
A. Permit Streamlining Techniques for PSD
and Title V
B. Implementation of Streamlining
Techniques and Overall Approach To
Administering PSD and Title V Programs
C. Strategies for Obtaining GHG Reductions
From Sources Under the Proposed GHG
Permit Thresholds
VIII. Description and Rationale of Proposed
Action
A. Proposed Permitting Thresholds for
GHGs
B. What is the definition of the GHG
pollutant for the proposed permitting
thresholds?
C. What is the rationale for selecting the
proposed GHG permitting thresholds for
PSD?
D. What is the rationale for selecting the
proposed first-phase GHG permitting
threshold for title V?
E. how will EPA assess the GHG permitting
thresholds in the first phase of the
tailoring program, and how will epa
develop the second phase?
IX. What would be the economic impacts of
the proposed rule?
A. What entities are affected by this rule?
B. What are the estimated benefits to small
sources due to regulatory relief?
C. What are the economic impacts of this
rulemaking?
D. What are the costs of the proposed rule
for society?
X. What implementation issues are related to
this proposal?
A. CAA Provisions Concerning SIP
Requirements for PSD Programs, State
Submittal Requirements, and EPA
Action
B. What PSD-Specific implementation
considerations are there?
C. What title V-Specific implementation
issues are there?
D. GHGs and title V permit fees
E. Implementation assistance and support
XI. Statutory and Executive Order Reviews
A. Executive Order 12866—Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
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
Concerning Regulations That
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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. Determination Under Section 307(d)
XII. Statutory Authority
III. Overview of Proposed Rule
EPA is proposing to tailor the major
source applicability thresholds for GHG
emissions under the PSD and title V
programs of the CAA by setting firstphase levels under both programs,
setting a first-phase PSD significance
level 1 for GHG emissions, undertaking
efforts to streamline administrability of
the programs, and committing to an
assessment of administrability within 5
years and a second-phase rulemaking
within 6 years.
This proposal is necessary because
EPA expects soon to promulgate
regulations under the CAA to control
GHG emissions from light-duty motor
vehicles and, as a result, trigger PSD and
title V applicability requirements for
GHG emissions. When the light-duty
vehicle rule is finalized, the GHGs
subject to regulation under that rule
would become immediately subject to
regulation under the PSD program,
meaning that from that point forward,
prior to constructing any new major
source or major modifications that
would increase GHGs, a source owner
would need to apply for, and a
permitting authority would need to
issue, a permit under the PSD program
that addresses these increases.
Similarly, for title V it would mean that
any new or existing source exceeding
the major source applicability level for
those regulated GHGs, if it did not have
a title V permit already, would have 1
year to submit a title V permit
application.
If PSD and title V requirements apply
at the applicability levels provided
under the CAA, many small sources
would be burdened by the costs of
individualized PSD control technology
requirements and permit applications.
In addition, State permitting authorities
would be paralyzed by enormous
numbers of these permit applications;
the numbers are orders of magnitude
greater than the current inventory of
permits and would vastly exceed the
current administrative resources of the
permitting authorities. Based on the
long-established judicial doctrines of
1 ‘‘Significant levels’’ for regulated NSR
pollutants are commonly called ‘‘significance
levels’’ or ‘‘significance thresholds,’’ and these
terms are used interchangeably for purposes of this
proposed action.
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‘‘absurd results’’ and ‘‘administrative
necessity,’’ this proposed rule would
phase in PSD and title V applicability.
As the first phase, this rule would
establish applicability thresholds for
both the PSD and title V programs at the
level of 25,000 tpy CO2e, and would
establish a PSD significance level of
between 10,000 and 25,000 tpy CO2e.
This rule also marks the beginning of a
concerted effort by EPA to streamline
administration of the PSD and title V
programs as much as possible and as
quickly as possible. In addition, EPA
commits that, within 5 years of
promulgating the first phase, EPA will
conduct a study of the permitting
authorities’ ability to administer the
programs going forward, and then,
within a year, conduct rulemaking for
the second phase of the program. This
second phase will either confirm the
first-phase permitting levels or establish
revised ones or other streamlining
techniques. EPA also proposes to
identify as the pollutant subject to PSD
and title V for applicability purposes the
group of up to six GHG emissions, each
one weighted for its global warming
potential, that are included in
regulations for their control under the
CAA. EPA also proposes to conform its
action on PSD State implementation
plans (SIPs) and title V programs to
match the proposed Federal
applicability requirements.
More specifically, following this
overview, section IV of this preamble
provides background information as to
the nature of GHG emissions and the
general requirements of the PSD and
title V programs. Currently, PSD applies
to sources that emit at least 100 or 250
(depending on the source category) tpy
of pollutants subject to regulation under
the CAA, and title V generally applies
to sources that emit at least 100 tpy of
pollutants subject to regulation under
the CAA. Currently, PSD and title V
requirements apply on the basis of
emissions applicability thresholds that
are pollutant-specific mass emissions
rates expressed in tpy. Under PSD,
construction of a stationary source that
has the potential to emit (PTE) a
regulated NSR pollutant in an amount
exceeding 100 or 250 tpy (depending on
the source category) (the ‘‘major
stationary source’’ threshold, in the
terminology of EPA regulations) triggers
PSD permitting requirements. PSD
permitting requirements are also
triggered if a major stationary source
undertakes a modification that is
projected to increase emissions of a
regulated NSR pollutant above an
emissions threshold (the ‘‘significance
level’’). For any particular pollutant,
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this level is zero unless and until EPA
establishes one on the basis of de
minimis emissions or administrative
necessity. Under title V, a source with
emissions exceeding a ‘‘major source’’
emissions threshold—generally 100 tpy
on a PTE basis—triggers title V
permitting requirements.
It should be noted that, as further
explained in the background section,
there are no geographic areas currently
designated ‘‘nonattainment’’ for GHG
pollutants; as a result, this action affects
only the PSD program, and we are not
proposing to amend the ‘‘nonattainment
NSR’’ provisions of our major NSR
program at this time, nor are we
proposing to amend any provisions that
affect minor NSR permitting.
Section IV of this preamble further
describes the current and expected
future treatment of GHG emissions for
applicability purposes under those PSD
and title V programs. In particular,
section IV describes the light-duty
motor vehicle rule, which EPA recently
proposed and expects to promulgate by
the end of March 2010, and which will
control GHG emissions from certain
mobile sources. Under EPA’s current
interpretation of PSD and title V
applicability requirements,
promulgation of this motor vehicle rule
will trigger the applicability of PSD and
title V requirements for stationary
sources that emit GHGs.
In section V of this preamble, EPA
describes the administrative burdens on
permitting authorities if the
requirements of PSD and title V
programs are triggered without having
this tailoring rule in place. In short,
without this tailoring rule, the
administrative burdens would be
immense, and they would immediately
and completely overwhelm the
permitting authorities. Without this
tailoring rule, permitting authorities
would receive approximately 40,000
PSD permit applications each year—
currently, they receive approximately
300—and they would be required to
issue title V permits for approximately
some six million sources—currently,
their title V inventory is some 15,000
sources. These increases are measured
in orders of magnitude. We estimate the
additional resource burdens in full-time
equivalents (FTEs) and time delays in
processing permits, but the sheer
numbers of additional permits by
themselves paint the picture of the
overwhelming administrative burdens.
In section VI of this preamble, we
describe the legal rationale for this
tailoring rule. The judicial doctrine of
‘‘absurd results’’ authorizes departure
from a literal application of statutory
provisions if it would produce a result
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that is inconsistent with other statutory
provisions or congressional intent, and
particularly one that would undermine
congressional purposes. The judicial
doctrine of ‘‘administrative necessity’’
authorizes an agency to depart from
statutory requirements if the agency can
demonstrate that the statutory
requirements, as written, are impossible
to administer. However, the agency
must first attempt to mitigate
administrative problems through
techniques consistent with the statutory
requirements, and, if variance from the
statutory requirements nevertheless is
necessary to allow administrability, the
variance must be limited as much as
possible.
As discussed in section VI of this
preamble, to apply the statutory PSD
and title V applicability thresholds to
sources of GHG emissions would bring
tens of thousands of small sources and
modifications into the PSD program
each year, and millions of small sources
into the title V program. This
extraordinary increase in the scope of
the permitting programs, coupled with
the resulting burdens on the small
sources and on the permitting
authorities, were not contemplated by
Congress in enacting the PSD and title
V programs. Moreover, the
administrative strains would lead to
multi-year backlogs in the issuance of
PSD and title V permits, which would
undermine the purposes of those
programs. Sources of all types—whether
they emit GHGs or not—would face long
delays in receiving PSD permits, which
Congress intended to allow construction
or expansion. Similarly, sources would
face long delays in receiving title V
permits, which Congress intended to
promote enforceability. For these
reasons, the absurd results doctrine
applies to avoid a literal application of
the thresholds.
By the same token, the impossibility
of administering the permit programs
brings into play the administrative
necessity doctrine. This doctrine also
justifies EPA to avoid a literal
application of the threshold provisions.
Instead, these doctrines authorize
EPA to apply the PSD and title V
applicability provisions through a
phased program. The first phase would
establish the applicability thresholds at
the 25,000-tpy levels and vigorously
develop streamlining measures that
would facilitate applying PSD and title
V on a broader scale with overburdening
sources and administrators. In this
manner, the phased approach reconciles
the language of the statutory provisions
with the results of their application and
with congressional intent.
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In section VII of this preamble, we
describe the streamlining techniques—
short of limiting the applicability of PSD
and title V to higher-emitting sources—
that may be available to improve
administrability. These techniques
range from defining ‘‘potential to
emit’’—which is the basis for
calculating the statutory thresholds—to
be closer to actual emissions, to general
permits and presumptive best available
control technology (BACT), which is the
principal control requirement under the
PSD program. Although these
techniques offer promise over the long
term to improve administrability, they
cannot be in place by March 2010, when
we expect PSD and title V requirements
to be triggered for GHG emitters, or
within a several-year period thereafter.
Accordingly, this tailoring rule is
necessary at this time.
In section VIII of this preamble, we
describe in detail our proposed tailoring
rule. For the PSD program, we are
proposing to establish, as the first phase,
the GHG ‘‘major stationary source’’
emissions applicability threshold level
at 25,000 tpy on a CO2e basis. That is,
sources that emit at this level or higher
would be considered ‘‘major stationary
sources’’ and therefore would become
subject to PSD requirements when they
construct or modify. We are also
proposing to establish in this first phase
a PSD ‘‘significance level’’ emissions
rate for GHGs and are proposing a range
for that value of 10,000 to 25,000 tpy
CO2e for comment. The ‘‘significance’’
level is important for determining
whether existing sources that make
physical or operational changes become
subject to PSD and for determining
whether sources that are subject to PSD
for other pollutants are also subject to
PSD for their GHG emissions.
As further described in section VIII of
this preamble, for the title V operating
permits program, we are also proposing
to establish the GHG emissions
applicability threshold level at 25,000
tpy CO2e for this first phase. That is,
sources that emit at this level or higher
would be considered ‘‘major sources’’
and therefore would become subject to
title V requirements.
As further described in section VIII of
this preamble, as an integral part of the
tailoring rule, EPA proposes to commit
to complete, within 5 years of a final
rule, a study to evaluate the actual
administrative burden resulting from
the proposed GHG permitting
thresholds and possible other
thresholds, and the progress of
developing streamlining techniques and
augmentation of permitting authorities’
resources. In addition, EPA commits to
propose and promulgate a rulemaking—
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informed by the study—within 6 years
from the effective date of a final version
of this rulemaking (i.e., 1 year from the
completion of the study) that would
establish the second phase, which
would either reaffirm the GHG
permitting thresholds, promulgate
alternative thresholds, adopt other
streamlining techniques, and/or take
other action consistent with the goal of
expeditiously meeting CAA
requirements in light of the
administrative burden that remains at
that time.
During this first phase of the tailoring
program, EPA proposes to make a
concerted effort to assess and
implement streamlining options, tools,
and guidance—some of which we
describe in section VII of this
preamble—to reduce the administrative
burden on permitting authorities when
implementing PSD and title V for GHGs.
EPA proposes to undertake as many of
these streamlining actions as possible
and to do so as quickly as possible. In
addition, for larger sources that would
be subject to PSD and title V
requirements during the first phase,
EPA intends to work closely with the
stakeholders to develop efficient
methods for implementing those
requirements. For smaller sources for
which PSD and title V requirements
would not apply during the first phase
due to the increase in the major source
applicability threshold, EPA intends to
identify cost-effective opportunities
available as soon as possible to achieve
GHG reductions through means other
than PSD and title V (e.g., energy
efficiency and other appropriate
measures).
Section VIII of this preamble further
describes our proposal to define the
relevant pollutants as the group of up to
six GHG emissions that have been
regulated for control, calculated on the
basis of global warming potential
(GWP).2
Section IX of this preamble describes
the burden and economic impacts of the
proposed rule.
Section X of this preamble discusses
implementation issues related to this
proposal. These include conforming
2 The Intergovernmental Panel on Climate Change
(IPCC) describes GWP as an index, based upon
radiative properties of well-mixed GHGs, measuring
the radiative forcing of a unit mass of a given wellmixed greenhouse gas in the present-day
atmosphere integrated over a chosen time horizon,
relative to that of CO2. The GWP represents the
combined effect of the differing times these gases
remain in the atmosphere and their relative
effectiveness in absorbing outgoing thermal infrared
radiation. (Intergovernmental Panel on Climate
Change (IPCC), Glossary of Terms used in the IPCC
Fourth Assessment Report, WG1). https://
www.ipcc.ch/
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EPA approval of the PSD programs in
SIPs and EPA approval of the State title
V programs to be consistent with the
proposed applicability threshold levels.
By way of background, as soon as EPA
promulgates a rule regulating for control
of GHG emissions—which we expect to
occur with the proposed light-duty
motor vehicle rule, scheduled for
promulgation at the end of March
2010—stationary sources will become
subject to PSD and title V requirements.
The major source thresholds for PSD
and title V, significance level for PSD,
and identification of GHGs subject to
PSD and title V as proposed in this
tailoring rule would each take effect
immediately in the Federal PSD
program (codified at 40 CFR 52.21) and
in the Federal operating permits
program (codified at 40 CFR 71), as
applicable. To conform EPA action on
PSD SIPs and State title V programs,
EPA intends to limit its previous
approval of those SIPs and title V
programs to cover only the permitting of
sources of GHG emissions at or above
the proposed threshold levels. EPA will
take no action on—that is, EPA will not
disapprove—the PSD SIPs and title V
programs to the extent they require
permitting of GHG emitters at levels
below the proposed thresholds. EPA
proposes to take this action by virtue of
its authority to reconsider its previous
regulatory actions. Section X of this
preamble also explains how we propose
to address the treatment of GHGs in the
fee programs under title V.
IV. Background
A. What are greenhouse gases and their
sources?
Gases that trap heat in the atmosphere
are often called GHGs. Some GHGs such
as carbon dioxide (CO2) are emitted to
the atmosphere through natural
processes as well as human activities.
Other gases, such as fluorinated gases,
are created and emitted solely through
human activities. The primary GHGs of
concern directly emitted by human
activities include CO2, methane (CH4),
nitrous oxide (N2O), hydrofluorocarbons
(HFCs), perfluorocarbons (PFCs), and
sulfur hexafluoride (SF6). These six
primary GHGs will, for the purposes of
this proposal, be referred to collectively
as ‘‘the six primary GHGs.’’ These six
gases, once emitted, remain in the
atmosphere for decades to centuries.
Thus, they become well-mixed globally
in the atmosphere and their
concentrations accumulate when
emissions exceed the rate at which
natural processes remove them from the
atmosphere. The heating effect caused
by the human-induced buildup of GHGs
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in the atmosphere is very likely the
cause of most of the observed global
warming over the last 50 years. A
detailed explanation of climate change
and its impact on health, society, and
the environment is included in EPA’s
technical support document for the
endangerment finding proposal (Docket
ID No. EPA–HQ–OAR–2009–0171–
0137).3
In the U.S., the combustion of fossil
fuels (e.g., coal, oil, gas) is the largest
source of CO2 emissions and accounts
for 80 percent of total GHG emissions.
More than half the energy-related
emissions come from large stationary
sources such as power plants, while
about a third come from transportation.
Of the six primary GHGs, four (CO2,
CH4, N2O, and HFCs) are emitted by
motor vehicles. Industrial processes
(such as the production of cement, steel,
and aluminum), agriculture, forestry,
other land use, and waste management
are also important sources of GHG
emissions in the U.S. These emissions
are inventoried at a national level by
EPA in the Inventory of U.S.
Greenhouse Gas Emissions and Sinks.4
Different GHGs have different heattrapping capacities. It is useful to
compare them to each other through the
use of the CO2e metric. This metric
incorporates both the heat-trapping
ability and atmospheric lifetime of each
GHG and can be used to adjust the
quantities, in tpy, of all GHGs relative
to the GWP of CO2. When quantities of
the different GHGs are multiplied by
their GWPs, the different GHGs can be
summed and compared on a CO2e basis.
Depending on which GWP values are
used, the calculated GHG emissions on
a CO2e basis will vary. Throughout this
preamble, we are applying the GWP
values established by the
Intergovernmental Panel on Climate
Change (IPCC) in its Second Assessment
Report (SAR) (IPCC 1996).5 For
example, CH4 has a GWP of 21, meaning
each ton of CH4 emissions would have
21 times as much impact on global
warming over a 100-year time horizon
as 1 ton of CO2 emissions. Thus, on the
basis of heat-trapping capability, 1 ton
3 ‘‘Document for Endangerment and Cause or
Contribute Findings for Greenhouse Gases under
Section 202(a) of the Clean Air Act,’’ Climate
Change Division, Office of Atmospheric Programs,
U.S. Environmental Protection Agency,
Washington, DC. April 17, 2009.
4 For additional information about the Inventory
of U.S. Greenhouse Gas Emissions and Sinks, and
for more information about GHGs, climate change,
climate science, etc., see EPA’s climate change Web
site at https://www.epa.gov/climatechange/.
5 ‘‘Inventory of U.S. Greenhouse Gas Emissions
and Sinks: 1990–2007,’’ U.S. Environmental
Protection Agency, EPA 430–R–09–004, April 15,
2009. Table 1–2, p. 1–6. https://www.epa.gov/
climatechange/emissions/usinventoryreport.html.
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of CH4 would equal 21 tons of CO2e.
The GWPs of the six primary GHGs
range from 21 (for CH4) up to 23,900 (for
SF6). Aggregating all GHGs on a CO2e
basis at the source level allows a facility
to evaluate its total GHG emissions
contribution based on a single metric.
For a complete list of the applicable
GWP values for each GHG, please refer
to EPA’s Inventory of U.S. Greenhouse
Gas Emissions and Sinks.
may refer to these levels as the 100/250tpy thresholds. A new source with a
PTE at or above the applicable ‘‘major
stationary source threshold’’ amount is
subject to major NSR. These limits
originate from section 169 of the CAA,
which applies PSD to any ‘‘major
emitting facility’’ 6 and defines the term
to include any source with a PTE of 100
or 250 tpy, depending on source
category.
B. What are the general requirements of
the PSD program?
b. Major Modifications
1. Overview of the PSD Program
The PSD program is a preconstruction
review and permitting program
applicable to ‘‘new major stationary
sources’’ and ‘‘major modifications’’ at
existing major stationary sources, in the
terminology of EPA’s implementing
regulations. The PSD program applies in
areas meeting the health-based National
Ambient Air Quality Standards
(NAAQS) or for which there is
insufficient information to determine
whether they meet the NAAQS
(‘‘unclassifiable’’ areas). The PSD
program is contained in part C of title
I of the CAA. The ‘‘nonattainment NSR’’
program applies in areas not meeting
the NAAQS and in the Ozone Transport
Region, and is implemented under the
requirements of part D of title I of the
CAA. Collectively, we also commonly
refer to these two programs as the major
NSR program. The governing EPA rules
are contained in 40 CFR 51.165, 51.166,
52.21, 52.24, and part 51, appendices S
and W. There is no NAAQS for CO2 or
any of the other primary GHGs, nor does
EPA plan to promulgate one; therefore,
we do not anticipate that the
‘‘nonattainment’’ major NSR program
will apply to GHGs.
The applicability of the PSD program
to a particular source must be
determined in advance of construction
or modification and is pollutantspecific. The primary criterion in
determining PSD applicability is
whether the proposed project is
sufficiently large (in terms of its
emissions) to be a major stationary
source or major modification, both of
which are described below.
a. Major Stationary Sources
Under PSD, a ‘‘major stationary
source’’ is any source type belonging to
a specified list of 28 source categories
which emits or has a PTE of 100 tpy or
more of any pollutant subject to
regulation under the CAA, or any other
source type which emits or has the
potential to emit such pollutants in
amounts equal to or greater than 250
tpy. See, e.g., 40 CFR 52.21(b)(1). We
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PSD applies to not only new
construction but also to existing sources
that undertake a ‘‘major modification,’’
which is defined in terms of the
following three criteria:
(1) A physical change in, or change in
the method of operation of, a ‘‘major
stationary source’’ must occur;
(2) The change must result in an
increase in emissions that is
‘‘significant,’’ that is, equal to or above
the significance level defined for the
pollutant in question, e.g., in 40 CFR
52.21(b)(23)); and
(3) The increase in emissions
resulting from the change must be a
significant net emissions increase. In
other words, when the increase from the
project is added to other
contemporaneous increases or decreases
in actual emissions at the source, the net
emissions increase must be significant
(equal to or above the significance level
defined, e.g., in 40 CFR 52.21(b)(23)).
Generally, significance levels for PSD
are pollutant-specific emissions rates.
For example, the significance level for
emissions of nitrogen oxides (NOX) is 40
tpy. See, e.g., 40 CFR 52.21(b)(23)(i).
However, for a regulated NSR pollutant
for which no specific significance level
is listed, PSD applies to ‘‘any increase.’’
See, e.g., 40 CFR 52.21(b)(23)(ii). Thus,
if GHGs were to become subject to
regulation and PSD review, and no
significance levels for GHGs had been
established, the default value would be
‘‘zero.’’
EPA has promulgated significance
levels for criteria pollutants and certain
other pollutants, which EPA generally
based on levels that represent a de
minimis contribution to air quality
problems. For example, for certain
pollutants regulated under the new
source performance standards (NSPS),
EPA generally based significance levels
at 20 percent of the NSPS. These
concentrations were compared to
available health and welfare data to
assure that significant adverse effects
6 EPA’s regulations employ the term ‘‘major
stationary source’’ in lieu of ‘‘major emitting
facility.’’ e.g., 40 CFR 52.21(a)(2)(i), (b)(1)(i).
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were avoided.7 To this point, EPA has
not established a significance level for
GHGs, and we currently do not have an
adequate supporting record to establish
a similar health and welfare-based de
minimis level for significance for GHGs.
2. General Requirements for PSD
Under the PSD program, one of the
principal requirements is that a new
major source or major modification
must apply BACT, which is determined
on a case-by-case basis taking into
account, among other factors, the cost
and effectiveness of the control. EPA
has developed a ‘‘top-down’’ approach
for BACT review which involves a
decision process that includes
identification of all available control
technologies, elimination of technically
infeasible options, ranking of remaining
options by control and cost
effectiveness, and then selection of
BACT. Under PSD, once a source is
determined to be major for any
regulated pollutant, a BACT review is
performed for each attainment pollutant
whose emissions exceed its PSD
significance level as part of new
construction or modification projects at
the source.
In addition to performing a BACT
review, the source must analyze the
impact of the project on ambient air
quality to assure that no violation of any
NAAQS or PSD increments will result,
and must analyze impacts on soil,
vegetation, and visibility. Sources or
modifications that would impact Class I
areas (e.g., national parks) may be
subject to additional requirements to
protect air quality related values
(AQRVs) that have been identified for
such areas. Under PSD, if a source
proposes to locate within 100 kilometers
of a Class I area, the Federal Land
Manager (FLM) is notified and is
responsible for evaluating a source’s
projected impact on the AQRVs and
recommending either approval or
disapproval of the source’s permit
application based on anticipated
impacts. There are currently no NAAQS
or PSD increments established for
GHGs, and therefore these PSD
requirements would not apply to GHG
emissions sources, even when PSD is
triggered for GHG emissions sources.
However, as noted previously, if PSD is
triggered for a GHG emissions source,
all regulated NSR pollutants which the
new source emits in significant amounts
would be subject to PSD requirements.
7 EPA established significance levels for
hazardous air pollutants on a similar basis, but
subsequently, in the 1990 Clean Air Act
Amendments, Congress mooted them by exempting
hazardous air pollutants from PSD, under CAA
section 112(b)(6).
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Therefore, if a facility triggers review for
regulated NSR pollutants that are nonGHG pollutants for which there are
established NAAQS or increments, the
air quality, additional impacts, and
Class I requirements would apply to
those pollutants.
When the reviewing authority reaches
a preliminary decision to authorize
construction of a proposed new major
source or major modification, it must
provide notice of the preliminary
decision and an opportunity for
comment by the general public,
industry, and other interested persons.
After considering and responding to the
comments, the reviewing authority may
issue a final determination on the
construction permit in accordance with
the PSD regulations.
Usually NSR permits are issued by
State or local air pollution control
agencies. In these cases, State and local
air pollution control agencies may have
their own permit programs that are
approved by EPA in the SIP or they may
be delegated the authority to issue
permits on behalf of EPA. In some areas,
the EPA issues the permits.
3. Minor NSR Program
The permitting program for minor
stationary sources is addressed by
section 110(a)(2)(C) of the CAA. We
commonly refer to this program as the
minor NSR program. A minor stationary
source means a source whose PTE is
lower than the major source
applicability threshold for a particular
pollutant as defined in the applicable
nonattainment major NSR program or
PSD program. As with nonattainment
NSR requirements, the CAA does not
require that minor source programs
apply to GHGs because there are no
NAAQS for GHGs.
C. What are the general requirements of
the title V operating permits program?
1. Overview of Title V
The title V operating permits program
was added to the CAA by Congress in
1990. The operating permits program
requirements under title V are intended
to improve sources’ compliance with
the requirements of the CAA. In
summary, the title V program requires
major sources (generally defined as
sources that actually emit or have the
potential to emit 100 tpy) and certain
other sources to obtain operating
permits that: Consolidate all CAA
requirements into a single document;
provide for review of these documents
by EPA, States, and the public; and
require permit holders to track, report,
and annually certify their compliance
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status with respect to their permit
requirements.
Title V will be triggered for GHG
emissions when EPA regulates them for
control under another provision of the
CAA. Section 502(a) of the Act sets forth
the sources required to obtain operating
permits under title V. These sources
include: (1) Any affected source subject
to acid rain rules under title IV of the
Act; (2) any major source; (3) any source
required to have a permit under part C
or D (PSD/NSR) of title I of the Act; (4)
‘‘any source subject to section 111
[NSPS] or section 112 [NESHAP];’’ and
(5) any other source designated by rule.
See also 40 CFR 70.3(a) and 71.3(a). The
requirements of section 502(a) are
primarily implemented through the
operating permit program rules at 40
CFR part 70, which sets out the
minimum requirements for title V
operating permit programs administered
by State, local, and tribal permitting
authorities (57 FR 32261; July 21, 1992);
and part 71, the Federal operating
permit program requirements that apply
where EPA or a delegate agency
authorized by EPA to carry out a Federal
permit program is the title V permitting
authority (61 FR 34228, July 1, 1996).
Title V generally does not add new
substantive requirements for pollution
control, but it does require that each
permit contain all of a facility’s
‘‘applicable requirements’’ under the
CAA, and that certain procedural
requirements be followed, especially
with respect to compliance with these
requirements. ‘‘Applicable
requirements’’ for title V purposes
include all stationary source
requirements, but do not include mobile
source requirements.
2. Title V Permit Requirements
When a source becomes subject to
title V, it must apply for a permit within
1 year of the date it became subject. The
application must include identifying
information, a description of emissions
and other information necessary to
determine applicability of CAA
requirements, identification and
certification of the source’s compliance
status with these requirements
(including a schedule to come into
compliance for any requirements for
which the source is currently out of
compliance), a statement of the methods
for determining compliance, and other
information. The permitting authority
then uses this information to issue the
source a permit to operate, as
appropriate. A title V source may not
operate without a permit, except that if
it has submitted a complete application,
the submission acts as a ‘‘shield’’ that
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authorizes it to operate while awaiting
issuance of its permit.
Title V permits must contain the
following main elements: (1) Emissions
standards to assure compliance with all
applicable requirements; (2) a duration
of no more than 5 years, after which the
permit must be renewed; (3) monitoring,
recordkeeping, and reporting
requirements necessary to assure
compliance, including a semiannual
report of all required monitoring and a
prompt report of each deviation from a
permit term; (4) provisions for payment
of permit fees as established by the
permitting authority such that total fees
collected are adequate to cover the costs
of developing and implementing the
program; and (5) a requirement for an
annual compliance certification by a
responsible official at the source. An
additional specific monitoring
requirement, compliance assurance
monitoring (CAM), also applies to some
emissions units operating at major
sources with title V permits. The CAM
rule requires source owners to design
and conduct monitoring of the operation
of add-on control devices used to
control emissions from moderately large
emissions units. Source owners use the
monitoring data to evaluate, verify, and
certify the compliance status for
applicable emissions limits. The CAM
rule is implemented in conjunction with
the schedule of the operating permits
program. While these are the main
elements relevant to a discussion of
GHGs, there are numerous other permit
content requirements and optional
elements, as set forth in the title V
regulations at 40 CFR 70.6.
In addition to the permit content
requirements, there are procedural
requirements that permitting authorities
(typically States) must follow in issuing
title V permits, including (1)
determining and notifying the applicant
that its application is complete; (2)
providing public notice and a 30-day
public comment period on the draft
permit, as well as the opportunity for a
public hearing; (3) giving notice to EPA
and affected States; and (4) preparing
and providing to any requester a
statement of the legal and factual basis
of the draft permit. The permitting
authority must take final action on
permit applications within 18 months of
receipt. EPA also has 45 days from
receipt of a proposed permit to object to
its issuance, and citizens have 60 days
to petition EPA to object. Permits may
also need to be revised or reopened if
new requirements come into effect or if
the source makes changes that conflict
with, or necessitate changes to, the
current permit. Permit revisions and
reopenings follow procedural
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requirements which vary depending on
the nature of the necessary changes to
the permits.
D. What is the current treatment of GHG
emissions under the title V and PSD
programs and what future actions may
change that treatment?
This section of the preamble describes
the current treatment of GHG emissions
under the PSD and title V programs—
under which GHG emissions are not
included for purposes of determining
applicability—including recent
regulatory and legal developments
related to this action, and then describes
what future action may change that
treatment.
1. Regulation of GHGs Under the CAA
a. The Massachusetts U.S. Supreme
Court Decision
On April 2, 2007, in Massachusetts v.
EPA, 549 U.S. 497 (2007), the U.S.
Supreme Court held that GHGs are air
pollutants covered by the CAA.
Therefore, the Court further held that
GHG emissions are subject to CAA
section 202(a) under which the
Administrator must determine whether
or not emissions of GHGs from new
motor vehicles or motor vehicle engines
cause or contribute to air pollution
which may reasonably be anticipated to
endanger public health or welfare, or
whether the science is too uncertain to
make a reasoned decision. This decision
resulted from a petition for rulemaking
under section 202(a) filed by more than
a dozen environmental, renewable
energy, and other advocacy
organizations. As a result of this
decision, EPA decided to issue an
advance notice of proposed rulemaking
(ANPR), discussed later in this
preamble, soliciting comment on how
GHG emissions should be regulated
under the CAA.
b. The EPA ANPR
On July 30, 2008, EPA published an
ANPR in the Federal Register entitled,
‘‘Regulating Greenhouse Gas Emissions
under the CAA.’’ 73 FR 44354, July 30,
2008. This ANPR presented information
relevant to, and solicited public
comment on how to respond to, the U.S.
Supreme Court’s decision in
Massachusetts v. EPA, holding that
GHGs are air pollutants subject to the
CAA. The notice reviewed the various
CAA provisions (including the PSD and
title V requirements) that may be
applicable to sources of GHGs,
examined the issues that regulating
GHGs under those provisions may raise,
provided information regarding
potential regulatory approaches and
technologies for reducing GHG
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emissions, and raised issues relevant to
possible legislation and the potential for
overlap between legislation and CAA
regulation.
In addition, the notice described and
solicited comment on petitions the EPA
had received to regulate GHG emissions
from ships, aircraft, and nonroad
vehicles such as farm and construction
equipment. Finally, the notice discussed
several other actions concerning
stationary sources for which EPA has
received comment regarding the
regulation of GHG emissions, including
promulgation of performance standards
or guidelines under CAA section 111 for
new and existing sources in various
source categories. The EPA included
options for phasing in the PSD program
and title V programs to mitigate burdens
that would occur if GHGs were to be
regulated under the CAA and solicited
comments on those actions. Section V.C
of this preamble summarizes some of
the substantive comments received on
the ANPR. In issuing the ANPR, EPA
made clear that it believed that the best
way to address the problems posed by
GHG emissions would be through
legislation directly addressing GHG
emissions, rather than through use of
the tools in the CAA.
2. Current Applicability of the PSD
Program to Sources of GHG Emissions
As explained earlier in this preamble,
EPA treats sources as subject to PSD
requirements only if they emit
‘‘regulated NSR pollutants’’ at specified
threshold levels. Currently, EPA does
not consider GHG emissions to be
‘‘regulated NSR pollutants’’ under the
PSD program because GHG emissions
have not, thus far, been subject to
regulation requiring control under the
CAA. As discussed later in this
preamble, EPA is in the process of
reviewing its approach to PSD
applicability and is in the process of
developing a rulemaking—the light-duty
motor vehicle rule—that will trigger
PSD applicability for GHG emissions.
a. PSD Interpretive Memorandum
EPA is currently reconsidering the
PSD Interpretive Memorandum
(previously referred to as the ‘‘Johnson
Memorandum’’), which describes the
circumstances under which EPA
considers a pollutant subject to PSD
requirements. See memorandum (in
docket for this rulemaking) from
Administrator Stephen L. Johnson to
Regional Administrators, ‘‘EPA’s
Interpretation of Regulations that
Determine Pollutants Covered by
Federal Prevention of Significant
Deterioration (PSD) Permit Program,’’
December 18, 2008. The PSD
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Interpretive Memorandum followed a
decision by the Environmental Appeals
Board (EAB) in In re Deseret Power
Electric Cooperative, on November 13,
2008. PSD Appeal No. 07–03 (EAB
2008) (In re Deseret). There, the Board
remanded a PSD permit that EPA
Region VIII issued on August 30, 2007,
to Deseret Power Electric Cooperative,
authorizing the latter to construct a new
waste-coal-fired electric generating unit
near its existing Bonanza Power Plant,
in Bonanza, Utah. The primary issue
before the Board was whether the
permit had to include BACT limits for
CO2, which depended on whether CO2
meets the definition of a ‘‘regulated NSR
pollutant’’ under 40 CFR 52.21(b)(50),
which in turn interprets the provisions
in CAA sections 165 and 169 that apply
the BACT requirement to ‘‘each
pollutant subject to regulation’’ under
the CAA. The Board rejected arguments
by the petitioner, the Sierra Club, that
the CAA compelled a broad
interpretation of the phrase ‘‘subject to
regulation,’’ which, according to the
petitioner, required EPA to apply BACT
to pollutants as long as they are subject
to monitoring and reporting
requirements. Currently, and since
1993, sources covered by the Acid Rain
program have been required to monitor
and report CO2 emissions pursuant to
the CAA. The Board also rejected the
view advanced by the EPA offices
involved in the case—Region VIII and
the Office of Air and Radiation—that
EPA had already established an
interpretation of ‘‘subject to regulation,’’
which was that this term authorized
BACT only for pollutants subject to
actual regulatory controls. Thus, the
Board remanded the permit to the
Region to ‘‘reconsider whether or not to
impose a CO2 BACT limit in light of the
‘subject to regulation’ definition under
the CAA.’’ In re Deseret, slip op. at 63.
On December 18, 2008, EPA’s thenAdministrator Stephen Johnson issued a
memorandum establishing an
interpretation clarifying the scope of the
PSD program under the CAA (the PSD
Interpretive Memorandum). This
memorandum interprets the definition
of ‘‘regulated NSR pollutant’’ to include
each pollutant subject to either a
provision in the CAA or regulation
adopted by EPA under the CAA that
requires actual control of emissions of
that pollutant, and to exclude pollutants
for which EPA regulations only require
monitoring or reporting.
On February 17, 2009, EPA
Administrator Lisa Jackson responded
to an amended petition for
reconsideration dated January 6, 2009,
filed on behalf of the Sierra Club and
other parties (petitioners), seeking
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reconsideration of the PSD Interpretive
Memorandum. In Administrator
Jackson’s response, she granted the
petition for reconsideration in order to
allow for public comment on issues
raised in the memorandum and stated
that EPA will also seek public comment
on any issues raised by the opinion of
the EAB with regard to the In re Deseret
decision (as discussed in the PSD
Interpretive Memorandum), to the
extent they are not coextensive with the
issues raised in the memorandum.
However, Administrator Jackson made
clear that the current interpretations in
the PSD Interpretive Memorandum
remain in effect during the
reconsideration process.
Because the PSD Interpretive
Memorandum concerns PSD
applicability, its reconsideration will
identify the circumstances under which
GHG emissions are treated as ‘‘subject to
regulation under the CAA’’ and,
therefore, are ‘‘regulated NSR
pollutants.’’ Once GHG emissions are
considered ‘‘regulated NSR pollutants,’’
PSD program requirements for existing
thresholds (100/250 tpy) are triggered.
The PSD Interpretive Memorandum
reconsideration is being addressed in a
proposed rule published in the Federal
Register on October 7, 2009 (74 FR
51535). Although several possible
triggering events may be considered in
that action, the latest of these events
would be the one that applies under
EPA’s current interpretation: A
nationwide rule controlling or limiting
GHG emissions. Presently, the EPA
expects that the first such rule will be
the light-duty motor vehicle rule.
b. Light-Duty Vehicle Rule
EPA is currently developing a rule to
regulate GHGs from mobile sources
under title II of the CAA (74 FR 24007;
May 22, 2009). EPA expects to
promulgate this rule by the end of
March 2010. As described in the PSD
Interpretive Memorandum, it is EPA’s
position that new pollutants become
subject to PSD and title V when a rule
controlling those pollutants is
promulgated (and even before that rule
takes effect). Accordingly, as soon as
GHGs become regulated under the lightduty motor vehicle rule, GHG emissions
will be considered pollutants ‘‘subject to
regulation’’ under the CAA and will
become subject to PSD and title V
requirements.
3. Current Applicability of Title V
Program to GHGs
CAA section 502(a) and related
definitions under sections 302 and 501,
require that specified types of sources
have operating permits. These include
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any source that emits or has a potential
to emit 100 tpy of a pollutant subject to
regulation (consistent with EPA’s policy
interpretation) 8, any source with a NSR
or PSD permit, any major source of a
hazardous air pollutant (HAP), any
source subject to acid rain requirements,
and certain minor sources subject to
section 111 or section 112 standards. As
with the PSD program, currently GHGs
are not considered to be subject to
regulation and have not been considered
to trigger title V applicability.
V. What would be the administrative
burdens of implementing PSD and title
V at the current permitting thresholds?
This section of the preamble describes
the additional administrative burdens
for the PSD and title V programs in
terms of staffing needs, time for
processing permits, and costs that
permitting authorities would incur if
sources of GHG emissions were to
trigger PSD and title V at the statutory
thresholds, which we shorthand as the
100/250-tpy thresholds. Evidence we
have collected to this point makes it
clear that if PSD and title V applicability
requirements are triggered at those
threshold levels, an enormous influx of
permits would occur—tens of thousands
of PSD permits and millions of title V
permits—which would create enormous
administrative burdens for permitting
authorities that would far exceed their
current capacity to administer the PSD
and title V programs. It is also worth
noting here that, under a scenario where
8 EPA included this policy interpretation that title
V addresses 100-tpy sources of ‘‘pollutants subject
to regulation’’ in a memorandum from Lydia
Wegman. Memorandum from Lydia N. Wegman,
Deputy Director, Office of Air Quality Planning and
Standards, U.S. EPA, ‘‘Definition of Regulated Air
Pollutant for Purposes of Title V’’ (Apr. 26, 1993).
EPA continues to maintain this interpretation. The
interpretation in this memorandum was based on:
(1) EPA’s reading of the definitional chain for major
source under title V, including the definition of ‘‘air
pollutant’’ under section 302(g) and the definition
of ‘‘major source’’ under 302(j); (2) the view that
Congress did not intend to require a variety of
sources to obtain title V permits if they are not
otherwise regulated under the Act, (see also CAA
section 504(a), providing that title V permits are to
include and assure compliance with applicable
requirements under the Act); and (3) promoting
consistency with the approach under the PSD
program. While the specific narrow interpretation
in the Wegman Memorandum of the definition of
‘‘air pollutant’’ in CAA section 302(g) is in question
in light of the Massachusetts v. EPA decision
(finding this definition to be ‘‘sweeping’’), EPA
believes the core rationale for its interpretation of
the applicability of title V remains sound. EPA
continues to maintain its interpretation, consistent
with CAA sections 302(j), 501, 502 and 504(a), that
title V applies to 100 tpy sources of pollutants
subject to regulation. This interpretation is based
primarily on the purpose of title V to include all
regulatory requirements applicable to the source in
one document to assure compliance, see, e.g., CAA
section 504(a), and to promote consistency with the
approach under the PSD program.
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State or local permitting authorities do
not have the resources to implement the
title V or PSD programs for GHG sources
at current CAA permitting applicability
thresholds, EPA may withdraw its
approval, in which case, EPA would
become the permitting authority and the
enormous resource requirements would
shift to EPA to implement these
programs.
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A. PSD Implications
We evaluated the additional
administrative burden and cost of
including GHG emitters in the PSD
program at the current 250-tpy major
source permitting threshold (but not at
100 tpy 9). To calculate the
administrative burdens and cost, we
first estimated the number of new
sources and modifications that would be
subject to PSD if GHGs were included
at the 250-tpy threshold level. We
developed these estimates of number of
new sources and modifications as part
of our GHG threshold data analyses. For
more information on these analyses, see
the technical support documents
entitled ‘‘Technical Support Document
for Greenhouse Gas Emissions
Thresholds Evaluation’’ and
‘‘Methodology for Estimating Modified
Sources That Would Be Subject to PSD
Permitting for GHGs;’’ Prepared by EPA
Staff; August 2009 in the docket for this
rulemaking.
After estimating the number of
affected facilities and sources, we then
evaluated the additional administrative
burden and cost of including these
numbers of new and modified GHG
emitters in the PSD program. Our
burden estimates are based on labor and
cost information from the existing
Information Collection Requests (ICRs)
for PSD programs.10
Based on our GHG threshold data
analysis, we estimate that almost 41,000
new and modified facilities per year
would be subject to PSD review, based
on the current rate of modifications at
major sources, if a GHG major source
threshold of 250 tpy CO2e were applied.
Compared to the 280 PSD permits
currently issued per year, this would be
an increase in permits of more than 140fold.
9 In light of time and resource constraints, we did
not calculate the additional administrative burden
and cost of including in the PSD program sources
that emit between 100 tpy and 250 tpy and that are
among the 28 source categories identified in CAA
section 169(l). Including these sources in the
calculation would increase the administrative
burdens and costs of implementing PSD at the
statutory thresholds.
10 ‘‘Summary of ICR-based Data Used to Estimate
Avoided Burden and Evaluate Resource
Requirements at Alternative GHG Permitting
Thresholds;’’ Prepared by EPA Staff; August 2009.
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We estimated the number of workload
hours and cost a permitting authority
would expend on each new source and
each modification. We based these
estimates on the workload hours and
cost for processing permits for new
sources of non-GHG emissions, which
we derived from labor and cost
information from the existing ICRs for
PSD programs. The ICRs show that
permitting authorities expend 301 hours
to permit a new or modified industrial
source. For more detail on information
used from the PSD ICR for this
evaluation, please refer to the docket for
this rulemaking.
We then made assumptions for
number of workload hours and costs for
new sources of GHG emissions. We
assumed that permitting new industrial
GHG sources that emit in excess of the
250-tpy threshold would be of
comparable complexity to permitting
non-GHG emitting industrial sources
that are subject to PSD. Thus, for these
sources, we assumed that permitting
authorities would expend the same
number of workload hours and costs, on
a per-permit basis, as they do for nonGHG emitting industrial sources. On the
other hand, for commercial and
residential GHG sources that emit GHGs
above the 250-tpy threshold (and as a
result would be subject to the
requirements of the PSD permitting
program at this threshold level), we
assumed that the workload hours and
cost for permitting these sources would
be significantly less than—only 20
percent of—the hours and cost
necessary to prepare and issue initial
PSD permits or permit modifications for
industrial GHG sources. This 20-percent
estimate amounts to 60 hours of
permitting authority time per residential
or commercial permit.
Based on these assumptions, the
additional annual permitting burden for
permitting authorities, on a national
basis, is estimated to be 3.3 million
hours at a cost of $257 million to
include all GHG emitters above the 250tpy threshold.
In addition to conducting our burden
analysis, we also reviewed summary
information from State and local air
permitting agencies regarding additional
resources and burden considerations if
GHG sources that emit above the 100/
250-tpy thresholds were subjected to the
PSD and title V programs. This
information covered 43 State and local
permitting agencies, representing
programs from different regions of the
country and various permitting program
sizes (in terms of geographic and source
population coverage). A summary of
this information can be found in the
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docket for this rulemaking.11 This
information showed significant burdens
projected by permitting agencies with
adding sources of GHG emissions in
terms of staffing, budget, and other
associated resource needs. Importantly,
the agencies based their analysis on the
assumption that, for purposes of
determining whether a source is major,
its emissions would be calculated on an
actual emissions (‘‘actuals’’) basis, and
not on a PTE basis. On an actuals basis,
the agencies estimated a 10-fold
increase in the number of permits.
Specifically, the agencies estimated
that:
• Assuming, again, that number of
permits was to increase by 10-fold
(based on actual emissions), the
resulting workload would require an
average of 12 more FTEs per permitting
authority at an estimated cost of $1
million/year;
• Without the additional FTEs, the
average processing time for a permit
would increase to 3 years, which is
three times the current average
processing time;
• Permitting authorities would need 2
years on average to add the necessary
staff;
• Permitting authorities would also
need, on average, eight additional
enforcement and judicial FTEs;
• Ninety percent of the permitting
agencies indicated that their staff would
need training in all aspects of permitting
for sources of GHG emissions; and
• A quarter of the permitting agencies
reported that they were currently under
a hiring freeze.
It is important to reiterate that the
State and local permitting information
on burden was based on the number of
additional facilities subject to PSD
because their emissions of GHGs exceed
the 100/250-tpy thresholds at actual
emissions rates, not PTE-based
emissions rates. However, the PSD
applicability requirements are based on
PTE. By adjusting the increase in
number of permits to account for GHG
sources that exceed the 100/250-tpy
applicability thresholds based on their
PTE emissions, EPA estimated a 140fold increase in numbers of PSD
permits, much more than the 10-fold
increase estimated by the States based
on actual emissions.
The GHG threshold analyses used to
identify the number of facilities that
would be affected at current PSD
permitting thresholds, and which is also
used later in Section VIII for evaluating
11 ‘‘NACAA Summary on Permitting GHGs Under
the Clean Air Act’’; Memorandum from Mary
Stewart Douglas, National Association of Clean Air
Agencies to Juan Santiago, EPA/OAQPS, September
3, 2009.
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alternative thresholds, are based on the
PTE of GHG sources. PTE is defined as
the maximum capacity of a stationary
source to emit a pollutant under its
physical and operational design,
including certain legal limitations, for
example, on emissions or hours of
operation. PSD and title V programs
both use PTE for defining major sources.
Our threshold analyses begin with
actual emissions estimates, but we then
adjust the numbers upward to account
for potential-to-emit. PTE adjustments
for industrial sources are generally
based on industry-specific capacity
utilization factors, while those used for
commercial and residential sources are
based on general sector-based
information on heating equipment and
appliance usage in these sectors. While
these PTE adjustments are important for
estimating affected facilities in all
sectors, they are a particularly relevant
concern for determining the number of
facilities in the commercial and
residential sector that may be affected,
where CO2 emissions are primarily due
to space heating/appliance usage and
combustion units are likely to be used
at levels well below constant operation
at maximum capacity. For example, our
PTE adjustment for commercial and
residential sources resulted in an
upwards adjustment ranging from 85 to
90 percent in emissions from their
actual emission values. The basis for our
PTE adjustments is described in the
‘‘Technical Support Document for
Greenhouse Gas Emissions Thresholds
Evaluation’’ found in the docket for this
proposal. We ask for specific comment
on the reasonableness of these PTE
adjustments as they apply to the
different sectors and source categories,
in particular, the commercial and
residential sectors where there is
limited information available on
equipment capacity utilization.
There are multiple sources of
uncertainty in our approaches for
estimating emissions, and thus for
estimating numbers of sources. For
example, the PTE adjustment factors
just described may overstate or
understate the maximum emissions
from sources particularly for the
commercial and residential sectors. In
addition, there are inherent
uncertainties in developing source
counts from nationally aggregated
statistics, as was done for the estimates
for commercial and residential sources
which rely on the allocation of national
level statistics for energy consumption.
The allocation factors we used, based on
U.S. Energy Information Administration
statistical sampling procedures, are
likely the best available to estimate the
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population of residential and
commercial sources exceeding different
GHG thresholds. Again, these
uncertainties may result in either
overestimates or underestimates. The
uncertainty is less for industrial
categories, where we generally utilized
facility-based methodologies, but
because it was necessary to use varying
methodologies for different source
types, as described in the Technical
Support Document, the uncertainties
will not be uniform across all categories.
We request comment on all aspects of
our threshold analysis, possible sources
of error, suggestions for reducing
uncertainties, and alternate approaches
to estimating emissions from
commercial and residential sources.
B. Title V Implications
The triggering of title V requirements
for GHG would result in administrative
burdens that stem from sources’
obligation to apply for permits. These
obligations apply differently depending
on whether the source already has a title
V permit. Most significant are the more
than six million sources of GHGs that
would become newly subject to title V
requirements because they exceed the
100-tpy threshold for GHG but did not
for previously regulated pollutants.
Although there are generally not
applicable requirements for GHGs that
apply to such sources, these six million
sources would be required to submit a
title V permit application within 1 year.
Permitting authorities would need to
issue these permits within 18 months of
receipt of a complete application, and
these permits would need to include
any requirements for non-GHGs that
may apply to the source, such as
provisions of an applicable SIP. For any
such requirements, permitting
authorities would also need to develop
terms addressing the various
compliance assurance requirements of
title V, including monitoring, deviation
reporting, six-month monitoring reports,
and annual compliance certifications.
Adding to the burden described above
would be the burden to add GHG terms
to the 14,700 existing title V permits.
While, in general, existing title V
permits would not immediately need to
be revised or reopened to incorporate
GHG (because as noted above, there are
generally not applicable requirements
for GHGs that apply to such sources),
permitting authorities may face burdens
to update existing title V permits for
GHG under two possible scenarios: (1)
EPA promulgates or approves any
applicable requirements for GHGs that
would apply to such a source, which
would generally require a permit
reopening or renewal application, or (2)
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the source makes a change that would
result in an applicable requirement for
GHGs to newly apply to the source,
such as PSD review, which would
generally require an application for a
permit revision. Permitting authorities
will also need to process permit renewal
applications, generally on a 5-year
cycle, and such renewals would need to
assure that the permit properly
addresses GHG. Finally they would
have to process title V applications for
new sources (including all the PSD
sources previously discussed).
Obviously, this massive influx of
permit applications would overwhelm
permitting authorities’ administrative
resources. Indeed, permitting authorities
report that they currently are having
difficulty keeping up with their existing
permit workloads. The Title V
Operating Permits System database,
which tracks permit issuance, confirms
that issuance of many permits is already
delayed. By increasing the volume of
permits by over 400 times, the
administrative burden would be
unmanageable.
As with PSD, we have quantified the
extent of the administrative problem
that would result in workload hours and
cost on the basis of information
concerning hours and costs for
processing existing title V permits that
is indicated on ICRs. However, we
recognize that more than 97 percent of
these new sources would be commercial
and residential sources. We estimate
that for permitting authorities, the
average new commercial or residential
permit would require 43 hours to
process, which is 10 percent of the time
needed for the average new industrial
permit. For an average existing permit,
which permitting authorities would
need to process through procedures for
significant revisions and permit
renewals, adding GHG emissions to the
permit would result in, we estimate, 9
additional hours of processing time,
which is 10 percent of the amount of
time currently necessary for processing
existing permits. We estimate that the
total nationwide additional burden for
permitting authorities for title V permits
from adding GHG emissions at the 100tpy threshold would be 340 million
hours, which would cost over $15
billion.
As noted in this preamble’s
discussion of PSD burdens, we also
reviewed summary information from
State and local permitting agencies,
which showed significant burdens
associated with adding GHGs in their
title V programs in terms of staffing,
budget, and other associated resource
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needs.12 Again, note that the permitting
agencies based their estimates on
numbers of permits that would be
required from sources subject to the
100-tpy title V applicability threshold
on an actuals–not PTE–basis. Based on
that level, the agencies assumed a 40fold increase in numbers of permits, and
estimated that:
• The resulting workload would
require an average of 57 more FTEs per
permitting agency at an estimated cost
of $4.6 million/year;
• Without the additional FTEs, the
average processing time for a permit
would increase to almost 10 years,
which is 20 times the current average
permit processing time;
• Permitting authorities would need 2
years on average to add the necessary
staff;
• On average, permitting authorities
would need 29 additional enforcement
and judicial staff;
• Eighty percent of the permitting
authorities indicated that their staff
would need training in all aspects of
permitting for sources of GHG
emissions; and
• A quarter of the permitting
authorities reported that they were
currently under a hiring freeze.
It is important to reiterate that, as
with PSD, the State and local
information on projected permitting
burden is based on the number of
additional facilities subject to title V
because their emissions of GHGs exceed
the 100-tpy thresholds at actual
emissions rates, not the PTE-based
emissions rates. However, the title V
applicability requirements are based on
PTE. As noted elsewhere in this
preamble, the State and local agencies
estimated a 40-fold increase in numbers
of title V permits based on the amount
of GHG sources’ actual emissions. By
adjusting the summary estimates
provided by the State and local agencies
to account for GHG sources that exceed
the 100-tpy threshold based on their
PTE emissions, EPA estimated that the
average permitting authority would
need 570 more FTEs to support its title
V permitting program.
requirements were triggered at the
current 100-tpy threshold. Most
industry stakeholders who commented
on the ANPR believe that triggering title
V and PSD applicability for GHG
emissions sources would be disastrous
and that a regulatory gridlock would
ensue. Many of these industry
commenters agreed with the U.S.
Chamber of Commerce’s study 13 which
found that regulating GHGs under the
CAA would cause 1,000,000 commercial
buildings, nearly 200,000 manufacturing
operations, and about 20,000 large farms
to become CAA-regulated stationary
sources. In fact, most of the industry
commenters believed that these
estimates underestimated the impacts.
Commenters expressed that the
implications of all these sources
becoming CAA-regulated stationary
sources would cause a large permitting
backlog, as States do not have the staff
or training to take on such a large
burden. In addition, commenters
stressed that many of these sources have
never needed an air permit before and
would have to obtain basic knowledge
of the permitting regulations and how to
comply with them, which would also
impose more burdens on the permitting
authorities. Many of the new sources
would be small emitters not previously
regulated under the CAA.
VI. What is the legal rationale for this
proposed action?
This section of the preamble discusses
the legal rationale for phasing in the
applicability thresholds for PSD and
title V purposes as proposed, which are
two doctrines that courts have relied on
in interpreting and applying statutory
requirements: The ‘‘absurd results’’
doctrine and the ‘‘administrative
necessity’’ doctrine. These doctrines are
related, apply in this case because of the
same factual circumstances, and justify
the same application—that is, the
phased approach—of the PSD and title
V applicability provisions. But they are
independent justifications, and
therefore will be discussed
independently.
C. ANPR Comments
We examined the ANPR comments
received for further information on the
additional administrative burdens that
permitting programs would carry if PSD
requirements for sources of GHG
emissions were triggered at the current
100/250-tpy thresholds and title V
A. ‘‘Absurd Results’’ Doctrine
This proposed action establishing the
first phase of the PSD and title V
applicability thresholds, in lieu of
applying the statutory 100/250 tpy
thresholds literally for GHG sources, is
supported by a judicial doctrine that
may be termed the ‘‘absurd results’’
doctrine. Applying the threshold
12 ‘‘NACAA Summary on Permitting GHGs Under
the Clean Air Act’’; Memorandum from Mary
Stewart Douglas, National Association of Clean Air
Agencies to Juan Santiago, EPA/OAQPS, September
3, 2009.
13 ‘‘A Regulatory Burden: The Compliance
Dimension of Regulating CO2 as a Pollutant’’;
Prepared for the U.S. Chamber of Commerce;
September 2008. See Docket ID No. EPA–HQ–OAR–
2008–0318–0402.1.
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provisions literally for the period
immediately after PSD and title V are
triggered for GHG emissions would lead
to results that contravene congressional
intent and, in fact, undermine
Congress’s purposes for both permitting
programs.
1. Overview
As discussed in detail below, the
courts are reluctant to invoke this
doctrine precisely because it entails
departing from the literal application of
statutory provisions, but they
nevertheless do so when the literal
application produces results that are
inconsistent with other statutory
provisions, run contrary to expressed
congressional intent or actually
undermine congressional intent, or are
otherwise so illogical or contrary to
sensible policy as to be beyond anything
that Congress could reasonably have
intended. This is one of the rare cases
in which the doctrine applies because
the extraordinary increases in PSD and
title V permit applications that would
result from a literal application of the
100/250 tpy threshold requirements
would, at least during the near term—
until EPA and the permitting authorities
can develop streamlining methods and
ramp up resources—extensively disrupt
the two permitting programs and
impose undue regulatory burdens in the
aggregate on the sources newly subject
to PSD and title V permit requirements.
These results would create tensions
with other explicit requirements of the
PSD and title V provisions, run contrary
to expressed congressional intent for the
PSD and title V provisions, and, in fact,
severely undermine both programs.
The applicability of the absurd results
legal doctrine to this proposal should be
reviewed with EPA’s proposed action in
mind: EPA proposes to establish a
process for implementing the PSD and
title V applicability requirements,
including a first phase that would
consist of establishing the specified
thresholds and vigorously developing
streamlining methods; then, after 5
years, preparing an assessment; and
then, by the sixth year, promulgating a
rulemaking for further action. In
addition, during this first phase, we
expect the permitting authorities to
ramp up resources for permit issuance.
With respect to PSD, a literal
application of the applicability
thresholds in CAA sections 165(a)(1)
and 169(2)(C) of 100 or 250 tpy for GHG
emitters would create significant
tensions with two other PSD provisions
during at least the first phase in period
after the triggering of PSD applicability
by the light-duty vehicle rule, and
before the development of streamlining
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methods and the addition of permitting
resources. First, a literal application
would render it impossible for
permitting authorities to meet the
requirement in CAA section 165(c) to
process permit applications within 12
months. During this initial period, the
number of permit applications would
increase by 150-fold, an unprecedented
increase that would far exceed
administrative resources. Permitting
authorities have estimated that it would
take 10 years to process a PSD permit
application, on average, and the
resulting backlog would affect the
permit applications for all sources, not
just the GHG emitters.
This backlog would grow by tens of
thousands each year following the
triggering of PSD applicability—again,
for at least the first few years—and
thereby undermine a second express
PSD provision, section 160(3). This
provision describes, as one of the
purposes of the PSD program, ‘‘to insure
that economic growth will occur in a
manner consistent with the preservation
of existing clean air resources.’’ Because
the PSD requirements apply on a
preconstruction basis—that is, they
require permits before sources may
construct or modify—tens of thousands
of sources seeking to construct or
modify during at least the first few years
after the triggering of PSD would instead
face many years of delay. This delay
would impede economic growth by
precluding any type of source—whether
it emits GHGs or not—from constructing
or modifying for years after its business
plan contemplates.
In addition, a literal application of the
100/250 tpy threshold in the PSD
provisions during at least the first few
years after PSD is triggered for GHG
emitters would be contrary to, and in
fact would undermine, expressed
congressional intent in several
important ways: As just noted, it would
undermine congressional intent to
authorize economic growth, albeit with
environmental safeguards. In addition,
the PSD requirements entail significant
regulatory costs to affected sources
because the sources must identify and
implement BACT on a source-specific
basis. The legislative history of the PSD
provisions makes clear that Congress
intended the PSD program to apply only
to larger sources, and not to smaller
sources, in light of the larger sources’
relatively greater ability to bear the costs
of PSD and their greater responsibility
for the pollution problems. In enacting
the PSD requirements during the 1977
Clean Air Act Amendments, Congress,
focused as it was on sources of
conventional pollutants and not global
warming pollutants, expected that the
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100/250 tpy applicability thresholds
would limit PSD to larger sources. But
because very small sources emit CO2 in
quantities as low as 100/250 tpy, a
literal application of the threshold to
GHG emitters, without streamlining,
would sweep in large numbers of small
sources and subject them to the high
costs of determining and meeting
individualized BACT requirements,
while also overwhelming permitting
authorities’ capacity to process those
applications. Thus, a literal application
of the 100/250 tpy thresholds would
sweep into the PSD program tens of
thousands of smaller sources that
Congress did not intend to include, and
the resulting strain on administrative
resources would preclude the hundreds
of larger sources that Congress did
intend to be subject to the program from
obtaining permits at least for an initial
period. In time, the development of
streamlining methods and the ramping
up of administrative resources would
bridge the gap between the literal
language and congressional intent, and
make it possible to expand the PSD
program in a sensible manner that
would make sense from the standpoint
of the sources and the permitting
authorities. But at least for the initial
period, these circumstances qualify as
‘‘absurd results’’ that merit avoiding a
literal application of the threshold
provision.
We reach similar conclusions for title
V. A literal application of the
applicability threshold in CAA sections
502(a), 501(2)(B), and 302(j) of 100 tpy
for GHG sources would bring some 6.1
million sources into the title V program.
For at least the first few years after title
V is triggered, until streamlining
methods are developed and
administrative resources are ramped up,
this would create significant tensions
with other title V provisions. The
extraordinary number of permit
applications would render it impossible
for permitting authorities to meet the
requirements of section 503(c) to
process title V permit applications
within 18 months. Further, this number
of permit applications would severely
disrupt implementation of the rest of the
carefully calibrated set of statutory
requirements that Congress set out in
title V. These requirements set out
specific—and brief—time frames for
EPA review and for public participation,
and they simply could not be complied
with at least initially for this number of
permit applications.
A literal application of the 100 tpy
threshold would also be inconsistent
with express congressional intent
concerning title V. The statutory
provisions by their terms, supported by
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the legislative history, indicate that
Congress designed the title V program to
promote compliance by compiling into
a single document all of the
requirements applicable to the source
under the Act. The legislative history
indicates that some in Congress
expected the title V permit program to
approximate the size of the Federal
water permit program. However,
applying the 100 tpy threshold for GHG
emitters would lead to permit
applications in numbers—some 6.1
million—that are almost 100 times
greater than what Congress expected.
The large permit backlog and inevitable
multi-year delays in permit issuance
that would ensue would thwart
Congress’s purposes in enacting title V
to promote compliance with CAA
requirements. As with PSD, this
disruption would affect all sources
covered by the provisions, whether or
not they emit GHGs.
Moreover, the great majority of the 6.1
million additional permittees would not
be subject to any CAA requirements
and, as a result, would be issued
permits that do not include any
applicable requirements. Because
Congress designed title V to require
permits to address applicable
requirements, and because Congress
envisioned a much smaller program,
immediately sweeping these sources
into the program is contrary to
congressional intent. Yet, their
inclusion in the program would
overwhelm administrative resources for
at least an initial period, until
streamlining methods are developed,
and preclude the timely issuance and
reissuance of permits to sources that
Congress clearly contemplated should
be included in the program. Thus, a
literal application of the title V
threshold provisions would bring in
millions of sources that Congress did
not intend to cover, and thereby
interfere with the administration of the
program for the thousands of sources
that Congress did intend to cover. As
with PSD, in time, the development of
streamlining methods and the ramping
up of administrative resources would
bridge the gap between the literal
language and congressional intent, and
make it possible to include more of
these sources in the title V program in
a manner that makes sense for both the
permittees and the permitters. But for
the initial period, as with PSD, these
circumstances qualify as ‘‘absurd
results’’ that merit avoiding a literal
application of the threshold provisions.
In the cases that apply the ‘‘absurd
results’’ doctrine, the courts go on to
apply the statutory provisions in
question in a manner that—while not in
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accordance with their literal reading—
effectuates congressional intent as much
as possible. We believe that the process
we propose in this notice, which
includes a first phase that establishes
thresholds at the specified levels while
allowing time to develop streamlining
approaches and ramp up resources,
followed by a study and further
rulemaking, is consistent with this
caselaw.
2. Tailoring Approach
In discussing the absurd results
caselaw and its applicability in this
case, it is important to keep in mind
EPA’s proposed action. As discussed in
detail elsewhere in this notice, EPA
proposes a phased plan designed to
achieve full compliance with the PSD
and title V threshold requirements. The
first phase entails the establishment of
applicability thresholds at the 25,000
tpy CO2e levels, and significance levels
at between 10,000 and 25,000 tpy CO2e.
In addition, the first phase entails
development of streamlining methods—
including potential revisions to the
definition of potential to emit, general
permits, and presumptive BACT—that
allow us to craft the application of PSD
and title V in ways that are achievable
and effectively balance the burdens on
both the permitting authorities and the
regulated community with the
reductions achievable. The first phase
also includes the collection of
information and further assessments in
a report, to be completed within 5 years,
and culminates in a rulemaking to be
promulgated by the sixth year that will
establish further action.
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3. PSD and Title V Threshold Provisions
Several PSD and title V provisions are
relevant for present purposes because of
the specific requirements that they
establish and the window that they
provide into congressional intent. These
provisions start with the PSD and title
V applicability provisions. For PSD
purposes, the key applicability
provisions are found in CAA sections
165(a) and 169(1), which identify the
new sources subject to PSD, and CAA
§ 111(a)(4), which describes the
modifications of existing sources that
are subject to PSD. CAA section 165(a),
42 U.S.C. 7475, provides:
No major emitting facility on which
construction is commenced after August 7,
1977, may be constructed in any area to
which this part applies unless—
(1) A permit has been issued for such
proposed facility in accordance with this part
setting forth emission limitations for such
facility which conform to the requirements of
this part;
(2) The proposed permit has been subject
to a review in accordance with this section
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* * *, and a public hearing has been held
with opportunity for interested persons
including representatives of the
Administrator to appear and submit written
or oral presentations on the air quality
impact of such source, alternatives thereto,
control technology requirements, and other
appropriate considerations; * * *
(4) The proposed facility is subject to the
best available control technology for each
pollutant subject to regulation under this
chapter emitted from, or which results from,
such facility * * *.
The term ‘‘major emitting facility’’ is
defined, under CAA § 169(1) to include:
* * * stationary sources of air pollutants
which emit, or have the potential to emit, one
hundred tons per year or more of any air
pollutant from [28 listed] types of stationary
sources. * * * Such term also includes any
other source with the potential to emit two
hundred and fifty tons per year or more of
any air pollutant. This term shall not include
new or modified facilities which are
nonprofit health or education institutions
which have been exempted by the State.
The thresholds in CAA section 169(1)
of 100-tpy for sources in the 28 listed
categories and 250-tpy for all other
sources may be referred to as the 100/
250-tpy thresholds.
As for modification of existing
sources, CAA section 169(1)(C) provides
that the term ‘‘construction,’’ as used in
CAA section 165(a) (the PSD
applicability section) ‘‘includes the
modification (as defined in section
111(a)(4)) of any source or facility.’’
Section 111(a)(4), in turn, provides:
The term ‘‘modification’’ means any
physical change in, or change in the
method of operation of, a stationary
source which increases the amount of
any air pollutant emitted by such source
or which results in the emission of any
air pollutant not previously emitted.
As interpreted by EPA regulations,
these provisions, taken together, provide
that new stationary sources are subject
to PSD if they emit at the 100/250-tpy
thresholds air pollutants that are subject
to EPA regulation, and that existing
stationary sources that emit such air
pollutants at the 100/250-tpy thresholds
are subject to PSD if they undertake a
physical or operational change that
increases their emissions of such air
pollutants by any amount.
For title V purposes, the key
applicability provisions are found in
CAA sections 502(a), 501(2)(B), and
302(j). These provisions provide that it
is unlawful for any person to operate a
‘‘major source’’ without a title V permit,
section 502(a), and define a ‘‘major
source’’ as ‘‘any major stationary facility
or source of air pollutants which
directly emits, or has the potential to
emit, one hundred tons per year or more
of any air pollutant.’’ CAA section
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55305
501(2)(B) and section 302(j). As noted
elsewhere, these provisions, taken
together and as interpreted by EPA,
provide that stationary sources are
subject to title V if they emit at the 100tpy threshold air pollutants that are
subject to EPA regulation.
Other provisions of particular
relevance are the requirements in the
PSD and title V programs for timely
issuance of permits. For PSD, the
permitting authority must ‘‘grant[ ] or
den[y] [any completed permit
application] not later than one year after
the date of filing of such completed
application.’’ CAA § 165(c). For title V,
‘‘the permitting authority shall approve
or disapprove a completed application
* * * and shall issue or deny the
permit, within 18 months after the date
of receipt thereof * * *.’’ CAA section
503(c). Title V goes on to include
several provisions designed to support
this 18-month requirement. First, the
permitting authority must develop
‘‘adequate, streamlined, and reasonable
procedures for expeditiously
determining when applications are
complete, for processing such
applications, for public notice * * *
and for expeditious review of permit
actions, including * * * judicial review
in State court of the final permit action
by [specified persons].’’ CAA section
502(b)(6). Second, title V includes a
‘‘hammer’’ provision designed to
reinforce timely permit issuance, which
is that the permitting authority’s
program must include:
To ensure against unreasonable delay by
the permitting authority, adequate authority
and procedures to provide that a failure of
such permitting authority to act on a permit
application or permit renewal application (in
accordance with the time periods specified in
[CAA § 503] * * *) shall be treated as a final
permit action solely for purposes of obtaining
judicial review in State court of an action
brought by any person referred to in
paragraph (6) to require that action be taken
by the permitting authority on such
application without additional delay. CAA
§ 502(b)(7).
Third, the permit program must include
‘‘[a]uthority and reasonable procedures
consistent with the need for expeditious
action by the permitting authority on
permit applications and related matters,
to make available to the public [certain
permit-related documents]’’. CAA
section 502(b)(8).
In addition, PSD includes a set of
provisions that specifically state ‘‘the
purposes of [the PSD program],’’ which
are to balance environmental protection
and growth. CAA § 160. One of the
purposes, in subsection (1), is
specifically ‘‘to protect public health
and welfare,’’ and another, in subsection
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(3), is ‘‘to insure that economic growth
will occur in a manner consistent with
the preservations of existing clean air
resources.’’ Title V does not have a
parallel set of provisions describing its
purpose, but it is clear from its
provisions and its legislative history,
discussed below, that its key goal is to
gather into a single document the Clean
Air Act requirements applicable to a
source and impose conditions necessary
to assure compliance with such
requirements, and thereby promote the
enforceability of CAA requirements
applicable to the covered sources. CAA
§ 503(b)(1) requires that the source’s
permit application must assure
‘‘compl[iance] with all applicable
requirements’’ of the CAA, and § 504(a)
requires that ‘‘[e]ach permit issued
under [title V] shall include * * * such
* * * conditions as are necessary to
assure compliance with applicable
requirements of [the Clean Air Act].’’
See H.R. Rep. No. 101–490, at 351
(1990) (‘‘It should be emphasized that
the operating permit to be issued under
this title is intended by the
Administration to be the single
document or source of all of the
requirements under the Act applicable
to the source.’’).
In addition, both PSD and title V
include detailed procedures for
implementation. The PSD provisions
most relevant for sources of GHG are
that the proposed permit for each source
must be the subject of a public hearing
with opportunity for interested persons
to comment, CAA § 165(a)(2), and each
source must be subject to best available
control technology, as determined by
the permitting authority on a source-bysource basis, CAA § 165(a)(4), 169(3).
Title V includes a comprehensive and
finely detailed implementation schedule
that mandates timely issuance of
permits while building in EPA and
affected State review, public
participation, and timely compliance by
the source with reporting requirements.
Following the date that sources become
subject to title V, they have 1 year to
submit their permit applications. CAA
§ 503(c). As noted above, the permitting
authority then has 18 months to issue or
deny the permit. CAA § 503(c).
Permitting authorities must provide an
opportunity for public comment and a
hearing. CAA § 502(b)(6). If the
permitting authority proposes to issue
the permit, the permitting authority
must submit the permit to EPA, and
notify affected States, for review. CAA
§ 505(a)(1). EPA then has 45 days to
review the permit and, if EPA deems it
appropriate, to object to the permit.
CAA § 505(b)(1). If EPA does object,
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then the permitting authority must,
within 90 days, revise it to meet the
objections, or else EPA becomes
required to issue or deny the permit.
CAA § 505(c). If EPA does not object,
then, within 60 days of the close of the
45-day review period, any person may
petition EPA to object, and EPA must
grant or deny the petition within 60
days. CAA § 505(b)(2). If a permit is
issued, it must include a permit
compliance plan, under which the
permittee must ‘‘submit progress reports
to the permitting authority no less
frequently than every 6 months,’’ and
must ‘‘periodically (but no less
frequently than annually) certify that
the facility is in compliance with any
applicable requirements of the permit,
and [ ] promptly report any deviations
from permit requirements to the
permitting authority.’’ CAA § 503(b).
4. ‘‘Absurd Results’’ Doctrine
The familiar Chevron two-step
analysis provides the starting point for
EPA’s interpretation of these statutory
provisions. Under Chevron step 1, an
agency must determine whether
Congress’s intent in a particular
provision on a particular question is
clear; if so, then the agency must follow
that intent. If the intent of a provision
is not clear, then the agency may, under
step 2, fashion a reasonable
interpretation of the provision. Chevron
U.S.A. Inc. v. NRDC, 467 U.S. 837, 842–
43 (1984).
Here, the applicability provisions for
PSD and title V are clear on their face.
However, the U.S. Supreme Court has
held that the plain meaning of a
statutory provision is not conclusive ‘‘in
the ‘rare cases [in which] the literal
application of a statute will produce a
result demonstrably at odds with the
intentions of the drafters’ * * * [in
which case] the intention of the drafters,
rather than the strict language,
controls.’’ Ron Pair, 489 U.S. at 242
(citations omitted).14
In describing these cases as ‘‘rare,’’
the U.S. Supreme Court seemed to be
referring to the small percentage of
14 Judge Learned Hand’s formulation of the
doctrine is often quoted in the caselaw:
Of course, it is true that the words used, even in
their literal sense, are the primary and ordinarily
the most reliable, source of interpreting the
meaning of any writing. * * * But it is one of the
surest indexes of a mature and developed
jurisprudence not to make a fortress out of the
dictionary; but to remember that statutes always
have some purpose or object to accomplish, whose
sympathetic and imaginative discovery is the surest
guide to their meaning.
Cabell v. Markham, 148 F.2d 737, 738 (2d Cir.),
aff’d 326 U.S. 404 (1945). See Giuseppi v. Walling,
144 F.2d 608, 624 (2d Cir. 1944) (opinion by Judge
Hand) (‘‘There is no surer way to misread any
document than to read it literally’’).
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statutory-construction cases that are
decided on the basis of the doctrine.
The D.C. Circuit, in surveying the
doctrine over more than a century of
jurisprudence, characterized the body of
law in absolute numbers as comprising
‘‘legions of court decisions.’’ In re
Franklyn C. Nofziger, 925 F.2d 428, 434
(D.C. Cir. 1991). The U.S. Supreme
Court cases include, among others,
Nixon v. Missouri Municipal League,
541 U.S. 125, 132–33 (2004) (‘‘any
entity’’ includes private but not public
entities); Raygor v. Regents of Univ. of
Minn., 534 U.S. 533, 542–45 (2002)
(‘‘implying a narrow interpretation of
* * * ‘any claim asserted’ so as to
exclude certain claims dismissed on
Eleventh Amendment grounds’’); Ron
Pair, 48 U.S. at 242; Green v. Bock
Laundry Machine Company, 490 U.S.
504 (1989) (provision in Federal Rule of
Evidence that protects ‘‘the defendant’’
against potentially prejudicial evidence,
but not the plaintiff, refers to only
criminal, and not civil, defendants);
Train v. Colorado Public Interest
Research Group, Inc., 426 U.S. 1, 23–24
(1976) (prohibition in Federal Water
Pollution Control Act against
discharging into navigable waters
‘‘pollutants,’’ which are defined to
include ‘‘radioactive materials,’’ does
not apply to three specific types of
radioactive materials); Lynch v.
Overholser, 369 U.S. 705, 710, (1962)
(statutory construction is not confined
to the ‘‘bare words of a statute’’); Utah
Junk Co. v. Porter, 328 U.S. 39, 44
(1946) (‘‘literalness may strangle
meaning’’); Markham v. Cabell, 326 U.S.
404, 409 (1945) (‘‘The policy as well as
the letter of the law is a guide to
decision.’’); United States v. American
Trucking Associations, Inc. 310 U.S. 534
(1940) (the term ‘‘employees’’ in the
Federal Motor Carrier Act, is limited to
employees whose activities affect
safety); C.V. Sorrels v. U.S., 287 U.S.
435, 446–49 (1932) (provisions of
National Prohibition Act that
criminalize possessing and selling
liquor do not apply if defendant is
entrapped; Court declines to apply the
‘‘letter of the statute’’ because doing so
‘‘in the circumstances under
consideration is foreign to its purpose’’);
Holy Trinity Church v. U.S., 143 U.S.
457, 516–17 (1892) (‘‘any alien’’ does
not include a foreign pastor; Court
stated, ‘‘It is a familiar rule, that a thing
may be within the letter of the statute
and yet not within the statute, because
not within its spirit, nor within the
intention of its makers * * * If a literal
construction of the words be absurd, the
Act must be construed as to avoid the
absurdity’’); United States v. Kirby, 7
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Wall, 482, 486, 19 L.Ed. 278 (1868) (the
statute punishing obstruction of the
mails is not to be applied to obstruction
for the lawful purpose of arresting a
mail carrier indicted for murder).
The D.C. Circuit has also handed
down several decisions that applied the
absurd results doctrine to avoid a literal
interpretation or application of statutory
provisions. See Buffalo Crushed Stone,
Inc. v. Surface Transportation Board,
194 F.3d 125, 129–30 (D.C. Cir. 1999)
(regulation of Surface Transportation
Board providing that if a notice of
exemption ‘‘contains false or misleading
information, the use of the exemption is
void ab initio’’ does not apply to a
notice containing false information
when declaring the notice void ab initio
would undermine the goals of the
governing statute; a conflict between the
‘‘literal application of statutory
language’’ and maintaining the integrity
of the regulatory scheme should be
resolved by construing the text in
accordance with its purpose); U.S. v.
Stewart, 104 F.3d 1377, 1388 (D.C. Cir.
1997) Environmental Defense Fund v.
EPA, 82 F.3d 451, 468–69 (D.C. Cir.
1996) (although Clean Air Act requires
that a Federal action conform to the
State implementation plan that is
currently in place, EPA may instead
require conformity to a revised
implementation plan that State commits
to develop; ‘‘[t]his is one of those rare
cases * * * [that] requires a more
flexible, purpose-oriented interpretation
if we are to avoid ‘absurd or futile
results.’ ’’); In re Nofziger, 925 F.2d 428,
434–35 (D.C. Cir. 1991) (provision
authorizing payment of attorney fees to
the subject of an investigation
conducted by an independent counsel
of the Department of Justice only if ‘‘no
indictment is brought’’ against such
individual does not preclude payment
of attorney fees when an indictment is
brought but is determined to be invalid).
To determine whether ‘‘the intentions
of the drafters’’ differ from the result
produced from ‘‘literal application’’ of
the statutory provisions in question, the
courts may examine the overall context
of the statutory provisions, including
whether there are related statutory
provisions that either conflict or are
consistent with that interpretation,15
15 A related line of cases addresses statutory
provisions that directly, on their face, conflict with
other statutory provisions. In these cases, as with
the ‘‘absurd result’’ cases, the courts may decline
to interpret literally the statutory provisions in
question, and instead interpret them to give as
much effect as possible to all of the relevant
provisions. See, e.g., Mountain States Telephone
and Telegraph Co. v. Pueblo of Santa Ana, 472 U.S.
237 (1985); Clark v. Uebersee Finanz-Korporation,
332 U.S. 480 (1947); Citizens to Save Spencer
County v. EPA, 600 F.2d 844 (D.C. Cir. 1977).
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and including whether there is
legislative history that exposes what the
legislature meant by the terms in
question. In addition, the courts may
examine whether a literal application of
the provisions produces a result that the
courts characterize variously as absurd,
futile, strange, or indeterminate, and
therefore so illogical or otherwise
contrary to sensible public policy as to
be beyond anything Congress would
reasonably have intended. After
concluding this examination, the courts
uphold an application of the provisions
that, albeit not the literal application, is
one that is nevertheless as consistent
with congressional intent as possible.
The U.S. Supreme Court applied the
absurd results doctrine in Green v. Bock
Laundry Machine Company, 490 U.S.
504 (1989). There, the Court considered
Federal Rule of Evidence 609(a), which
provides:
General Rule. For the purpose of attacking
the credibility of a witness, evidence that the
witness has been convicted of a crime shall
be admitted * * * but only if the crime (1)
[is of a specified type] and the court
determines that the probative value of
admitting this evidence outweighs its
prejudicial effect to the defendant.
(Emphasis added.) The Court recognized
that read literally, Rule 609(a) applies in
both criminal and civil litigation and
gives an advantage to defendants.
Specifically, the rule extends to both the
criminal and civil defendants the
protection of weighing the probative
value of evidence of certain crimes
against its prejudicial effect, but as for
plaintiffs, the rule requires that
evidence of those crimes be admitted
without weighing against prejudicial
effect. The Court found that for criminal
litigation, this result makes sense
because it is consistent with the greater
protections generally afforded to
defendants. However, for civil litigation,
the Court found that this ‘‘literal reading
would compel an odd result’’ because,
among other things, civil defendants are
not accorded greater protections than
civil plaintiffs and, in any event,
whether a litigant is designated plaintiff
or defendant often is happenstance. The
Court emphasized that ‘‘[n]o matter how
plain the text of the Rule may be,’’ it
could not accept this result, and
concluded that ‘‘as far as civil trials are
concerned, Rule 609(a)(1) ‘can’t mean
what it says.’ ’’ 490 U.S. at 509–11
(citations omitted). The Court reviewed
the legislative history, and concluded
that notwithstanding the plain language,
Congress ‘‘intended that only the
accused in a criminal case should be
protected from unfair prejudice by the
balance set out in Rule 609(a)(1).’’ Id. at
523–24.
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In cases in which the ‘‘absurd results’’
doctrine of statutory constructions
authorizes an agency to depart from the
literal meaning of the statute, the agency
must do so in as limited a manner as
possible to effectuate underlying
congressional intent. As the D.C. Circuit
has stated:
The rule that statutes are to be read to
avoid absurd results allows an agency to
establish that seemingly clear statutory
language does not reflect the
‘‘unambiguously expressed intent of
Congress,’’ * * * and thus to overcome the
first step of the Chevron analysis. But the
agency does not thereby obtain a license to
rewrite the statute. When the agency
concludes that a literal reading of a statute
would thwart the purposes of Congress, it
may deviate no further from the statute than
is needed to protect congressional intent.
Mova Pharmaceutical Corp. v. Shalala, 140
F.3d 1060, 1068 (D.C. Cir. 1998).
5. PSD and Title V Applicability
Requirements
The plain meaning of the PSD
applicability provisions in CAA
§§ 165(a)(1) and 169(1) is clear that once
PSD is triggered for GHG emissions, a
source will be subject to PSD if it either
belongs to one of 28 specifically
identified source categories and
‘‘emit[s], or ha[s] the potential to emit,
one hundred tons per year or more of
any air pollutant,’’ including GHGs, or
does not belong to one of those source
categories and has ‘‘the potential to emit
two hundred and fifty tons per year or
more of any air pollutant,’’ including
GHGs. Similarly, the plain meaning of
the title V applicability requirements in
CAA §§ 501(2)(B) and 302(j) is clear that
once the title V requirements are
triggered, they would apply to a source
that ‘‘directly emits, or has the potential
to emit, one hundred tons per year or
more of any air pollutant,’’ including
GHGs.
As described in detail elsewhere,
applying the plain meaning of these
provisions once PSD and title V are
triggered for GHG emissions would
impose PSD and title V permitting
requirements on an extraordinarily large
number of sources: The number of
sources subject to PSD permits would
increase from less than 300 per year to
some 41,000 per year, and the number
of sources subject to the title V
requirements would grow from less than
14,000 to some 6.1 million. For at least
an initial period of time, before
permitting authorities could develop
streamlining mechanisms, these
obligations would have severe effects.
From the permitting authorities’
standpoint, the number of permit
applications would far exceed their
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administrative capacity, and would
inevitably result in delays in issuance of
permits to all sources—whether
emitting conventional pollutants or
GHGs—that would be measured in
many years. From the sources’
standpoints, thousands of sources that
are quite small and that have never been
confronted with CAA obligations would
incur the expenses of PSD permitting
requirements, including, most
importantly, indentifying and
developing BACT controls on a sourceby-source basis. As for title V, millions
of sources would be required to submit
permit applications that meet title V
requirements, even though the great
majority of them would not be subject
to any applicable CAA requirements.
During this initial period, permitting
authorities could develop streamlining
approaches and ramp up administrative
resources so that afterwards, they would
be better able to accommodate the large
numbers of permit applications and
sources would be better able to comply.
But, again, during the initial period,
severe problems would ensue.
We believe that these effects of a
literal application of the PSD and title
V applicability thresholds and their
collateral consequences are well beyond
anything that Congress envisioned when
it drafted the PSD and title V
requirements, and indeed undermine
both permitting programs. As a result,
these effects bring into play the ‘‘absurd
results’’ doctrine.
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a. PSD
(1) Tensions With Other Statutory
Requirements
Turning first to PSD, an important
indication that Congress would not have
intended that the threshold provisions
be applied literally under the present
circumstances may be found in the
tensions that this literal application
would create with other PSD provisions.
CAA § 165(c) is particularly important
in this regard. It requires that the
permitting authority grant or deny
‘‘[a]ny completed permit application for
a major emitting facility * * * not later
than one year after the date of filing of
such completed application.’’ A literal
interpretation of CAA sections 165(a)(1)
and 169(1) to apply at the 100/250 tpy
levels for GHG sources would render
compliance with this provision
impossible by requiring far more permit
applications than permitting authorities
could process under this 12-month
deadline, for at least an initial period of
time until streamlining methods are
developed. As noted elsewhere, States
have estimated that the number of PSD
permits that would be required under a
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100/250 tpy threshold on an actuals
basis would result in an average
processing time of 10 years.16
A literal interpretation of CAA
sections 165(a)(1) and 169(1) to apply at
the 100/250 tpy levels would also be
directly inconsistent with the PSDpurpose provision in CAA § 160, in
particular, § 160(3), which is ‘‘to insure
that economic growth will occur in a
manner consistent with the preservation
of existing clear air resources.’’ As the
legislative history makes clear, Congress
enacted the PSD provisions to resolve
issues arising when sources of criteria
pollutants seek to build or expand in
areas with air quality that meets the
national ambient air quality standards,
but that would deteriorate with the
addition of such new or expanded
sources. Congress designed the PSD
provisions to provide a mechanism for
allowing sources to construct or modify
in those clean-air areas, but with
safeguards that both protected health
and welfare, and that also left enough
room in the airshed for still more
economic growth. See, e.g., H. Rpt. 95–
294, 95th Cong., 1st Sess., at 154
(legislation ‘‘not only protect[s] public
health and welfare but also assur[es]
future air resources will be available for
continuing the industrial and energy
development so necessary for the
growth of the Nation’’). Because PSD is
a preconstruction requirement,
increasing permitting authorities’
workload from 300 to 41,000 permits
would severely undermine this purpose
of facilitating economic growth, at least
initially, until permitting authorities can
develop streamlining methods and ramp
up resources. Each year, many
thousands of sources would face multiyear delays in receiving their permits,
and as a result, for all practical
purposes, they would be forced to place
on hold indefinitely their plans to
construct or modify.
(2) Inconsistency With Congressional
Intent
The legislative history of the PSD
provisions—enacted, again, in the 1977
Clean Air Act Amendments—also
makes clear that a literal application of
the applicability provisions would lead
to results that are diametrically
inconsistent with Congress’s expressed
intent. In reviewing the legislative
history, it should be borne in mind that
Congress was focused on sources of
16 As noted elsewhere, because the applicability
provisions apply on a potential-to-emit basis, as
well as an actuals basis, the number of permit
applications would be much greater than the
permitting authorities assumed, and therefore the
processing times would be much longer than 10
years.
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criteria pollutants—primarily sulfur
dioxide (SO2), particulate matter,
nitrogen oxides (NOX), and carbon
monoxide (CO)—and not GHG
emissions. This focus stems from the
basic purpose of the PSD program,
which is to safeguard maintenance of
the NAAQS, combined with the limited
awareness at that time of the problem of
climate change. See S 95–127 (95th
Cong., 1st Sess.), at 27.
Congress designed the PSD provisions
to impose significant regulatory
requirements, on a source-by-source
basis, to identify and implement BACT
and, for criteria pollutant, to also
undertake certain studies. Congress was
well aware that because these
requirements are individualized to the
source, they are expensive. Accordingly,
Congress designed the applicability
provisions to apply these requirements
to industrial sources of a certain type
and a certain size—sources within 28
specified source categories and that emit
at least 100 tpy—as well as all other
sources that emit at least 250 tpy, and,
by the same token, to exempt other
sources from these requirements. The
legislative history shows that Congress’s
limitation of PSD to larger sources was
quite deliberate, and was based on its
determination to limit the costs that
PSD permitting entails to the larger
sources in certain industries. The D.C.
Circuit has had occasion, in Alabama
Power, to acknowledge this legislative
history: ‘‘Congress’s intention was to
identify facilities which, due to their
size, are financially able to bear the
substantial regulatory costs imposed by
the PSD provisions and which, as a
group, are primarily responsible for
emissions of the deleterious pollutants
that befoul our nation’s air.’’ Alabama
Power, 636 F.2d at 353. The Court
added, ‘‘Though the costs of compliance
with [the PSD] requirements are
substantial, they can reasonably be
borne by facilities that actually emit, or
would actually emit when operating at
full capacity, the large tonnage
thresholds specified in section 169(1).’’.
Id. at 354.
Although Congress required that CAA
requirements generally apply to ‘‘major
emitting facilities,’’ defined as any
source that emits or has the potential to
emit 100 tpy of any pollutant, Congress
applied PSD to only sources at 100 tpy
or higher in 28 specified industrial
source categories, and at 250 tpy or
more in all other source categories. This
distinction was deliberate: According to
Sen. McClure, Congress selected the 28
source categories after reviewing an EPA
study describing 190 industrial source
categories. 122 Cong. Rec. 24521 (July
29, 1976) (statement by Sen. McClure).
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Congress also relied on an EPA
memorandum that identified the range
of industrial categories that EPA
regulated under its regulations that
constituted the precursor to the
statutory PSD program, and listed both
the estimated number of new sources
constructing each year and the amount
of pollution emitted by the ‘‘typical
plant’’ in the category. The
memorandum was prepared by B.J.
Steigerwald, Director of the Office of Air
Quality Planning and Standards and
Roger Strelow, EPA’s Assistant
Administrator for Air and Waste
Management (‘‘Steigerwald-Strelow
memorandum). The SteigerwaldStrelow memorandum makes clear that
the 100 tpy cut-off for the 28 listed
sources categories, and the 250 tpy cutoff for all other sources, was
meaningful; that is, there were a large
number of sources below those cut-offs
that Congress explicitly contemplated
would not be included in PSD. Id. at
24548–50.
Consistent with this, the legislative
history on the Senate side also
specifically identified certain source
categories that Senators believed should
not be covered by PSD. The Senate bill
language limited PSD to sources of 100
tpy or more in 28 listed source
categories, and to any other categories
that the Administrator might add. Sen.
Muskie stated that the Senate bill
excluded ‘‘houses, dairies, farms,
highways, hospitals, schools, grocery
stores, and other such sources.’’ 123
Cong. Rec. 18021 (June 8, 1977)
(statement of Sen. Muskie). Sen.
McLure’s list of excluded source
categories were ‘‘[a] small gasoline
jobber, or a heating plant at a
community college, [which] could have
the potential to emit 100 tons of
pollution annually.’’ 122 Cong. Rec.
24548–49 (July 29, 1976) (statement of
Sen. McClure). The Senate Committee
Report included a comparable list, and
in describing it, concisely articulated
the cost-conscious basis for the linedrawing: ‘‘[the PSD] procedure * * *
must include an effective review-andpermit process. Such a process is
reasonable and necessary for very large
sources, such as new electrical
generating plants or new steel mills. But
the procedure would prove costly and
potentially unreasonable if imposed on
construction of storage facilities for a
small gasoline jobber or on the
construction of a new heating plant at
a junior college, each of which may
have the potential to emit 100 tons of
pollution annually.’’ S. Rpt. 95–127 at
96–97.
The enacted legislation differs from
the Senate bill by replacing the
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authorization to EPA to include by
regulation source categories in addition
to the listed 28 source categories with
an inclusion of all other sources if they
exceed 250 tpy, and with an
authorization for the States to exempt
hospitals and educational institutions.
But Congress’s overall intention remains
clear, as the D.C. Circuit described in
Alabama Power:. ‘‘Congress’s intention
was to identify facilities which, due to
their size, are financially able to bear the
substantial regulatory costs imposed by
the PSD provisions and which, as a
group, are primarily responsible for
emissions of the deleterious pollutants
that befoul our nation’s air * * * [With
respect to] the heating plant operating in
a large high school or in a small
community college * * * [w]e have no
reason to believe that Congress intended
to define such obviously minor sources
as ’major’ for the purposes of the PSD
provision.’’ 17 636 F.2d at 353–54.
However, applying the 100/250 tpy
threshold literally to CO2 emissions
would frustrate congressional intent by
subjecting to PSD sources that Congress
specifically intended not to include.
This occurs simply because although
Congress evaluated whether sources
should be included in PSD by reference
to the amount of the emissions of
conventional pollutants, many sources
combust fossil fuels for heat or
electricity, and the combustion process
produces quantities of CO2 that are far
in excess of the sources’ quantities of
conventional pollutants and, in many
cases, Congress’s carefully considered
100 and 250 tpy thresholds. As a result,
many of the ‘‘typical plant[s]’’ identified
in the Steigerwald-Strelow
memorandum that Congress thought
would be excluded from PSD due to the
relatively small amounts of their
conventional pollutants would in fact be
included due to the CO2emissions from
their heating or electricity generating
equipment.But the clearest and most
important indication that applying the
100/250 thresholds literally in the case
of GHG emissions would undermine
congressional intent comes in
considering the emissions profile of the
small-sized boilers. Congress focused
closely on identifying which sources
with emissions in excess of 100 tpy
should not be subject to PSD even
though they are subject to CAA
requirements generally. But Congress
viewed a large set of sources as emitting
17 Note that although Congress specifically
authorized the States to exempt ‘‘nonprofit health
or education institutions’’ from the definition of
‘‘major emitting facility,’’ this statement by the D.C.
Circuit should be taken as the Court’s view that
Congress did not design PSD to cover sources of the
small size described.
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below 100 tpy and therefore not
included in the PSD program and,
indeed, not even subject to debate as to
whether they should be included in the
PSD program. Chief among these
sources, in terms of absolute numbers of
sources, were small boilers. The
Steigerwald-Strelow memorandum
identified two categories of these
boilers, differentiated by size. The first
ranges in size from 10 to 250 × 106 Btu/
hr, and has a ‘‘typical plant’’ size of 107
Btu/hr, with ‘‘BACT emissions from
typical plant’’ of 53 tpy, and a total of
1,446 sources in the category. The
second category ranges in size from 0.3
to 10 × 106 Btu/hr, and has a ‘‘typical
plant’’ size of 1.3 × 106 Btu/hr, with
‘‘BACT emissions from typical plant’’ of
2 tpy, and a total of 11,215 sources in
the category. The memorandum
discusses these two categories in the
context of explaining which source
categories exceed a size of 100 tpy—and
therefore would be subject to PSD if a
100 tpy threshold were set—by stating,
‘‘Fortunately, most truly small boilers
and typical space heating operations
would not be covered.’’ 122 Cong. Rec.
24549 (July 29, 1976). However, if the
CO2 emissions of these small boilers are
considered, then most of them would be
subject to PSD. In general, most boilers
of these small sizes are fired with
natural gas, and a natural gas boiler
greater than 0.5 × 106 Btu/hr emits at
least 250 tpy CO2. As a result, the small
commercial and residential sources that
include these boilers would become
subject to PSD, and this would directly
contravene Congress’s intention to limit
PSD to ‘‘industrial plants of significant
impact.’’ 122 Cong. Rec. 24548–49
(statement of Sen. McClure). The
legislative history also provides a
window into the scope of the program
that Congress anticipated and related
administrability concerns. According to
the Steigerwald-Strelow memorandum,
the number of new sources each year
whose ‘‘BACT emissions from typical
plant’’ exceed 100 for the 28 listed
source categories and 250 for all other
source categories is less than 100 per
year. Although the Steigerwald-Strelow
memorandum does not attempt to
estimate the number of modifications, it
appears that based on this information,
Congress had reason to expect the total
size of the PSD program to be measured
in the hundreds of permits each year. A
program of this size would be
manageable by EPA and the permitting
authorities.
The D.C. Circuit based its holding in
Alabama Power that potential-to-emit
for purposes of the applicability
thresholds should be defined as
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emissions at full capacity with
implementation of control equipment,
in part on its view that with this
definition, the number of sources
subject to PSD would be manageable:
Though the costs of compliance with
section 165 requirements are
substantial, they can reasonably be
borne by facilities that actually emit, or
would actually emit when operating at
full capacity, the large tonnage
thresholds specified in section 169(1).
The numbers of sources that meet these
criteria, as we delineate them, are
reasonably in line with EPA’s
administrative capability.
Alabama Power, 636 F.2d at 354
(emphasis added). However, applying
the thresholds literally to GHG
emissions would increase the size of the
PSD program far beyond what Congress
had reason to expect and what the D.C.
Circuit evidently had in mind.
Returning to the Steigerwald-Strelow
table, applying the thresholds literally
would bring into PSD the great majority
of the small boilers constructed each
year, which numbered, in total, 12,661.
Adding more sources from other source
categories, and, most importantly,
modifications, indicates that the size of
the PSD program would very likely be
at least an order of magnitude greater
than what Congress intended. At least
for an initial period of time, until
streamlining methods could be
developed, these numbers of sources
would be well beyond the
‘‘administrative capability’’ that the D.C.
Circuit described EPA as having.
(3) Absurd Results
Applying the PSD thresholds to
sources of GHG emissions literally
results in a PSD program that is so
contrary to what Congress had in
mind—and that in fact so undermines
what Congress attempted to accomplish
with the PSD requirements—that it
should be avoided under the ‘‘absurd
results’’ doctrine. As described above,
Congress designed the PSD program as
a mechanism to allow construction of
new sources and expansion of existing
sources in areas meeting the NAAQS,
but only after those sources, on a
source-by-source basis, undertook
analyses to demonstrate that their
emissions would not significantly
deteriorate air quality and implemented
controls representing BACT.
Recognizing that PSD imposed
significant costs on sources, Congress
constructed a statutory scheme that it
viewed as limiting PSD to large
industrial sources that could bear the
financial costs and that caused most of
the pollution problem. These limits
were the 100/250 tpy thresholds.
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Congress had reason to expect that with
these thresholds, the program would
approximate the size of the current PSD
program, which numbers in the
hundreds of sources each year.
Throughout its deliberations, Congress
focused primarily on emissions of
conventional pollutants.
But applying the 100/250 tpy
thresholds literally to sources of CO2
would sweep aside this carefully
designed construct by bringing in tens
of thousands of sources of a different
type and much smaller size than
Congress had in mind: Commercial and
residential sources whose primary—if
not sole—source of emissions is CO2
from small boilers that primarily
provide heat. Moreover, applying the
thresholds literally would bring in many
additional sources in the source
categories Congress expected PSD to
apply to, but of a size Congress expected
to be below the cut-off. Congress did not
intend to apply PSD to these sources
because of the expenses that compliance
with PSD entails and because Congress
did not view these sources as causing a
sufficiently great part of the pollution
problem. Including these sources would
also expand the PSD program to well
beyond what Congress had reason to
expect, and what permitting authorities
can administer.
The administrability problems lead
the results of applying the thresholds
literally beyond contravening
congressional intent and into actually
undermining congressional intent. At
least for an initial period, until
streamlining methods could be
developed, the extraordinary number of
sources subject to PSD would preclude
the permitting authorities from
processing permit applications for all
sources, including those that Congress
intended be subject to PSD. Because
PSD is a preconstruction program, those
sources would face many years of delay
before they could construct or modify,
which would undermine congressional
intent to allow economic growth in PSD
areas. These results are the types of
‘‘absurd results’’ from a literal reading of
statutory provisions that courts have
declined to sanction.
b. Title V
For title V, the application of the
absurd results doctrine parallels that of
PSD. First, a literal application of the
100 tpy threshold requirement in CAA
§§ 502(a), 501(2)(B), and 302(j) would be
in tension with a specific CAA
requirement, that of CAA § 503(c),
which imposes a time limit of 18
months from the date of receipt of the
completed permit application for the
permitting authority to issue or deny the
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permit. It would be flatly impossible for
permitting authorities to meet this
statutory requirement if their workload
increases from some 14,000 permits to
6.1 million. Instead, permit applications
would face multi-year delays in
obtaining their permits.
Moreover, these delays would
undermine the overall statutory design
that promotes the smooth-running of the
permitting process, and the very
purpose of the title V program itself. As
noted elsewhere, Congress intended
through title V to facilitate compliance
by establishing an operating permit
program that requires the source to
combine in a single permit all of its
CAA requirements. Congress established
a comprehensive process to implement
the operating permit program. Through
this process, following the date that
sources become subject to title V, they
have 1 year to submit their permit
applications. CAA § 503(c). As noted,
the permitting authority then has 18
months to issue or deny the permit.
CAA § 503(c). Permitting authorities
must provide an opportunity for public
comment and a hearing. CAA
§ 502(b)(6). If the permitting authority
proposes to issue the permit, the
permitting authority must submit the
permit to EPA, and notify affected
States, for review. CAA § 505(a)(1). EPA
then has 45 days to review the permit
and, if EPA deems it appropriate, to
object to the permit. CAA § 503(b)(1). If
EPA does object, then the permitting
authority must, within 90 days, revise it
to meet the objections, or else EPA
becomes required to issue or deny the
permit. CAA § 503(c). If EPA does not
object, then, within 60 days of the close
of the 45-day review period, any person
may petition EPA to object, and EPA
must grant or deny the petition within
60 days. This set of applicant,
permitting authority, and EPA actions
and deadlines establishes the process
for the prompt and efficient issuance of
operating permits for the appropriate
universe of sources.
The legislative history of title V,
enacted by Congress in the 1990 CAA
Amendments, indicates that Congress
expected the provisions to apply to a
much smaller set of sources than would
become subject at a 100-tpy GHG
threshold level. The Senate Committee
report noted that under the title V
provisions that would be enacted, ‘‘the
additional workload in managing the air
pollution permit system is estimated to
be roughly comparable to the burden
that States and EPA have successfully
managed under the Clean Water Act[,]’’
under which ‘‘some 70,000 sources
receive permits, including more than
16,000 major sources.’’ S. Rep. 101–228,
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at 353. Applying title V to GHG emitters
at the 100-tpy threshold would result in
approximately 6.1 million sources
becoming subject to title V, which is far
in excess of the number that Congress
contemplated.
Moreover, the great majority of these
sources will not be subject to any CAA
requirements, so that although they
would need to apply for and receive a
permit, there would be no applicable
requirements to include in the permit
and the exercise would not improve
compliance. But at least for an initial
period, until streamlining methods
could be developed, the extraordinary
numbers of these sources would sweep
aside Congress’ carefully constructed
program, with its multi-step process and
deadlines of as short as 45 days—and
instead, backlog the permit authorities
for many years. Multi-year delays in
issuance of all permits would ensue,
those for sources that have applicable
requirements and that Congress clearly
intended the program to cover, and for
the millions of sources that are not
subject to any applicable requirements.
Thus, as with PSD, a literal
interpretation of the title V threshold
provisions would apply title V to
millions of sources that Congress did
not intend be covered, and the ensuing
administrative burdens—at least
initially—would impede the issuance of
permits to the thousands of sources that
Congress did intend be covered. This
result is the type of ‘‘absurd results’’
from a literal application of statutory
provisions that the courts have held
should be avoided.
c. Application of PSD and Title V
Thresholds
Because a literal application of both
the PSD and title V threshold
requirements produces absurd results,
EPA may develop a different application
that promotes consistency with other
statutory provisions and is consistent
with congressional intent. We believe
that this proposal would achieve these
objectives by establishing a threshold
for the first phase at the level of 25,000
tpy CO2e, and committing to vigorous
efforts to streamline implementation of
both programs’ requirements and to
complete a study and then conduct
further rulemaking.
A first phase 25,000-tpy CO2e major
source GHG threshold, combined with
vigorous efforts to develop streamlining
methods, is consistent with
congressional intent for the PSD
provisions for several reasons. The
25,000-tpy CO2e threshold reconciles
the PSD provisions that, absent this
regulation, would be in tension with
each other, and thereby maintains the
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overall functioning of the PSD program.
The threshold maintains the
environmental purposes of the PSD
program, while allowing economic
growth, as set forth in CAA § 160. As
discussed elsewhere in this preamble, a
majority of stationary source GHG
emissions in the U.S. come from a
relatively small number of high-emitting
sources that would remain subject to
PSD because they emit at or above the
25,000-tpy CO2e threshold. By
comparison, about 75 percent of
stationary source GHG emissions come
from all sources above 250 tpy.
Accordingly, the 25,000-tpy CO2e
threshold would, during this first phase,
exempt from PSD numerous small
sources that emit only about 7 percent
of GHGs, and that smaller amount of
emissions coverage would not
jeopardize the environmental protection
goals of PSD. Moreover, the program
will remain of a manageable size, so that
permitting authorities will be able to
process permit applications and issue
permits, which sources must have to
construct or expand. As discussed
elsewhere, the information available to
us indicates that the 25,000-tpy CO2e
level is the level closest to the statutory
levels that permitting authorities can
reasonably administer during this initial
phase. The ‘‘absurd results’’ caselaw
requires that if a statutory provision
cannot be applied literally, then it
should be applied as close to literally as
possible, consistent with congressional
intent. With this level of 25,000-tpy
CO2e, permitting authorities would be
able to reasonably comply with the 12month deadline requirement for acting
on PSD permit applications under CAA
§ 165(c). Further, the first phase
threshold of 25,000 tpy and the
development of streamlining methods is
consistent with congressional intent to
limit the PSD program—with the high
costs that result from its source-bysource applications—to sources that can
bear the costs. The first phase would
allow for the implementation of
streamlining methods, which could
facilitate the orderly development of the
program by reducing the costs of
compliance for sources of GHG
emissions. In addition, the first phase
threshold maintains the program at a
manageable size so that permitting
authorities will be able to continue to
timely issue permits to sources seeking
to construct or expand.
The first phase 25,000-tpy CO2e
threshold, combined with the
development of streamlining methods
and the study and subsequent
regulations, is also consistent with the
purposes of the title V provisions. This
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first phase would assure a manageable
size for the program so that permitting
authorities could continue to issue
permits to sources with applicable CAA
requirements, as Congress intended. The
implementation of streamlining
methods—in particular, general
permits—could facilitate the orderly
development of the title V program to
include a broader set of sources based
on their GHG emissions.
B. ‘‘Administrative Necessity’’ Doctrine
1. Overview
Once EPA takes regulatory action to
trigger PSD and title V requirements for
GHG emitters, a literal application of the
PSD and title V applicability
requirements (i.e., the 100/250-tpy PSD
major stationary source threshold and a
‘‘zero’’ significance level threshold, and
the 100-tpy title V threshold) would
result in a volume of permit
applications that is so high that the PSD
and title V programs would become
impossible for State and Federal
authorities to administer. The PSD and
title V permitting processes would
become overwhelmed and essentially
paralyzed.
Under these circumstances, the
judicial doctrine of administrative
necessity authorizes EPA to undertake a
process for rendering the PSD and title
V requirements administrable. As part
of this process, EPA must consider ways
to streamline the PSD and title V
definitions and operative requirements
so that the permitting authorities may
more efficiently process the expected
influx of GHG permit applications.
These streamlining methods may
include refinements to the definition of
PTE and issuance of some form of
general permits with presumptive
BACT. See section VII.A of this
preamble for a description of what these
streamlining methods entail for PSD and
title V programs, respectively.
However, the development, adoption,
and implementation of these
streamlining approaches would take
several years, and, upon their
completion, would still leave permitting
authorities confronting a sufficiently
large increase in workload that, absent
a corresponding increase in resources,
would continue to render the PSD and
title V programs impossible to
administer. See section VII of this
preamble for an explanation of the
procedures and timeframes necessary to
develop these streamlining techniques.
As a result, under the doctrine of
administrative necessity, EPA is
authorized to phase in the PSD and title
V requirements in as refined a manner
as possible, so as to allow
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administration of the PSD and title V
programs. As part of the first phase, EPA
proposes to establish the thresholds at
the levels proposed, as well as
undertake streamlining as much as
possible and as quickly as possible, and
explore with permitting authorities
methods to ramp up resources for
processing GHG permit applications.
EPA also commits to conduct an
assessment of the administrability issue
within 5 years and, by the end of 1 year
later, promulgate the second phase of
the tailoring process, which would
include the thresholds and streamlining
methods determined at that time to be
appropriate.
2. Chevron Standard for Statutory
Interpretation
As noted above, the PSD requirements
apply to the construction and
modification of a ‘‘major emitting
facility,’’ CAA §§ 165(a)(1), 169(2)(C),
which is defined as a ‘‘stationary
source[ ] [in one of 28 listed categories
of sources] of air pollutants which
emit[s], or ha[s] the potential to emit,
one hundred tons per year or more of
any air pollutant’’ or ‘‘any other source
with the potential to emit two hundred
and fifty tons per year or more of any
air pollutant,’’ with certain exceptions.
CAA § 169(1). The title V requirements
apply to any ‘‘major source,’’ CAA
§ 502(a), which is defined to include
‘‘any stationary facility or source of air
pollutants which directly emits, or has
the potential to emit, one hundred tons
per year or more of any air pollutant.’’
CAA §§ 501(2)(b), 302(j).
Although these applicability
provisions are clear by their terms, the
Courts have held that the Chevron
approach of applying the literal
language of the provisions may not
apply when the administrability of the
provisions is at issue.
3. Doctrine of Administrative Necessity
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a. Administrative Necessity Doctrine in
the Context of Chevron
The Courts have acknowledged the
administrative necessity doctrine as an
overlay on the Chevron doctrine of
statutory construction, so that even
when a statutory requirement expresses
a clear congressional intent, if the
provision is impossible for the agency to
administer, then the agency is not
required to follow the literal
requirements, and instead, the agency
may adjust the requirements in as
refined a manner as possible to assure
that the requirements are administrable,
while still achieving Congress’s overall
intent. As discussed below, the D.C.
Circuit set out the doctrine of
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‘‘administrative necessity’’ in a line of
cases that most prominently includes
Alabama Power v. Costle, 636 F.2d 323
(D.C. Cir. 1980). The Court cited the
doctrine most recently in New York v.
EPA, 443 F.3d 880, 884, 888 (D.C. Cir.
2006).18
First, the D.C. Circuit described the
basis for the administrative necessity
doctrine as, in effect, an overlay on clear
statutory intent. Specifically, in a
section of the opinion titled,
‘‘Exemptions Born of Administrative
Necessity,’’ the Court stated:
b. Alabama Power
The Court provided its most robust
expression of the ‘‘administrative
necessity’’ doctrine in the seminal
decision, Alabama Power Co. v. Costle,
636 F.2d 323 (D.C. Cir. 1980) (Alabama
Power), a case that resolved industry
and citizens group challenges to many
aspects of the regulations EPA
promulgated shortly after enactment of
the 1977 CAA Amendments to
implement the newly enacted statutory
provisions. One regulatory provision
purported to exempt sources that
qualified as major emitting facilities if
their actual emissions were 50 tpy or
less. EPA sought to justify this provision
on grounds that some 2,400 major
emitting facilities emit 50 tpy or less,
and that the large burdens on the agency
and industry of permit development and
review would outweigh the small
benefits of permitting. The Court
invalidated this regulatory exemption as
not authorized by the statute, but in so
doing, recognized EPA’s concerns about
administrative burdens and,
anticipating future agency efforts to
adjust statutory mandates to
administrative realities, went on to
articulate the basis for the
administrative necessity doctrine.19 636
F.2d at 356–57.
Certain limited grounds for the creation of
exemptions are inherent in the
administrative process, and their
unavailability under a statutory scheme
should not be presumed, save in the face of
the most unambiguous demonstration of
congressional intent to foreclose them.
18 It should be noted that numerous cases have
held that an agency may consider administrative
factors in choosing regulatory policies under
statutory provisions that authorize choices. See,
e.g., National Mining Association v. EPA, 59 F.3d
1351, 1364 (D.C. Cir. 1995); Phillips Petroleum Co.
v. EPA, 803 F.2d 545, 562 (D.C. Cir. 1986); National
Wildlife Federation v. Gorsuch, 693 F.2d 156, 182
(D.C. Cir. 1982). While these cases support the
general proposition that administrative
considerations are important, they differ from the
‘‘administrative necessity’’ doctrine because in
those cases, the Agency’s actions were within the
ambit of the statutory language; whereas under the
‘‘administrative necessity’’ doctrine, the Agency’s
actions depart from the statutory language.
19 The Court also explained that in that case,
EPA’s concern that large numbers of small sources
would be subject to PSD was misplaced because it
was based on an erroneous interpretation of the
requirement that the threshold for determining
whether a source was a major emitting facility (and
thereby subject to PSD) was the source’s PTE. EPA
erroneously believed that PTE had to be calculated
without reference to pollution controls, an
interpretation that would have meant that many
sources of a low level of actual emissions would be
treated as major emitting facilities. The Court held,
in another part of the Alabama Power opinion, that
PTE must be calculated with reference to pollution
controls, and went on to observe that this holding
effectively mooted EPA’s concerns that underlay its
effort to exempt 50-tpy-or-less sources from PSD
requirements.
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Id. at 357.
Second, the Court identified several
types of administrative relief that may
be available to an agency. One is
‘‘[c]ategorical exemptions from the clear
commands of a regulatory statute,’’
which the court stated are ‘‘sometimes
permitted,’’ but emphasized ‘‘are not
favored.’’ Id. at 358. A second is ‘‘an
administrative approach not explicitly
provided in the statute,’’ such as
‘‘streamlined agency approaches or
procedures where the conventional
course, typically case-by-case
determinations, would, as a practical
matter, prevent the agency from carrying
out the mission assigned to it by
Congress.’’ Id. A third is a delay of
deadlines upon ‘‘a showing by [the
agency] that publication of some of the
guidelines by that date is infeasible.’’ Id.
at 359 (quoting NRDC v. Train, 510 F.2d
692, 712 (D.C. Cir. 1974).
Finally, the Court explained it would
evaluate whether the agency faced an
administrative impossibility, and the
acceptability of the agency’s choices,
based on the essential circumstances
confronting the agency, including the
volume and nature of the tasks required
of the agency, its financial and
personnel resources, and the time
available to it. Specifically, the Court
observed that the administrative
necessity doctrine would apply based
on the ‘‘administrative need to adjust to
available resources * * * where the
constraint was imposed * * * by a
shortage of funds * * *, by a shortage
of time, or of the technical personnel
needed to administer a program.’’ Id. at
358. The Court added that another
administrative constraint could be ‘‘the
degree of administrative burden posed
by enforcement.’’ Id. at 405. See NRDC
v. Train, 510 F.2d 692, 712 (D.C. Cir.
1974) (recognizing constraints imposed
by budgetary commitments, manpower
demands, or inability to evaluate
sufficiently the necessary scientific and
technical determinations).
Even so, the Court went on to caution
that ‘‘administrative necessity’’ is a high
hurdle: ‘‘[T]he agency [bears] a heavy
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burden to demonstrate the existence of
an impossibility.’’ Id. at 359. The Court
particularly noted its reticence to
uphold agency claims of administrative
impossibility when those claims are
made in advance of actual efforts to
administer or enforce: ‘‘The agency’s
burden of justification in such a case is
especially heavy.’’ Id. at 359.
In Alabama Power, the D.C. Circuit
emphasized that its exposition of the
administrative necessity doctrine was
consistent with U.S. Supreme Court
decisions holding that administrative
considerations could factor into agency
decisions. The D.C. Circuit noted that
the Supreme Court, in Permian Basin
Area Rate Cases, 390 U.S. 747 (1968),
‘‘approv[ed] the adopting by the FPC of
area rate regulation as the practical
means to regulate thousands of natural
gas producers,’’ and quoted the
Supreme Court as explaining,
‘‘[c]onsiderations of feasibility and
practicality are certainly germane to the
issues before us. * * * We cannot, in
these circumstances, conclude that
Congress has given authority inadequate
to achieve with reasonable effectiveness
the purpose for which it has acted.’’
Alabama Power, 636 F.2d at 359 (citing
Permian Basin Area Rate Cases, 390
U.S. at 777). The Court in Alabama
Power also cited Morton v. Ruiz, 415
U.S. 199, 230–31 (1973), in which the
Supreme Court ‘‘acknowledged the
substantive authority of the Secretary [of
the Bureau of Indian Affairs] to take
appropriate action to cope with the
administrative impossibility of applying
the commands of the substantive
statute. Alabama Power, 636 F.2d at
359.20
20 Although Alabama Power presented the D.C.
Circuit’s most robust exposition of the
administrative necessity doctrine, the Court first
identified the doctrine, albeit in the relatively
narrow application of a deadline extension, in the
1974 decision, NRDC v. Train, 510 F.2d 692 (D.C.
Cir. 1974). There, the Court considered EPA
objections that it would be unable to meet a
statutory requirement that established a deadline
for promulgating effluent limitations. While
declining to grant extensions of the deadline in that
case, the Court acknowledged that under certain
circumstances, judicial relief in the form of a
deadline extension would be warranted in light of
administrative considerations. The Court observed
that ‘‘budgetary commitments and manpower
demands’’ needed to meet a deadline could be
‘‘beyond the agency’s capacity or would unduly
jeopardize the implementation of other essential
programs;’’ and that ‘‘EPA may be unable to
conduct sufficient evaluation of available control
technology’’ by the deadline. Under these
circumstances, the Court stated, ‘‘[t]he courts
cannot responsibly mandate flat * * * deadlines
* * *.’’ The Court grounded its conclusion, that a
court could consider administrative considerations
in evaluating an agency’s claimed inability to meet
a statutorily mandated deadline, in a court’s
equitable powers to fashion appropriate relief. Id.
at 713 (citations omitted). Although the NRDC v.
Train decision concerned the agency’s compliance
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It should be emphasized that the
Court in Alabama Power discussed the
‘‘administrative necessity’’ doctrine in
the context of PSD applicability, which,
along with title V applicability, is the
subject of this action. The Court
discussed the doctrine extensively in
the part of its opinion that followed its
invalidation of EPA regulations that
attempted to overlay an exemption for
PSD applicability onto statutory
requirements, where the Court stated it
was anticipating future agency efforts to
adjust statutory mandates to
administrative realities. Id. at 356–57.
Moreover, the Court made clear in
another part of its opinion that the
doctrine could be applied to another
aspect of PSD applicability, concerning
existing sources. There, the Court stated:
EPA does have discretion, in administering
the statute’s ‘‘modification’’ provision, to
exempt from PSD review some emission
increases on grounds of de minimis or
administrative necessity.
Id. at 400.
c. Case Law After Alabama Power
Shortly after Alabama Power, the D.C.
Circuit reiterated the validity of the
‘‘administrative necessity’’ doctrine in
EDF v. EPA, 636 F.2d 1267 (D.C. Cir.
1980), which reviewed the legality of
EPA’s regulation of polychlorinated
biphenyls (PCBs) under the Toxic
Substances Control Act. As the Court
noted, ‘‘The statutory language is
simple: ‘‘no person may * * * use any
polychlorinated biphenyl in any manner
other than in a totally enclosed
manner.’’ 15 U.S.C. 2605(e)(2)(A).
Similarly, the prohibitions on
manufacture, processing, and
distribution refer to ‘‘any
polychlorinated biphenyl.’’ See id.
§ 2605(e)(3)(A).’’ EDF v. EPA, 636 F.2d
at 1281. EPA’s regulations exempted
materials containing concentrations of
PCBs less than 50 parts per million
(ppm). EPA justified the 50-ppm cutoff
as an exemption based on
administrative necessity. The Court
reiterated that such an exemption was at
least potentially available. Quoting
Alabama Power, the Court stated:
Under the heading of ‘‘administrative
necessity,’’ this court has recognized that an
agency may depart from the requirements of
a regulatory statute. * * * While the court in
Alabama Power emphasized that ‘‘categorical
exemptions from the clear commands of a
regulatory statute, though sometimes
permitted, are not favored.’’ Id. at 358–360,
with deadlines, which are a relatively narrow issue,
the case established the proposition that an agency
may, under certain circumstances, depart from a
statutory mandate due to administrative
considerations.
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it also noted that there is ‘‘substantive
authority (for an agency) to take appropriate
action to cope with the administrative
impossibility of applying the commands of
the substantive statute.’’ Id. at 358–359.
EDF v. EPA, 636 F.2d at 1283. However,
on the facts before it, the Court found
that EPA had not ‘‘made [a] showing
that it cannot carry out the statutory
commands for concentrations of PCBs
below fifty ppm,’’ and therefore that
‘‘EPA [had] fail[ed] to meet its heavy
burden. Thus, administrative need, on
this record, provides no basis for the
fifty ppm cutoff.’’ Id.
Some 3 years later, the D.C. Circuit
handed down a decision concerning the
‘‘administrative necessity’’ doctrine in
Sierra Club v. EPA, 719 F.2d 436, 463
(D.C. Cir. 1983). There, the Court
reviewed EPA’s efforts to justify a
narrow regulatory definition of
‘‘dispersion techniques’’ on
administrative necessity. CAA § 123
prohibits the use of tall stacks and
‘‘other dispersion techniques’’ to meet
emissions limitations. The Court found
that the term ‘‘dispersion techniques’’
should be defined broadly ‘‘to
encompass * * * the use of devices,
alterations to the stack, or other
techniques when they are significantly
motivated by an intent to gain emissions
credit for greater dispersion.’’ Id. at 462.
EPA’s regulations defined the term
narrowly to include only certain types
of equipment, and not to require an
inquiry into intent. The Court observed,
that ‘‘[s]ince the regulations do not
regulate all the techniques contained in
this definition, the regulations
effectively create an exemption not
indicated in the statute itself. Such
categorical exemptions are generally not
favored * * * but there are two
situations in which they are allowed:
Cases of administrative necessity and de
minimis situations’’ (citing Alabama
Power). Id. Thus, the Court affirmed that
the doctrine of ‘‘administrative
necessity’’ could be used to allow an
agency to depart from the requirements
of the statute.
The Court went on to find, however,
that in this case, EPA’s justification for
‘‘administrative necessity’’ was not
sufficient. EPA had explained that
defining ‘‘dispersion techniques’’ more
broadly to necessitate inquiring into a
source’s subjective intent as to whether
other equipment or methods were
designed to disperse emissions, as
opposed to achieving some other end,
would be ‘‘difficult’’ to enforce, a
conclusion generally supported by a few
State and local agencies that commented
on the rule. The Court found that the
Agency’s narrow definition of
‘‘dispersion techniques’’ amounted to a
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categorical exemption from statutory
requirements, and one that was based
on Agency predictions of future
enforcement difficulties rather than
actual experience. The Court reiterated
its statements in Alabama Power under
these circumstances, that the Agency’s
burden of showing impossibility is
especially heavy, and that in this case,
EPA’s showing ‘‘falls far short.’’ Id. at
463. The Court added that EPA may be
able to develop ‘‘less taxing’’ ways to
define ‘‘dispersion techniques,’’
including developing classes of plant
techniques that could be considered to
be dispersion techniques. Id.21
In 1989, in Public Citizen v. FTC, 869
F.2d 1541 (D.C. Cir. 1989), the D.C.
Circuit reiterated the validity of the
‘‘administrative necessity’’ doctrine,
although on the facts, the Court held
that the Federal Trade Commission’s
(FTC) claims of administrative necessity
failed. There, the Court considered the
Smokeless Tobacco Act, which,
according to the Court, ‘‘imposes a
blanket requirement, subject only to one
narrow and specifically mentioned
exception for billboard advertising, that
producers and distributors of smokeless
tobacco products must include a
warning label whenever they ‘advertise
* * * any smokeless tobacco product.’
15 U.S.C. 4402(a)(2).’’ Id. at 1553. In the
face of this provision, the FTC issued an
21 Shortly after Sierra Club, the D.C. Circuit
considered another case that raised an
‘‘administrative impossibility’’ issue, Northern
Colorado Water Conservancy Dist. v. FERC, 730
F.2d 1509 (D.C. Cir. 1984) (NCWCD). However,
there the Court did not appear to follow the line of
cases that included Alabama Power. In NCWCD, the
Court found that the Federal Energy Regulatory
Commission (FERC) improperly failed to comply
with requirements under section 4(f) of the Federal
Power Act to give written notice to local water
authorities of preliminary permit applications filed
by private developers for a hydroelectric power
project. In failing to give notice, FERC had followed
a longstanding, but unannounced policy, which it
justified in part on grounds ‘‘that strict adherence
to the statute’s language would be administratively
impossible.’’ FERC explained that the requirement
to notify municipalities required administrative
flexibility in light of the ‘‘estimated 50,000
specialized local governmental units performing a
myriad of services,’’ many of which, ‘‘such as water,
utility or drainage districts, are not readily
identifiable.’’
The Court rejected FERC’s contention that those
administrative concerns justify FERC’s practices.
Without citing Alabama Power or any of its other
decisions concerning the ‘‘administrative necessity’’
doctrine, the Court stated that those practices must
nevertheless remain ‘‘within a range of
reasonableness with respect to Congress’
instruction,’’ that is, within the ambit of the
statutory requirements, as well as be reasonably
well articulated and generally made known to the
public, and that in this case, FERC’s practices failed
on all those counts. 731 F.2d at 1521.
Notwithstanding this case, the weight of the D.C.
case law supports the availability of the
administrative necessity doctrine to authorize
agency departure from statutory requirements in
limited circumstances.
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exemption for utilitarian items (ranging
from golf balls to T-shirts) distributed
for promotional purposes, so that such
objects would not need to include the
warning label. The FTC attempted to
justify the exemption on grounds of
administrative necessity. The Court
acknowledged the doctrine, stating that
‘‘there exists a narrow range of inherent
discretion in an agency to create caseby-case exceptions in order to come
within the practical limits of feasibility
in administering a statute.’’ Id. at 1556
(citing Alabama Power) (emphasis
added by Court). However, the Court
went on to dismiss the FTC’s claims of
administrative necessity, stating that the
FTC had not justified its application and
suggesting that the FTC had improperly
undertaken a cost-benefit analysis in the
guise of an administrative necessity
claim. Id.
d. Analogous Case Law Concerning
Other Legal Obligations
There is another line of case law,
which involves contempt-of-court
proceedings, in which the Courts
recognize that impossibility of
performance is relevant to the lawful
discharge of legal obligations, and this
case law provides some analogous
support to the administrative necessity
doctrine. In contempt-of-court
proceedings, as the Supreme Court has
noted, ‘‘a defendant may assert a present
inability to comply with the order in
question’’ and may thereby be excused
from the duty to comply. U.S. v.
Rylander, 460 U.S. 752, 757 (1983)
(citing Maggio v. Zeitz, 333 U.S. 56, 75–
76 (1948); Oriel v. Russell, 278 U.S. 358,
366 (1929)) (emphasis in original)
(‘‘Rylander’’). In addition, as discussed
below, this doctrine applies fully to
administrative agencies, providing even
closer analogous support for the
doctrine of administrative necessity.
Even so, it should be acknowledged that
the extent of support is limited because
the contempt-of-court line of cases
involves a court’s equitable discretion in
enforcing court orders, and the
administrative necessity line of cases
involves the extent to which a Court
will allow deviation from explicit
statutory requirements.
In Rylander, which involved a
corporate officer’s failure to comply
with a civil contempt order imposed for
noncompliance with an earlier order
enforcing an IRS summons, the Court
stated that ‘‘[w]hile the court is bound
by the enforcement order, it will not be
blind to evidence that compliance is
now factually impossible. Where
compliance is impossible, neither the
moving party nor the court has any
reason to proceed with the civil
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contempt action.’’ Rylander, 460 U.S. at
757 (finding that contemnor failed to
meet the burden of production sufficient
to establish an impossibility defense).
The D.C. Circuit, noting that ‘‘[i]t is
well established that impossibility of
performance constitutes a defense to a
charge of contempt,’’ has recognized
that the Court has an obligation to
‘‘consider carefully a claim by the
alleged contemnor that compliance was
impossible. * * * Although both the
fact and duration of noncompliance
with [an] order are elements to be
considered, the court must consider as
well [a party’s] inability, without fault
on its part, to render obedience.’’
Tinsley v. Mitchell, 804 F.2d 1254 (D.C.
Cir. 1986) (quoting SEC v. Ormant Drug
& Chemical Co., 739 F.2d 654, 656–57
(D.C. Cir. 1984)) (remanding to District
Court to adjudicate contemnor’s claim
of inability to pay fines).
Importantly, the doctrine is fully
available to government agencies, as the
D.C. Circuit affirmed in Evans v.
Williams, 206 F.3d 1292 (D.C. Cir.
2000). There, in a class action
challenging conditions at a public
institution for the mentally retarded, the
District of Columbia failed to comply
with deadlines set in a consent decree,
citing unanticipated ‘‘financial
problems of horrendous proportions.’’
Id. at 1293. Discussing the district
court’s refusal to make retroactive a
modification of the consent decree
ameliorating the financial penalties for
missing deadlines, the Court noted,
We do not of course suggest that a party may
be relieved from the obligation to comply
with an injunction simply by making a
motion for a modification. But here the
District claimed that it could not comply,
despite making a good faith effort to do so.
If true, this should have relieved it from
liability. See Tinsley v. Mitchell, 804 F.2d
1254, 1256 (D.C. Cir. 1986) (‘‘If a party lacks
the financial ability to comply with an order,
the court cannot hold him in contempt for
failing to obey.’’)
Id. at 1299. Finding that the district
court based its order on irrelevant
information regarding the District’s
financial circumstances, the Court
reversed and remanded for further
proceedings. Id.
The Courts have also recognized that
a party may avoid compliance with a
court order by showing that it made a
good-faith effort to comply but fell
short, and that under these
circumstances, the party is not required
to demonstrate that compliance is
absolutely impossible. In Washington
Metropolitan Transit Authority v.
Amalgamated Transit Union, 531 F.2d
617 (D.C. Cir. 1976), the D.C. Circuit
vacated a final contempt judgment and
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fine against a labor union for continuing
to strike in contravention of a
restraining order; among other
procedural failings, the district court
made no findings of fact on the union’s
defenses of substantial compliance and
inability to comply. Id. at 619–20. In
directing the district court to provide
adequate due process on remand, the
court emphasized, ‘‘[e]valuation of good
faith efforts to comply, once raised, is
necessary to determine the possibility of
compliance. In our view good faith
should also be considered in mitigation
of penalty.’’ Id. at 621 (citation omitted).
This aspect of the doctrine is also
fully applicable to agencies. In Chairs v.
Burgess, 143 F.3d 1432 (11th Cir. 1998),
the Eleventh Circuit emphasized that
good-faith compliance efforts by a State
agency could support a claim for relief
based on impossibility. There, the State
of Alabama was required under a
consent decree to remove State
prisoners from a county jail within a
certain timeframe. Id. at 1434. The
county sought a court order to enforce
the decree and requested that the Court
hold the State in contempt. Id. In light
of the fact that the State was then
subject to 79 identical court orders, the
Court accepted the State’s defense of
present inability to comply due to
‘‘entirely inadequate’’ resources in the
State prison system. Id. at 1437. The
Court vacated the district court’s order,
declaring: ‘‘ ‘Inability,’ as a defense to
contempt, does not mean that
compliance must be totally impossible.
Instead, the inability that will absolve a
party from being held in contempt
requires only that the noncomplying
party has made ‘in good faith all
reasonable efforts to comply’ with the
terms of a court order.’’ Id. (citations
omitted).
3. Step-by-Step Process for
Implementing the Administrative
Necessity Doctrine
We believe that the administrative
necessity case law establishes a threestep process under which an
administrative agency may, under the
appropriate circumstances, in effect
revise statutory requirements that the
agency demonstrates are impossible to
administer so that they are
administrable. This section of the
preamble describes the requirements for
each step, along with a brief application
of each step to PSD permitting
thresholds and significance levels as
well as title V permitting thresholds.
In brief, the three steps are as follows:
When an agency has identified what it
believes may be insurmountable
burdens in administering a statutory
requirement, the first step the agency
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must take is to evaluate how it could
streamline administration as much as
possible, while remaining within the
confines of the statutory requirements.
The second step is that the agency must
determine whether it can justifiably
conclude that even after whatever
streamlining of administration of
statutory requirements (consistent with
those statutory requirements) it
conducts, the remaining administrative
tasks are impossible for the agency
because they are beyond its resources,
e.g., beyond the capacities of its
personnel and funding. If the agency
concludes with justification that it
would be impossible to administer the
statutory requirements, as streamlined,
then the agency may take the third step,
which is to phase in or otherwise adjust
the requirements so that they are
administrable. However, the agency
must do so in a manner that is as refined
as possible so that the agency may
continue to implement as fully as
possible Congressional intent.
Step 1: Reduce administrative
burdens by streamlining administration
as much as legally permissible. When an
agency has identified what it believes
may be insurmountable burdens in
administering a statutory requirement,
the agency must first evaluate how it
could streamline administration as
much as possible, while remaining
within the confines of the statutory
requirements. Sierra Club, 719 F.2d at
463 (even if EPA’s claims that its
method for enforcement ‘‘is in fact
impossible, there nevertheless may be
less taxing ways to enforce the law’’);
Alabama Power, 636 F.2d at 358
(‘‘Courts frequently uphold streamlined
agency approaches or procedures where
the conventional course, typically caseby-case determinations, would, as a
practical matter, prevent the agency
from carrying out the mission assigned
to it by Congress’’).
As discussed in detail below, EPA
believes that it may have several
potentially useful tools available in the
streamlining toolbox for the PSD
permitting threshold level, the PSD
significance level, and the title V
permitting threshold. For the PSD
permitting threshold level and
significance level, there are at least three
such tools: The first is interpreting the
definition of ‘‘potential to emit’’ so that
the amount of a source’s emissions that
counts in determining whether it
qualifies as a major source and therefore
is above the permitting threshold
requirements is closer to the amount of
its emissions when it is in actual
operation, rather than the amount of
emissions that the source would emit if
it were operating continuously.
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Narrowing the definition of PTE is a
potentially extremely important tool in
this context because identifying the
amount of a source’s emissions as closer
to its actual emissions in this manner
would mean that very large numbers of
residential and commercial sources
would have significantly lower
emissions and would fall below the
statutory threshold requirements for
triggering PSD. Second, EPA believes it
may be able to develop programs
involving general permits, under which
large numbers of similarly situated
sources would each be covered by
essentially the same permit established
through a regulatory action by the
permitting authority. This approach
could achieve economies of scale and
thereby reduce administrative burden.
Third, EPA believes it may be able to
streamline the single most timeconsuming element of the PSD permit
program, which is the determination of
BACT as required under CAA
§ 165(a)(4), by establishing presumptive
BACT levels for certain source
categories that comprise large numbers
of sources. As for title V, as discussed
below in detail, EPA believes that
defining ‘‘potential to emit’’ to reflect
more closely a source’s actual operation
and developing a program of general
permits could streamline the
administration of title V permits.
As also discussed below, these
streamlining efforts cannot be
implemented as soon as PSD and title V
are triggered, or even shortly thereafter.
However, EPA intends to develop these
streamlining methods as vigorously and
as quickly as possible and phase them
into the program. These streamlining
methods were described in the ANPR
and EPA received comment on them,
and EPA is continuing to develop the
methods and to solicit further comment
with this action.
Step 2: Determine that the task that
remains is impossible to administer.
The agency must determine whether it
can justifiably conclude that even after
whatever streamlining of administration
of statutory requirements the agency is
able to effectuate, the agency’s
remaining administrative tasks are
impossible for the agency because they
are beyond its resources. To make this
determination, the agency must
consider: (1) When it can complete
streamlining administration of the
statutory requirements and how well it
can administer those requirements in
the meantime; and (2) what
administrative tasks would remain after
it achieves streamlining and how well it
can handle those tasks. To make this
latter determination, the agency must
compare its resources to the tasks at
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hand. The agency must then determine
whether it can administer the statutory
requirements as mandated by Congress,
or whether it may justifiably conclude
that those requirements remain
impossible to administer.
As discussed below, PSD and title V
requirements will become applicable to
very large numbers of sources
immediately following a final rule
regulating GHG emissions. EPA expects
to complete such a rule, establishing
emissions limits for motor vehicles, by
the end of March 2010.
As discussed below, although EPA
intends to aggressively develop
streamlining methods to the extent
feasible, EPA simply does not have time
to do so prior to the date that we expect
PSD and title V to become applicable.
As a result, EPA and the States will
have to implement PSD for those
sources as soon as PSD is triggered.
Preliminary information that we have
obtained concerning State permitting
authority resources, and data we
collected concerning the numbers of
sources that emit GHGs (using both a
CO2 and CO2e basis) at the 100- and
250-tpy levels, make clear that as of the
date that PSD and title V applicability
is triggered, the number of sources
needing permits would overwhelm
permitting authorities and thereby
effectively paralyze the permitting.
Specifically, the total number of PSD
permits that are issued in the U.S. is
approximately 280 per year. A
permitting authority’s action on each
PSD permit is resource-intensive
because for each permit, the authority
must apply source-specific BACT, apply
other source-specific requirements, and
allow public comment. However, EPA
estimates that when the PSD
requirements are triggered for sources of
GHGs, more than 40,000 PSD permits
both from newly constructed facilities
that emit at greater than 250 tpy (using
either a CO2 or CO2e metric) and from
modifications at existing major sources
will be required. Under the PSD
program as presently constituted,
permitting authorities’ actions on each
of these permits will be resourceintensive, as described above.
This volume of permitting represents
more than a 140-fold increase from the
current volume—again, approximately
280 permits per year—of major PSD
permits that are processed by permitting
authorities nationwide. We estimate that
this increase in volume of PSD permits
would require an annual increase in
labor hours of almost 44 times the
current labor allocation for PSD
programs. This increase in workload
would overwhelm the permitting
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authorities’ resources and paralyze the
permit issuance process.
The problem for title V purposes is
comparable. Specifically, the total
number of existing title V permits in the
U.S. is approximately 14,700. However,
EPA estimates that when the title V
requirements are triggered for sources of
GHGs, approximately 6.1 million
sources that emit at least 100 tpy (using
either a CO2 or CO2e metric) will be
required to obtain a title V permit.
These sources will be required to submit
a permit application within 1 year, and
the permitting authorities will be
required to act on those applications,
including allowing an opportunity for a
public hearing.
We estimate that this additional
volume of permitting would require an
annual increase in labor hours of almost
250 times the current labor allocation
for title V programs. Like the increase in
PSD workload, this increase in title V
workload, combined with the source-bysource nature of the permitting process
and the requirements for public input,
would overwhelm the permitting
authorities’ resources and paralyze the
permit issuance process.
For both PSD and title V permits,
permitting authorities would be
required to hire and train staff in
numbers that are multiples of their
current staff, a task that cannot be
accomplished—or, indeed, can barely be
begun—by the time PSD and title V
requirements become applicable to GHG
emitters.
Step 3: Implement a scheme that is
administrable, but in doing so, depart
from the statute as little as possible.
If the EPA concludes with
justification that it would be impossible
to administer the statutory
requirements, as streamlined, then the
agency may phase in or otherwise adjust
the requirements so that they are
administrable. However, the agency
must do so in a manner that is as refined
as possible so that the agency may
continue to implement as fully as
possible congressional intent.
In this tailoring rulemaking, EPA is
proposing, as the first phase, to establish
a temporary ‘‘major stationary source’’
threshold for PSD purposes, a temporary
‘‘significance level’’ threshold for PSD
purposes, and a temporary ‘‘major
source’’ threshold for title V purposes,
for sources that emit GHGs, to levels
that capture a significant share of GHG
emissions while rendering both
permitting programs administratively
feasible. The specific options proposed
for temporary thresholds and the
rationale for their selection are
described below.
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Moreover, and as explained in detail
below, EPA intends to proceed
aggressively to develop streamlining
methods, and it is possible that
permitting authorities will be able to
augment their permitting resources.
Even so, available information does not
confirm that EPA and the permitting
authorities will be able to rely on these
steps within 6 years after PSD and title
V requirements become applicable to
GHG emissions. Accordingly, it is
necessary to maintain the major
stationary source threshold and
significance level proposed and also
necessary to reassess the administrative
situation and conduct further
rulemaking to address it within 6 years.
5. Consistency With Case Law
EPA’s proposed application of the
administrative necessity doctrine to
phase in the major source permitting
thresholds for PSD and title V purposes,
and to establish the significance level
for PSD purposes, is consistent with the
case law.
It is clear under the D.C. Circuit case
law that the administrative necessity
doctrine is available under certain
circumstances, to authorize an agency to
‘‘depart from the requirements of a
regulatory statute.’’ EDF v. EPA, 636
F.2d at 1283 (citing Alabama Power).
Thus, it is clear that the doctrine may
be applied—under the appropriate
circumstances—to authorize EPA to
phase in the major source thresholds for
PSD and title V permitting as well as to
establish a PSD significance level.
Indeed, the D.C. Circuit established the
administrative necessity doctrine, in
Alabama Power, in the context of efforts
by EPA to establish thresholds for PSD
permitting of new and existing sources.
Alabama Power, 636 F.2d at 357, 400.
The D.C. Circuit has emphasized,
however, that the agencies have a high
threshold to justify the use of the
doctrine, EDF v. EPA, 636 F.2d at 1283,
and the Court did not uphold the
attempts by the agencies in those cases
to invoke the doctrine. EDF v. EPA, 636
F.2d at 1283; Sierra Club v. EPA, 719
F.2d at 463; Public Citizen v. FTC, 869
F.2d at 1556.
We believe that the facts here are
much more supportive of an
administrative necessity application
than in those cases. EPA’s application of
the administrative necessity doctrine
hews closely to the three-step process
that we read the case law to establish.
Step 1: Reduce administrative
burdens by streamlining administration
as much as legally permissible. In some
of the case law described above, the D.C.
Circuit emphasized that the agencies
had failed to consider means of solving
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their alleged administrative problems in
ways consistent with the statutory
requirements. In Sierra Club v. EPA, the
Court invalidated EPA’s effort to narrow
the definition of ‘‘dispersion
techniques’’ to only certain types of
equipment and thereby exempt from the
definition certain categories of methods
that were intended to disperse
emissions. The Court based its holding
in part on the grounds that EPA had
failed to explore available, ‘‘less taxing’’
regulatory alternatives that would
reduce the administrative burden of
determining the purpose of changes in
stack or plume parameters. Sierra Club
v. EPA, 719 F.2d at 463–64. The Court
offered examples of possible
streamlining measures, such as
quantifying the amount of plume rise
that could be presumed to have an
engineering rationale, or selectively
exempting classes of improvements that
have a trivial impact on the goals of the
CAA or for which use as a dispersion
technique was only theoretically
possible. Id. at 464. Stating that ‘‘[w]e
see no evidence that EPA has
adequately explored these regulatory
alternatives,’’ the Court overturned
EPA’s effective categorical exemption.
Id.
The Court used similar reasoning in
EDF v. EPA, where the Court found that
EPA’s proposed 50-ppm cutoff for
regulating PCBs was not
administratively necessary. EDF v. EPA,
636 F.2d at 155. There, although basing
its dismissal of the claim primarily on
EPA’s failure to make a prima facie
showing of impossibility, the Court
emphasized that statutorily authorized
alternatives were available to EPA. See
id. at 154–156. ‘‘While some cutoff may
be appropriate,’’ the Court noted, ‘‘the
Administrator did not explain why the
regulation could not be designed
expressly to exclude ambient sources,
thus directly fulfilling congressional
intent, rather than achieve that goal
indirectly with a cutoff, thereby partly
contravening congressional intent.’’ Id.
at 154.
Here, in contrast, EPA has begun the
process of narrowing the administrative
burden through means consistent with
the statutory requirements by evaluating
what streamlining approaches would be
feasible but, as discussed below, this
process is complex and EPA cannot
complete it for several years. EPA is
soliciting comment on those methods
and any others that may occur to
stakeholders or the public. In NRDC v.
Train, the Court indicated that an
agency’s diligent, good-faith efforts to
discharge its statutory responsibilities
will factor in favor of the Court’s
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resolution of an impossibility claim.
NRDC v. Train, 510 F.2d at 333.
Step 2: Determine that the task that
remains is impossible to administer. In
Alabama Power, the D.C. Circuit
described the administrative necessity
doctrine as rooted in agency workload
and resources: Specifically, the Court
stated that the administrative
impossibility doctrine would apply
based on the ‘‘administrative need to
adjust to available resources * * *
where the constraint was imposed
* * * by a shortage of funds * * *, by
a shortage of time, or of the technical
personnel needed to administer a
program.’’ 636 F.2d at 358. The Court
added that another administrative
constraint could be ‘‘the degree of
administrative burden posed by
enforcement.’’ Id. at 405. However, the
Court cautioned that ‘‘the agency [bears]
a heavy burden to demonstrate the
existence of an impossibility.’’ Id. at
359.
In several of the cases described
above, the D.C. Circuit emphasized that
the agencies had failed to meet their
heavy burdens of establishing
administrative impossibility. In NRDC
v. Train, EPA neglected to specify the
resource or methodological constraints
that prevented the agency from meeting
a mandatory deadline for promulgating
effluent limitation guidelines. NRDC v.
Train, 510 F.2d at 712–13. Although the
Court inferred from the imminent
deadline that the Agency would likely
experience a burden on its resources in
promulgating the guidelines for most
source categories, the Court was
reluctant to grant EPA an extension in
response to a merely conclusory
statement that compliance with the
deadline would be impossible. Id. at
713.
A few years later, in EDF v. EPA, the
Court based its dismissal of EPA’s
administrative necessity claim on the
fact that the Agency did not provide
sufficient data to support the claim that
administering the statute as written was
impossible. In that case, EPA failed to
provide information relating to the
amount of PCBs that would be left
unregulated by its use of a 50-ppm
cutoff, where the statute required ‘‘any’’
PCB to be prohibited. EDF v. EPA, 636
F.2d at 155. As a result, EPA could not
show that carrying out the statutory
requirements for concentrations of PCBs
below 50 ppm would be
administratively impossible. Id. ‘‘Thus,’’
the Court found, ‘‘administrative need,
on this record, provides no basis for the
fifty ppm cutoff.’’ Id. Furthermore, the
Court noted in a footnote that EPA’s
claim that the burden to industry
justified a categorical exemption was
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undermined by EPA’s lack of ‘‘firm
data’’ on the extent of the burden. Id. at
155, fn. 43.
Likewise, in Sierra Club v. EPA, EPA
alleged only that it would be ‘‘difficult’’
to administer a proposed subjective
intent test that would examine whether
dispersion techniques were used for the
prohibited purpose of achieving
compliance with emissions limitations.
Without more, the Court determined,
EPA’s showing fell ‘‘far short’’ of
meeting the heavy burden of
demonstrating the existence of an
impossibility. Sierra Club v. EPA, 719
F.2d at 461–62.22
Thus, in the cases concerning
administrative necessity, the agencies
generally did not attempt to quantify the
administrative workload and resource
constraints that they thought merited
departure from the statutory
requirements and instead limited
themselves to generally conclusory
assertions. In NRDC v. Train, the Court
recognized that EPA could cure its
insufficient record and demonstrate the
administrative impossibility of
complying with the deadline once it
specified the actual burden on its
resources. NRDC v. Train, 510 F.2d at
713. In the event that EPA could
demonstrate that ‘‘manpower or
methodological constraints’’ threatened
to delay the promulgation of guidelines
for particular categories of sources, the
Court held open the possibility of an
exemption from the deadline. Id. at 714.
Here, in sharp contrast to that case
law, EPA has developed specific factual
evidence concerning the administrative
difficulties of implementing PSD and
title V at the statutory threshold levels.
Moreover, those constraints are
compelling; it is clear from just the
evidence collected so far that at the time
that EPA expects to trigger application
of the PSD and title V programs to
sources that emit GHGs—which, if
based on a possible mobile source final
rulemaking, would be near the end of
March 2010—it will be flatly impossible
for permitting authorities to administer
the PSD and title V programs at the
statutory threshold levels. The massive
number of permits would overwhelm
the limited resources available to the
permitting authorities. EPA expects to
collect as much specific information
concerning administrability as possible
through the comment period.
22 In Public Citizen v. FTC, the D.C. Circuit
dismissed FTC’s claims of administrative necessity
where the agency’s rationale for its categorical
exemption appeared to rely on an impermissible
weighing of the relative costs and benefits of
compliance, rather than on the impossibility of
compliance. Public Citizen, 869 F.2d at 1556.
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The administrative burdens that EPA
confronts in administering the PSD and
title V thresholds have no precedent in
the case law. The closest situation
appears to be Alabama Power, where
the Court rejected EPA’s interpretation
of ‘‘potential to emit’’ as a matter of
legal interpretation, and not on
administrative necessity grounds, but
where the Court noted that EPA’s
interpretation would have brought
approximately 2,400 additional facilities
into the PSD program, which entailed
the case-by-case review and BACT
determination for each permit
application. Alabama Power, 636 F.2d
at 356. Even so, the PSD and title V
program burdens anticipated for GHG
emitters at the statutory thresholds are
exponentially greater than the burdens
alleged in Alabama Power. The
projected resource burden for
administering the PSD program alone
will be greater than 10-fold the burden
alleged in Alabama Power: Each year,
regulating GHGs under the CAA is
estimated to trigger PSD requirements
for approximately 41,000 sources that
emit at levels greater than the 100/250tpy threshold when they engage in new
construction or significant
modifications. As for title V, in total,
some six million permits would be
required, which would entail an
enormous expenditure of administrative
resources, as described elsewhere.
It should be acknowledged that the
D.C. Circuit has stated that the
administrative necessity doctrine is
particularly difficult to assert when the
agency had not yet tried to enforce the
statutory requirements. Sierra Club v.
EPA, 719 F.2d at 463. Although the
Court did not spell out its reasoning for
this distinction, a logical reason would
be that actual efforts to implement the
statutory provision would more clearly
establish the extent of the
administrative problems than would
advance predictions. Even so, the Court
left the door open to approving claims
of administrative necessity in advance
of actual implementation efforts. Here,
EPA does not propose to attempt to
administer the statutory thresholds once
PSD and title V requirements are
triggered for GHG emitters, but the
impact of the statutory thresholds on
permitting authority caseloads and
resources are so massive as to be
predictable with a sufficient degree of
accuracy to support a claim of
administrative necessity. EPA has
gathered a substantial amount of
evidence concerning those impacts and
intends to gather more through the
comment period on this notice. Under
these circumstances, it is not necessary
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to await actual implementation.
Attempting to do so—that is, allowing
the statutory thresholds to apply,
assessing the extent of the
administrative problem, and then
conducting rulemaking to raise the
thresholds—would leave the PSD and
title permitting process in disarray for
years.
Step 3: Phase-in the statutory
requirements to be administrable, but in
doing so, depart from the statute as little
as possible. In Alabama Power, the D.C.
Circuit listed the types of departures
from the statute that it would sanction,
under the appropriate circumstances, on
grounds of administrative necessity.
One is ‘‘[c]ategorical exemptions from
the clear commands of a regulatory
statute,’’ which the Court stated are
‘‘sometimes permitted,’’ but ‘‘are not
favored.’’ A second is an
‘‘administrative approach,’’ such as
‘‘streamlined agency * * * procedures’’
in lieu of, for example, case-by-case
determinations, and a third is a delay of
deadlines. 636 F.2d at 358.
Here, turning first to PSD, EPA is
proposing to phase in the threshold for
PSD permitting, which would have the
effect of allowing sources that are above
the statutory threshold of 100/250 tpy
but below the regulatory threshold of
25,000 tpy CO2e to build new facilities
or modify existing ones without being
subject to PSD. Thus, this proposal is a
type of exemption.
Although the Court has said that
‘‘categorical exemptions’’ are ‘‘not
favored,’’ the Court has indicated that
they are ‘‘sometimes permitted,’’ and
the exemption at issue here is one that
should be permitted. For one thing, it is
time limited. In addition, during phase
one of the phase-in period, establishing
the thresholds at 25,000 tpy CO2e and
[10,000 to 25,000] tpy CO2e, and thereby
exempting sources from PSD
applicability at the time that they
construct or modify, is the only way to
address the administrative burdens that
would otherwise result at the time that
PSD is triggered. At that time, EPA will
not have been able to develop any
streamlining methods, which is the
second type of relief that the D.C.
Circuit identified in Alabama Power.
Even so, this proposal is that, as quickly
as possible, during the next 6 years, EPA
will implement as extensive a
streamlining of PSD requirements as
possible (consistent with statutory
requirements) and then will reassess the
administrative burdens and conduct
additional rulemaking concerning the
thresholds and streamlining techniques.
This approach has the potential to limit
the extent of the exemption. It should be
noted that a deferral of the permitting
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obligation, which is the third type of
relief that the D.C. Circuit identified,
would not be useful. For PSD purposes,
because sources cannot construct or
modify without first obtaining a permit,
a deferral would prevent construction
and modification activities. In addition,
a deferral would simply create a backlog
that would quickly become
unmanageable at any foreseeable point
in the future and would create
unacceptable uncertainty for the
regulated community. In particular,
because sources cannot construct or
modify without first obtaining a permit,
the backlog would prevent construction
and modification activities.
As discussed elsewhere, for PSD
purposes, the 25,000-tpy and [10,000 to
25,000] tpy CO2e levels proposed for the
major source permitting threshold and
significance level, respectively, are the
lowest levels that we believe permitting
authorities will be able to administer for
the upcoming 6-year period. By the end
of the first 5 years, EPA will conduct a
study and, within the following year,
will conduct another rulemaking to
revisit and possibly revise those
thresholds, depending on the Agency’s
findings of the maximum extent to
which permitting authorities can
administer the statutory program. In this
manner, the levels proposed are the
least possible departure from the
statutory requirements.
For the title V purposes, the first
phase threshold level of 25,000 tpy
CO2e must also be considered to be the
narrowest possible departure from the
statutory requirements because it is the
lowest amount that is administrable and
because there are no other choices.
There is not enough time for EPA to
develop streamlining measures or for
the States to ramp up resources.
Although sources have 1 year to submit
permit applications, and, once they
submit them, they receive the
protections of the permit shield, failure
to phase in the threshold level would
leave permitting authorities confronting
an influx of millions of permit
applications that would begin within a
year. Little can be done during that year
to meaningfully streamline the program.
In addition, for title V purposes, the
first-phase threshold must be
considered a deferral of, and not an
exemption from, permitting obligations
because existing sources must apply
periodically for a title V permit. That is,
if, during the second-phase rulemaking,
EPA lowers the threshold, sources that
are able to avoid title V permitting
obligations under the first phase may be
required to obtain a title V permit.
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C. Step-by-Step Process
In addition to the ‘‘absurd results’’
and ‘‘administrative necessity’’ case
law, a separate line of cases may be
relevant for this action: Cases that have
held that agencies may approach
problems one step at a time. In these
cases, the Courts have dismissed
challenges to agency actions that
implement part of, but not the entirety
of, a statutory mandate, on grounds that
agencies may proceed in an incremental
fashion. In these cases, the Courts
emphasized that the agency’s partial
action was a step in an overall path
toward achieving full implementation of
the statutory mandate. We solicit
comment on whether this caselaw is
supportive of our action in this notice.
In Massachusetts v. EPA, 549 US 497,
524 (2007), the U.S. Supreme Court, in
holding that EPA has authority under
the Clean Air Act to regulate GHG
emissions, noted that ‘‘[a]gencies, like
legislatures, do not generally resolve
massive problems in one fell regulatory
swoop.’’ 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.’’
The D.C. Circuit, in Grand Canyon Air
Tour Coalition v. FAA, 154 F.3d 455,
477–78 (DC Cir 1998), considered a
challenge to the Federal Aviation
Administration’s (‘‘FAA’’) final rule for
reduction of aircraft noise from
sightseeing tours in Grand Canyon
National Park. There, the 1987
Overflights Act required the FAA to
develop a plan within 120 days for
limiting aircraft overflights in order to
achieve substantial restoration of
natural quiet. The Overflights Act
further required that the FAA
implement the plan by regulation; and
then, within 2 years after the date of the
plan, submit to Congress a report
discussing whether the plan had met the
statutory goals or whether revisions to
the plan were needed. The FAA did
issue a final rule—the one that was
challenged—but did not do so until 10
years after enactment, and that rule
required only partial action for limiting
overflights. At the same time that it
issued the rule, the FAA proposed two
additional rules, and stated that the set
of three rules together would achieve
substantial restoration of natural quiet
in another 10 years. The Court upheld
the final rule and declined to compel
the FAA to take additional action on a
faster time frame. The Court explained:
We agree that it would be arbitrary and
capricious for an agency simply to thumb its
nose at Congress and say—without any
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explanation—that it simply does not intend
to achieve a congressional goal on any
timetable at all. * * * But the FAA has not
taken that course here. It has never defended
the Final Rule as the sole means for restoring
the natural quiet, but only as the first of three
steps. Its contemplation was that the three
rules together would achieve that goal
[within 10 additional years].
Id.
Similarly, in City of Las Vegas v.
Nevada Dev. Comm’n, 891 F.2d 927,
935 (DC Cir 1989), the Court upheld the
Department of Interior’s emergency
regulation listing as endangered species
the tortoise population in the Nevada
portion of the Mojave Desert, even
though the regulation excluded the
population in the Sonoran portion. The
Court found that ‘‘agencies have great
discretion to treat a problem partially,’’
and held that it would not strike down
agency action ‘‘if it were a first step
toward a complete solution.’’
In these cases, the agencies were
required to implement a statutory
directive through rulemaking. The D.C.
Circuit upheld partial action by the
agencies when the Court considered it
to be an initial step towards meeting the
directive. This action is set in a
somewhat different context. The
statutory provisions at issue here—the
PSD and Title V applicability thresholds
—provide that when GHG requirements
are triggered, GHG emitters must obtain
permits. When the triggering event
occurs, the agency need take no further
action before regulatory consequences
ensue; sources included within the PSD
and Title V programs must obtain
permits once these statutory provisions
are triggered. However, as we have
described, if sources are required to
apply for permits in accordance with
the literal requirements of the statute,
the permitting authorities would not
have the resources to process those
permits, and severe adverse results
would occur. This action would
ameliorate that situation by establishing
a process for compliance with the
statutory requirements. As discussed
elsewhere, this process consists of a first
phase that entails establishing the
applicability thresholds at the specified
levels, developing methodologies for
general permits and other streamlining
approaches, collecting data, preparing
an assessment, and then promulgating
rulemaking for further action. This
process would allow us to craft the
application of PSD and title V in ways
that are achievable and effectively
balance the regulatory burdens with the
reductions achievable. In this sense, this
action bears similarity to the agency
actions upheld by the D.C. Circuit as
partial steps.
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We solicit comment on whether this
line of cases is relevant for our action in
this notice.
In particular, we solicit comment on
whether an approach that includes stepdowns in the applicability thresholds,
coupled with regular examination of
whether the administrative situation is
improving, is an appropriate way to
achieve compliance while taking into
account the administrative imperatives.
If so, we ask for suggestions on how we
could structure such an approach (e.g.,
when future phases should begin, how
we should determine the appropriate
thresholds for each phase, etc.) In
addition, we solicit comment on the
level of detail with which we would be
required to identify our path towards
facilitating full administration of the
PSD and title V applicability
requirements in order for the Court to
uphold our initial steps under this case
law. We also solicit comment on
whether this proposal establishes such a
path with sufficient detail and, if not,
what further actions we should include
in the final rulemaking or commit to
undertake in subsequent rulemaking.
D. What were the ANPR comments
received on GHG tailoring options for
regulating GHG emissions under PSD
and title V?
Responses to the ANPR give us some
perspective of the initial views of some
of the permitting authorities, sources,
and the public on permit GHG tailoring
options. Many of the ANPR
commenters, including representatives
from States, environmental groups and
industry, recommended that EPA limit
permitting, at least initially, to higheremitting sources. While there were few
recommendations on specific permitting
levels, suggestions ranged from 10,000
to 100,000 tons per year CO2. A number
of environmental groups stated that if
the rationale for treating smaller sources
differently relies on principles of
administrative necessity, the cutoff
point should relate to what is
administratively feasible while
maximizing the objectives of the CAA.
Most industry stakeholders,
representing a broad profile of affected
sources, stated that title V and PSD
applicability for sources of GHG
emissions at current permitting
thresholds would be economically
disastrous and would create regulatory
gridlock. Alternatively, some
environmental groups opposed any
temporary permitting thresholds, stating
that EPA does not have legal authority
to change thresholds to limit
applicability.
Some States and environmental
groups recommended streamlining
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through the use of general permits and
presumptive BACT. This option was
supported mostly by States, but one
industry commenter also agreed that it
was an alternative worth pursuing if
EPA insisted on regulating GHG
emissions under the current CAA. Some
States noted that they have a successful
history of using general permits and
believe the use of general permits as
well as presumptive BACT could be part
of an effective and reasonable approach
to reduce regulatory costs and
administrative burdens. Other industry
groups said that presumptive BACT and
general permits are unaffordable and
require too much negotiation, and EPA
lacks authorization to use them.
States and industry commenters
acknowledged that it would take a
significant amount of time to define
presumptive BACT or general permits
for different categories, although some
States said that, over time, they have
developed similar approaches to
permitting with success for non-GHG
gases for certain source categories.
Industry commenters argued that the
case-by-case review of permit
applications that the NSR program
requires is the epicenter of NSR, and
that a one-size-fits-all approach will not
mesh with the diversity of different
manufacturing industries of all sizes.
Furthermore, even with the use of these
streamlining approaches, industry
claims that there will still be tens of
thousands of previously unregulated
sources who would need to undergo
PSD permitting. To review comments
received on the ‘‘Regulating Greenhouse
Gas Emissions Under the Clean Air Act’’
ANPR (73 FR 44354, July 30, 2008), see
Docket ID No. EPA–HQ–OAR–2008–
0318.
VII. Streamlining Options and Tools To
Address the Administrative Burdens of
PSD and Title V for GHGs
As noted in earlier sections of this
preamble, we believe that the
application of PSD and title V
requirements to sources of GHG
emissions at current statutory
thresholds would be administratively
impossible at the time that we expect
PSD and title V requirements to be
triggered for those sources, which we
expect to be the end of March 2010.
These requirements would also impose
undue burdens on the sources.
However, we recognize that there are
several streamlining techniques with the
potential to reduce over time the
burdens on sources and the
administrative burdens of the PSD and
title V requirements. We have initially
assessed the general availability and
usefulness of the streamlining
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techniques that are consistent with the
statutory requirements to address,
manage and reduce the administrative
burden on permitting authorities. In
addition, if we are compelled to
promulgate regulatory requirements that
depart from the statutory requirements,
we recognize that we must do so to the
smallest extent possible and must
remain as close as possible to
congressional intent. Other of these
streamlining techniques may depart
from the statutory requirements, but
they may be preferable to the extent that
the departure is to a smaller degree than
raising the applicability thresholds.
However, as we will discuss below,
we do not believe that we can develop
and implement any of these
streamlining techniques in the near term
in the manner necessary to make the
programs administrable at the statutory
PSD and title V permitting thresholds.
Accordingly, at this time, we cannot
rely on these techniques in lieu of
phasing in the applicability thresholds
in the manner that we propose.
However, we believe that these
streamlining techniques should be an
integral part of a strategy during the first
phase of the phase-in period—which
includes evaluating the threshold we
propose to establish—to address and
reduce the burden on permitting
authorities. Thus, during the first phase,
we plan to aggressively pursue further
development of these techniques, and
we plan to implement as many of them
for as many source categories as
possible and to do so as soon as
possible. The reassessment and
additional rulemaking that we propose
to undertake at the end of the first phase
will take into account the extent to
which these streamlining techniques, as
well as the permitting authorities’
ability to enhance their resources,
promote administrability. Moreover, for
smaller sources for which PSD and title
V requirements would not apply due to
the increase in the major source
applicability thresholds, EPA will also
assess and identify cost-effective
opportunities available in this notice to
achieve GHG reductions through means
other than PSD (e.g., energy efficiency
and other appropriate measures).
In section VII.A of this preamble, we
discuss streamlining techniques that
either have been used or could
potentially be used in the PSD and title
V programs. Some techniques may have
applications to both programs (e.g.,
general permits), while some are
applicable to only one program (e.g.,
presumptive BACT for PSD). In sections
VII.B and VII.C of this preamble, we
describe the implementation of these
techniques as they relate both to
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permitting GHG emitters under current
PSD and title V permitting thresholds
and to a broader GHG tailoring strategy
that involves the applicability
thresholds proposed with this action.
We solicit comment on the permit
streamlining approaches discussed in
section VII.A of this preamble and also
request information and comment on
any other tools or options that could
address or reduce the administrative
burden of implementing PSD and title V
for major GHG sources and reduce the
burdens on the sources.
A. Permit Streamlining Techniques for
PSD and Title V
We believe that a strategy to address
the administrative burden associated
with implementing the PSD and title V
programs for sources of GHGs could
include one or more of the following
permit streamlining techniques or
processes.
1. Redefining ‘‘Potential to Emit’’
Both PSD and title V requirements
apply to ‘‘major’’ sources, and ‘‘major’’
sources are defined as sources that emit,
on a PTE basis, 100/250 tpy for PSD
purposes and, in general, 100 tpy for
title V purposes. PTE is basically
defined as the maximum capacity of a
source to emit any air pollutant under
its physical and operational design,
including legal limitations, if any, on,
for example, emissions or hours of
operation. Many source categories have
no legal limits on their hours of
operation and, as a result, are treated as
if operating 24 hours per day, seven
days per week—which totals 8,760
hours per year—and emitting during
that entire time. As a result, basing the
applicability thresholds on PTE, rather
than on actual emissions, has the effect
of sweeping enormous numbers of
additional sources into the PSD and title
V programs. For example, sources that
do not in fact operate for part of the
year, but that have no legal limitation on
their operating hours, must calculate
their PTE on the basis of the amount of
emissions that would result if those
sources did operate, and therefore emit,
on a year-round basis.
However, sources in such situations
may take legally and practically
enforceable limits on their operational
parameters, by, for example, agreeing to
operate during only part of the year or
during only a limited number of hours
per day, or employing control devices.
These limitations would lower the
sources’ PTE and thereby allow them to
avoid classification as ‘‘major.’’ PTE
limits are already frequently used in
PSD and title V permitting programs.
There, the permitting authorities
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typically apply PTE limits as a sourcespecific limit that is crafted in a
facility’s minor source permit and
tailored to the source’s individual
circumstances.
This approach of reducing PTE to
more closely approximate a source’s
actual emissions—and, in the case of
smaller sources, thereby allowing the
PTE to fall below the ‘‘major’’ source
threshold that triggers PSD or title V
applicability—offers promise to
significantly reduce the number of
sources subject to PSD and title V, and
thereby significantly ease
administrability of those programs once
GHG emitters become subject to them.
This approach may be particularly
suitable to sources in certain categories
of GHG-emitting, combustion-related,
small sources that do not operate at
anywhere close to the 8,760 possible
hours over a given year that is generally
assumed in the PTE calculation. These
categories may include: Furnaces,
which likely only operate during the
winter season and parts of spring and
fall; water heaters, which only combust
fuel at periodic intervals necessary to
maintain water temperature; and small
stationary engines, which may operate
only for limited and defined periods of
time for certain businesses.
The permitting authorities typically
apply PTE limits as a source-specific
limit that is crafted in a facility’s minor
source permit and tailored to the
source’s individual circumstances.
However, creating PTE limits for very
large numbers of GHG-emitting sources
nationwide would require a more
efficient approach than creating them
through individual minor source
permits, as permitting authorities have
done to date. Otherwise, the sheer
volume of permits and the process
involved for each permit would
themselves create administrative
burdens that would be self-defeating.
This could particularly be the case for
the title V program, for which many
sources may seek PTE limits as soon as
the program becomes effective for GHG
emitters, and as a result, permitting
authorities would need to deal with a
large number of sources at the same
time.
In lieu of individual minor source
permitting, we intend to evaluate and to
consider adopting, or encouraging State
permitting authorities to adopt, rules for
source categories that we expect to
include large numbers of sources whose
actual GHG emissions are well below
major source thresholds but which,
absent such rules, have PTE above those
thresholds.
There are several approaches through
which EPA could take this action or
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encourage States to undertake similar
actions. For certain source categories, it
may be possible to define the source so
that its PTE more closely tracks its
actual emissions. To return to one of the
examples provided earlier, it may be
possible to define furnaces (which have
the potential to operate year-round) to
include the thermostats to which they
are attached, which constrain them from
operating in warmer weather. In this
manner, the PTE of the furnacethermostat source would take into
account the operational constraints, so
that PTE would more closely
approximate actual emissions. This type
of rule would not constitute any legal
constraint within which the source must
comply; rather, it would define the
source as including specified pieces of
equipment that, in turn, incorporate
operational constraints.
For other source categories, it is
conceivable that the only way to limit
PTE would be to promulgate regulations
that limit a source’s operation. These
regulations are often referred to as
‘‘prohibitory rules.’’ For example, the
permitting agency could promulgate a
regulation that would preclude certain
sources from operating for more than a
certain number of hours per year, while
also providing a streamlined method to
allow a source to operate for longer
hours upon request to the permitting
agency.
We have some experience with
developing and issuing guidance on
PTE calculation methodologies through
1990s guidance for States wishing to
create PTE limits through prohibitory
rules or other mechanisms for several
categories that were subject to seasonal
operational shutdowns or that did not
operate at maximum capacity for each
hour of each day, so that actual
emissions were well below their
unadjusted PTE. See the memorandum
entitled ‘‘Potential to Emit (PTE)
Guidance for Specific Source
Categories,’’ from John S. Seitz, Director,
OAQPS, OAR, EPA, to EPA Regions,
April 13, 1998, found at EPA–HQ–
OAR–2009–0517. These categories
included grain elevators, industrial
boilers, gas stations, emergency
generators, printing operations, and
cotton gins. The guidance document
provided assumptions and calculations
that States could use to develop
prohibitory rules or other mechanisms
to easily limit the PTE of sources in
these categories.
We envision a similar approach to
establish PTE calculation methods for
various categories of sources that emit
GHGs. The following steps would need
to occur for full development and
implementation of such a program:
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Step 1: EPA identifies source
categories that are generally conducive
to this approach, considering the
amount of their GHG emissions,
complexity of operations, and emissions
unit characteristics.
Step 2: EPA collects data from the
industry and individual sources on
typical operations, including emissions
unit and process parameters.
Step 3: Acting through guidance or
regulatory changes to the Federal PSD
regulations, EPA develops PTE
calculation methodologies and
implementation procedures for the
appropriate source categories.
Step 4: EPA solicits comment from
permitting authorities and affected
sources on PTE calculation
methodologies and implementation
procedures.
Step 5: EPA issues the final
regulations or guidance.
Step 6: Permitting authorities adopt
revisions that incorporate EPA’s
regulations or guidance.
Step 7: Sources comply with any
applicable legal limits.
Based on our efforts in the 1990’s, we
believe that it would take EPA
approximately 1 year to issue guidance
for a given source category. We believe
many States would be able to
immediately apply this guidance. Some
States may need to adopt the guidance
in their SIP, which EPA must then
approve, a process that could take
approximately 3 years. Finally, for those
rules that would not be selfimplementing, sources would need time
to meet the requirements of the rule. We
ask for specific comment on
stakeholders’ experience with limiting
PTE by rule rather than through
individual permits, considerations in
phasing in this approach to GHG
sources, and identification of categories
that might benefit from the use of rules
limiting PTE.
2. Presumptive BACT
CAA section 165(a)(4) requires that
sources subject to PSD implement BACT
for each pollutant subject to regulation
under the Act, and CAA section 169(3)
requires that BACT emissions limits be
determined ‘‘on a case-by-case basis’’
that reflects the use of state-of-the-art
demonstrated control technology at the
time of the permit action. Thus, BACT
is required to be source-specific,
changes over time, and requires
continual updating. The permitting
authority’s decision as to what control
requirements constitute BACT affords
flexibility to consider a range of casespecific factors, such as available
control options and collateral cost,
energy, and environmental impacts.
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However, full consideration of those
factors requires significant data and
analysis in order for permitting
authorities to arrive at a case-by-case
permitting decision that is appropriate
for each individual source when it
constructs or modifies. For all these
reasons, determining BACT for a
particular source can often be a
complicated, resource-intensive, timeconsuming, and sometimes contentious
process. If the number of required PSD
permitting decisions increases
significantly, these challenges will be
magnified, and BACT determinations
will be a major factor contributing to
uncertainty and delay for sources
seeking PSD permits. Furthermore, the
increase in workload of BACT
determinations will require large
investments of resources by permitting
authorities, sources, EPA, and the
public interested in commenting on
these decisions.
In order to streamline the BACT
process for the many new small sources
that will be brought into the PSD
program based on their GHG emissions,
EPA will investigate ways to move from
a system under which permitting
authorities set BACT limits on an
individual, case-by-case basis to a
system under which they make BACT
determinations for common types of
equipment and sources, and apply those
determinations to individual permits
with little to no additional revision or
analysis. The EPA has previously
introduced this concept, known as
‘‘presumptive BACT’’, to streamline
permitting for desulfurization projects at
refineries as well as in other instances,23
and some State permitting authorities
have adopted similar approaches.24
Based on our understanding of the types
of sources that will become subject to
PSD if GHG emissions are regulated at
the statutory 100/250-tpy threshold, we
believe the presumptive BACT process
could offer significant streamlining
benefits. These benefits arise because
many of the sources that would become
subject to BACT will likely have very
similar emissions producing equipment,
and there will be little variation across
23 See Memorandum, ‘‘BACT and LAER for
Emissions of Nitrogen Oxides and Volatile Organic
Compounds at Tier 2/Gasoline Sulfur Refinery
Projects,’’ from John S. Seitz, Director, Office of Air
Quality Planning and Standards, to Regional Air
Division Directors (January 19, 2001).
24 For example, Wyoming has a minor source
permitting program that includes a BACT analysis,
and they use a presumptive BACT process for
issuing minor source permits to a particular source
category—oil and gas production facilities. See
Permitting Guidance for Oil and Gas Production
Facilities, Wyoming Dept. of Environmental
Quality, Air Quality Division (August 2007
revision).
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sources with respect to the cost, energy,
and environmental considerations in the
BACT decision.
The central component of a
presumptive BACT approach would be
the recurring technical determination,
subject to notice and comment, of the
presumptive BACT levels for various
categories. Because of the limited data
currently available about the number
and types of sources that would become
subject to the BACT requirement for
GHGs, we cannot at this time predict
how many or which categories might
benefit from such an approach. We
recognize that considerable work will be
needed to determine what options exist
for controlling GHG emissions from
these categories of sources and the
various types of emitting equipment
they use.
As noted above, the CAA requirement
for BACT, found in sections 165(a)(4)
and 169(3), mandate that BACT
determinations be made for each
pollutant on a ‘‘case-by-case basis.’’
Accordingly, we need to explore
whether we can develop a process that
benefits from the efficiencies that
presumptive BACT would provide
while also allowing for
individualization of permits. A possible
approach would be to develop, through
notice-and-comment rulemaking, a
presumptive BACT level for sources in
a particular source category, but require
that permitting authorities allow public
comment on individual permits as to
whether there are significant casespecific energy, economic, and/or
environmental impacts that would
require adjustment of the presumed
limit for that particular source. This
phase in approach could streamline the
BACT determination process to some
extent, although the prospect that
presumptive BACT determinations
would, as a result of public comment,
still have to be reviewed for numerous
individual sources could well negate
those streamlining benefits.
Accordingly, we believe that we also
need to investigate a system under
which presumptive BACT levels for a
source category are developed through
notice-and-comment rulemaking but
applied to individual sources in that
category without requiring permitting
authorities to individualize the BACT
determination or to allow for public
comment on how presumptive BACT
levels would apply to an individual
source. The D.C. Circuit, in the Alabama
Power case discussed above, stated that
courts ‘‘frequently uphold streamlined
agency [regulatory] approaches or
procedures where the conventional
course, typically case-by-case
determinations, would, as a practical
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matter, prevent the agency from carrying
out the mission assigned to it by
Congress.’’ 636 F.2d at 358. The Court
recognized that such streamlining
measures may be needed when time or
personnel constraints or other practical
considerations ‘‘would make it
impossible for the agency to carry out its
mandate.’’ See id. at 359. Given the
significant increase in new sources that
would likely be brought into the PSD
program once GHGs are regulated,
maintaining individual case-by-case
BACT determinations may well be
impractical and may well warrant a
presumptive BACT approach that does
not authorize individualized, sourcespecific determinations. This approach
could well be an important tool to allow
EPA, State and local permitting
authorities to carry out the PSD program
in as timely and efficient manner as
necessary to promote (rather than
hinder) control of GHG emissions from
the many new, small source categories
that would be required to have PSD
permits based on their GHG emissions.
This approach would preserve
opportunities for public participation by
taking comment during the
determination of presumptive BACT
levels for a source category. Although
this type of presumptive BACT
approach—one that does not permit
individualized, source-specific
determinations—would depart from a
literal application of the statutory
requirements for BACT, it may
nevertheless remain closer to the
congressional intent for the PSD
program than maintaining the
applicability threshold at a level higher
than the statutory level. If this is the
case, then EPA could be required to
establish a presumptive BACT approach
and lower the applicability thresholds
from the first phase level proposed in
this action.
Several other factors should be taken
into account when considering a change
from case-by-case BACT determinations
to a presumptive BACT process for
some specific source categories within
the PSD program. As a general matter,
we will need to consider how such
presumptive BACT limits should be
established and used, and what
provisions in the CAA would set
requirements or limits on their
establishment and use. In particular,
EPA recognizes the CAA section 169(3)
requirement to set BACT limits after
taking into account site-specific energy,
economic, and environmental impacts
(otherwise known as collateral impacts).
In addition, while case-by-case BACT
determinations allow for the continual
evolution of BACT requirements over
time (as controls applied in prior
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permits are considered in each
subsequent case-by-case BACT
determination), EPA recognizes that
application of presumptive BACT to a
category of sources over many
permitting decisions may diminish the
technology forcing effects of PSD. EPA
is interested in options that would help
maintain advances in control
technologies, such as a requirement to
update and/or strengthen BACT at set
intervals (such as after 3 years).
EPA seeks comment on all aspects of
the use of presumptive BACT limits
within the PSD program, including
EPA’s authority to do so, whether there
is need for and value to such an
approach, and suggestions for how such
limits could be established, updated,
and used consistently within the
requirements of the CAA, or by
departing as little as possible from those
requirements. We also ask for comment
on whether there are issues at
traditional PSD major sources that arise
for GHGs and that would not be
addressed by a presumptive BACT
approach. If so, we ask for comment on
additional options for streamlining the
BACT requirement to address these
issues.
3. General Permits and Permits-by-Rule
A general permit is a permit that the
permitting authority drafts one time,
and then applies essentially identically
(except for some source-specific
identifying information) to each source
of the appropriate type that requests
coverage under the general permit.
Congress expressly codified the concept
of general permits when it enacted the
title V program and States have been
using general permits and similar
processes for years in their own permit
programs, particularly for minor source
NSR and operating permits. Due to the
case-by-case nature of PSD for
‘‘traditional’’ major sources and the
differences among individual PSD
sources, there has not been much
interest or activity in general permitting
for the PSD program. However, we
believe this approach merits strong
consideration for both PSD and title V
programs due to the large number and
similar characteristics of many of the
sources that EPA expects will become
newly subject to these permitting
programs because of their GHG
emissions.
A general permit provides a
streamlined application and permitting
process for sources that are similar in
terms of operations, emissions units,
and applicable requirements. By issuing
a general permit, a permitting authority
indicates that it approves the activities
authorized by the general permit,
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provided that the owner or operator of
the source registers with the permitting
authority and meets the requirements of
the general permit.
Permit-by-rule provisions may be very
similar to general permit provisions, but
they typically authorize a source owner
to operate in accordance with certain
requirements provided that the source
owner registers with the permitting
authority or certifies that they are
complying with all applicable
requirements. Thus, a source subject to
the permit-by-rule would not need to
wait for permitting authority approval,
as is the case with the general permit,
prior to operating under a permit-byrule.
General permits are attractive in their
ability to dramatically reduce permitting
timeframes for affected source types. At
the same time, general permits are
highly conducive to automation and the
development of web-based applications.
For example, New Jersey’s Department
of Environmental Quality has fully
automated its air general permitting
process, allowing source owners to go
online, apply for a general permit, build
the permit themselves, issue it to
themselves by printing it out, and pay
for it by credit card. This type of onestop processing has the potential to
dramatically streamline the air
permitting process for source types
covered by general permits, and the
resulting electronic records create
spillover benefits for compliance
tracking, inspection management, and
pollution prevention outreach.
a. General Permits for the PSD Program
EPA has limited experience in
developing general permits and permitsby-rule under the PSD program due to
the predominance of the case-by-case
BACT decision process described in
section VII.A.2 of this preamble. In
considering the use of general permits
within the PSD program, EPA is
considering how such general permits
should be established and used, and
what provisions in the CAA might limit
their establishment and use. One option
is to model PSD general permits on the
general permits used in title V, as
provided in 40 CFR 70.6(d). However,
an important consideration in
establishing PSD general permits is the
requirement in CAA § 165(a)(2) that
permits be issued after ‘‘a public hearing
has been held with opportunity for
interested persons including
representatives of the Administrator to
appear and submit written or oral
presentations.’’ One option for
addressing this public participation
requirement at least to some extent is
the approach followed for title V general
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permits in 40 CFR 70.6(d), which
provides that permitting authorities may
establish general permits after following
notice-and-comment procedures
required under 40 CFR 70.7(h) and then
grant a source’s request to operate under
a general permit without repeating the
public participation procedures. Other
considerations for establishing general
permits under the PSD program include
the requirement to determine BACT on
a case-by-case basis (as discussed in an
earlier section of this preamble), and the
other procedural requirements referred
to in section VII.A.3 of this preamble
concerning the Class I consultation and
the analysis of air quality and other
potential impacts under CAA section
165(e).
Because permitting authorities have
had minimal experience in developing
general permits and permits-by-rule for
PSD, sufficient time would be needed to
develop them as useful tools to reduce
the administrative burden associated
with the application of the PSD program
to major GHG sources. Sufficient time
would be needed for the following
steps: (1) EPA must determine best
candidate sources for general permits
and permits-by-rule; (2) EPA must
determine similar types of processes
and source types and sizes to combine;
(3) EPA must prioritize the development
and use of general permits and permitsby-rule; (4) EPA must issue guidance or
rulemaking (as needed) for each
grouping of similar sources; (5) States
must adopt the guidance or rulemaking
in their SIPs, as needed; and (6) sources
must implement the requirements. We
estimate that EPA would require more
than 3 years to develop and deploy
general permits and permits-by-rule
would require more than 3 years to
develop and deploy for a candidate
group of sources, and that additional
time would be needed for the States and
sources to take the indicated steps.
EPA seeks comment on the use of
general permits within the PSD
program, including both EPA’s authority
to do so and suggestions for how general
permits would be established and used
consistent with the requirements of the
CAA and identification of source
categories that could benefit from such
an approach.
b. General Permits for the Title V
Program
In contrast to the PSD program, in the
title V program, general permits are
specifically authorized under CAA
section 504(d), which provides:
The permitting authority may, after
notice and opportunity for public
hearing, issue a general permit covering
numerous similar sources. Any general
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permit shall comply with all
requirements applicable for permits
under this subchapter. No source
covered by a general permit shall
thereby be relieved from the obligation
to file an application under section 503
of this Act.
EPA regulations describe general
permits in 40 CFR § 70.6(d). These
provisions specifically authorize the use
of general permits covering numerous
similar sources under the title V
program. The general permit must also
follow the public participation
requirements of 40 CFR 70.7(h). The
information development and review
conducted as part of streamlining for an
individual source can be used by the
permitting authority to generate a
general permit for similar sources or
portions of sources. If a general permit
were used, EPA and public review
beyond that needed to issue the general
permit would not be necessary when
sources subsequently applied for the
streamlined permit conditions
established under the general permit.
Even where a general permit is not
issued, the availability of information
obtained from the streamlining of one
source may be useful as a model for
future streamlining actions involving
other similar sources. EPA notes that the
part 71 regulations addressing title V
permits issued by EPA (and delegated
authorities) contain parallel provisions
regarding general permits. See 40 CFR
71.6(d).
We believe general permits may have
more near-term applications for the title
V program than for the PSD program
because of past experience of permitting
authorities, however limited, in using
this permit streamlining technique for
title V. Certain States have already used
general permits for a relatively narrow
population of certain minor, mainly
area-type sources with a simple set of
applicable requirements that were
relatively easy for both permitting
authorities and sources to implement.
These general permits allowed the
sources a more focused ‘‘roadmap’’ to
meeting their regulatory requirements
with far less burden associated with
applying for the permits and
administering them in general. In
response to the ANPR, some State
commenters noted that they have a
successful history of using general
permits and believe the use of general
permits could be an effective and
reasonable approach to reduce
regulatory costs and administrative
burdens.
We agree that there are similarities
between the way general permits have
been used in the past, particularly under
title V, and the challenges permitting
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authorities would face for permitting
GHG emissions for sources that would
not already have, or necessarily need, a
more comprehensive title V permit.
However, most permitting authorities
lack experience with general permits
and with GHG sources in general. As a
result, we believe that the process of
developing general permits for title V
purposes would parallel in certain
respects the process of developing them
for PSD purposes. Specifically, title V
permitting authorities would need
sufficient time to (1) determine
candidate sources for general permits,
(2) determine similar permit elements
for those sources and develop adequate
templates and formats for the general
permits for those sources, (3) conduct
formal EPA and public review of the
general permit, and (4) develop an
adequate implementation plan for
sources to apply for such permits and
for permit review staff to process such
permits. After this, sources would need
additional time to comply with the
general permits. We believe this process
would take at least 2 to 3 years for a
partial set of general permits to be fully
developed and ready for deployment.
4. Electronic Permitting
Implementation of electronic
permitting (e-permitting) systems is
growing across the U.S., as more and
more States implement new or upgraded
systems. We believe these systems,
possibly in conjunction with general
permitting procedures, could assist in
addressing some of the administrative
burden created by adding GHG
emissions sources to the PSD and title
V programs.
Most States are currently using agency
Web sites to deliver a range of air
permitting program services, from
enabling electronic submittal of permit
applications to providing the public
web access to permits and related
documents. Permitting authorities find
value in e-permitting systems because
these systems can lead to improved
customer service, decreased data entry
errors, shortened permit review
timeframes, and improved systems for
managing permitting processes. In short,
e-permitting systems can make better
permits more quickly. Common State epermitting activities include:
• Development of air permit
application forms which can be
accessed, completed, and submitted
online;
• Development of specialized
software or database applications to
review submitted permit applications
and to support the permit development
process; and
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• Posting issued permits and draft
permit documents to air permitting Web
sites.
New technology is expanding the
opportunity for collaboration and joint
development around information
system tools. To enable permitting
authorities to handle the administrative
workload associated with the
application of the PSD and title V
programs to GHG sources, EPA could
assess and identify best practices for epermitting system implementation and
support States in implementing effective
and efficient systems using targeted epermitting tools and resources. For
example, EPA could work with States to
develop effective GHG permitting
strategies in the following areas:
• Permit application submittal which
would involve processes for facilities to
identify permits needed, determine the
scope of information to include in
permit applications, access and
complete application forms, and submit
those forms and supporting data to State
and local permitting authorities.
• Application review and draft permit
generation which would involve
processes for State and local permitting
authorities to conduct administrative
and technical permit application
reviews, develop permit conditions, and
sometimes create draft permit
documents. This category could also
include a broad range of information
technology tools and resources that
could support permit writers in
preparing better permits more quickly.
• Draft permit review and final
permit issuance which would involve
processes for State and local permitting
authorities to manage completion of
external reviews (including public and
EPA review periods) and any related
updates to the draft permit document,
issuance of the final permit, and
collection of permit fees.
• Post-issuance activities which
would incorporate all activities related
to permits that are managed by State
and local permitting authorities after
permits are issued (including public
access to permits and related
documents, permit appeals, permit
modifications, permit renewals, and
inspections and compliance
monitoring).
• Workflow tracking and management
which would incorporate all of the
management procedures and tools that
State and local permitting authorities
use to track the permit development
process, including internal permit
authority timeline tracking and public
access to workflow information.
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5. ‘‘Lean’’ Techniques for Permit Process
Improvement
In the business world, ‘‘lean’’
techniques refers to a collection of
process improvement principles,
methods, and tools designed to help
organizations identify and eliminate
non-value-added activity (‘‘waste’’), in
order to meet customer needs better,
more quickly, and more efficiently. Lean
techniques have been adopted across
numerous business sectors and been
adapted to address both production and
administrative processes. Lean process
improvements could help permitting
authorities to address administrative
burdens that are created if numerous
GHG sources are added to their air
permitting programs.
In the context of air permitting, Lean
improvement events typically focus on
eliminating the following types of
administrative process waste: Backlogs
in permitting; errors in documents;
unnecessary rework on documents; and
delays associated with transmission of
documents between the various parties
that develop and approve them. Since
2003, State environmental agencies have
increasingly used Lean manufacturing
principles and methods to drive rapid,
continuous improvement in air
permitting and other agency processes.
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B. Implementation of Streamlining
Techniques and Overall Approach To
Administering PSD and Title V
Programs
As noted above, these potential
streamlining options and tools will
require time to develop, issue, and reach
full deployment. Each technique would
generally take from 3 to 4 years to fully
develop and implement. Therefore, if
we did not phase in the applicability
thresholds for sources of GHG emissions
as soon as PSD and title V requirements
are triggered for them, there would be a
significant time period when numerous
GHG sources exceeding the statutory
permitting thresholds for PSD and title
V would need to obtain permits, and
permitting agencies would be faced with
overwhelming administrative burdens.
Also, at this point in time we do not
have enough information to predict the
full potential applications and impact of
these streamlining techniques for
permitting GHG sources. Therefore, it is
impossible to predict a specific time in
the future when and if such
streamlining techniques would reduce
the administrative burden of permitting
authorities sufficiently for them to
administer PSD and title V programs for
GHGs at the current permitting
thresholds. Instead, we propose to
commit to investigating and developing
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these techniques as vigorously and as
soon as possible as part of an overall
GHG tailoring strategy that involves
phasing in the GHG major source
permitting thresholds as soon as PSD
and title V requirements are triggered
for GHG emitters, but that further
involves reassessing the situation,
completing a study within 5 years, and
then taking up to 1 additional year to
finalize regulations adopting the lowest
threshold that we conclude is
administrable based on the study.
Even so, we have enough information
now about some streamlining
techniques, such as presumptive BACT
in support of PSD permitting and
general permits in support of title V
permitting, to recognize that those
techniques are quite likely to be
beneficial to both permitting agencies
and affected sources. We believe that
within the framework we propose in
this action there will be sufficient time
to deploy the streamlining techniques
and to evaluate their effectiveness in
addressing administrative burden.
Therefore, in conjunction with our
proposed action to tailor the GHG
permitting thresholds, we are
committing to a concurrent effort to
investigate, evaluate, and support the
implementation of permit streamlining
techniques to address GHG sources. We
believe that while the proposed
temporary thresholds will allow the
permitting authorities to implement
their programs for PSD and title V, it is
also necessary for us to pursue
applicable streamlining techniques that
may help our assessment of the
temporary thresholds as part of the
threshold evaluation study. We believe
that at the end of the threshold
evaluation period we will have a better
understanding and a sufficient record of
the effectiveness of different permit
streamlining techniques and how these
techniques may influence the need to
consider alternative thresholds.
We request comment on which types
of streamlining techniques, and for what
source categories, would be of most
value to permitting authorities and
affected sources. We also request
comment on the anticipated impact
such techniques would have on
permitting authorities’ administrative
capabilities to address GHG permitting
and how such impact would affect the
need for the temporary thresholds
proposed under this action. We also
request comment on the time periods
needed to develop and implement any
such streamlining techniques and on
how such time frames can expeditiously
meet CAA requirements in light of the
administrative burden that would
remain.
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C. Strategies for Obtaining GHG
Reductions From Sources Under the
Proposed GHG Permit Thresholds
In addition to pursuing permit
streamlining techniques that may
ultimately have application to smaller
GHG source categories (e.g., those in the
commercial and residential sectors), we
also recognize that there are both
current and future EPA programs that
could be used to mitigate GHG
emissions from these smaller sources. It
may well be the case that, for the
smaller sources, these approaches,
which are summarized in this section,
will result in more efficient and costeffective regulation than would case-bycase permitting. We therefore intend to
fully explore the use of all available
tools for addressing these sources at the
same time as we explore streamlining
the permitting programs.
While EPA is proposing that during
the first phase, GHG sources less than
25,000 tpy CO2e will not be subject to
PSD and title V requirements for
purposes of applicability, there are
feasible, cost-effective opportunities for
reductions from these sources through
means other than PSD and title V during
the first phase. The tailoring proposal
does not restrict our ability to explore
these opportunities during this first
phase. EPA has strong interest in
pursuing such opportunities and
therefore requests your comments on
the practicability of near-term regulatory
and nonregulatory programs to address
smaller sources.
The near-term opportunities for GHG
emissions reductions in smaller-scale
stationary sources include increased
energy efficiency, process efficiency
improvements, recovery and beneficial
use of process gases, and certain raw
material and product changes that could
reduce inputs of carbon or other GHGgenerating materials. The use of
alternative fuels and energy are also
promising methods for achieving GHG
reductions.
One key challenge in addressing
sources emitting less than 25,000 tpy
CO2e is their diversity. The source types
may range from landfills to small
stationary fuel combustion devices to
waste water treatment plants and
electronics manufacturing. In addition
to including a range of processes, these
source categories may include large
(>25,000 tpy CO2e) and small sources.
EPA is soliciting public comment on a
fair and systematic way to address the
diverse number of categories where
individual sources are comparatively
small, but the source category could be
addressed through some cost effective
means.
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Controls on sources at this scale
would likely involve decisions on how
proposed installations of equipment and
processes for a specific source category
can be redesigned to make those sources
more energy efficient, for example,
while taking cost considerations into
account. However, these types of
approaches have yet to be adopted
widely, because of market barriers,
insufficient financial and legal
incentives, or other barriers. Below, EPA
provides some examples of approaches
that could be taken and existing
programs that could provide useful
platforms to address smaller sources.
We request comment on the types of
strategies that may be appropriate for
these sources, considerations—such as
cost and feasibility—with respect to
implementing programs for smaller
sources, approaches to incentivize these
types of programs, and ways to measure
the effectiveness of such initiatives. We
also request comment on whether these
initiatives have the potential to be
developed in such a way as to meet the
essential PSD and title V program
requirements for sources, even if the
initiatives do not necessarily meet the
letter of those requirements (such as the
case-by-case determinations required
under the PSD program), based on
administrative imperatives.
For instance, EPA could design a
hybrid approach where sources on the
larger end of the below-25,000-tpy CO2e
range could be required to analyze
pathways to reduce GHG emissions by
a certain percentage, but EPA or the
States could use flexible criteria in
requiring reductions from those sources,
including the timeframe for achieving
such reductions. These requirements
could be supplemented by an incentive
program, through which a State could
use loan, grant, or emissions credit
incentives to help such sources lower
their GHG emissions profile, especially
when the source is performing a
modification. Any approach would have
to be systematic, in that the criteria used
would have to be responsive to the
source volume of emissions, the
reductions that might be achieved, costeffectiveness, permanence and
enforceability.
A further alternative would be the use
of section 111(d) of the CAA to work
with smaller sources to reduce
emissions. In contrast to other
provisions in the Act which require
regulation of all sources above specific
size thresholds, section 111 gives EPA
significant discretion to identify the
facilities within a source category that
should be regulated. To define the
affected facilities, EPA can use size
thresholds for regulation and create
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subcategories based on source type,
class or size. Emissions limits also may
be established either for equipment
within a facility or for an entire facility.
EPA also has significant discretion to
determine the appropriate level for the
standards.
In addition to exploring regulatory
options, EPA will continue to consider
existing nonregulatory programs to
achieve cost-effective emissions
reductions. Some of the EPA’s current
programs, discussed below, are
aggressively working to cost-effectively
mitigate GHG emissions through energy
efficiency in industry and consumer
products and other voluntary programs
that address several key CH4 and other
high-GWP sources. The source
categories discussed below are not
exhaustive, and are discussed as
illustrative examples. It is also
important to note that particular sources
in these categories could fall above or
below a threshold value of 25,000 tpy
CO2e.
Energy efficiency is one of the lowest
cost means for addressing climate
change. Since 1992, EPA, through the
ENERGY STAR program, has achieved
GHG reductions by helping U.S.
businesses adopt cost-effective, energyefficient technologies and practices. The
program combines several elements,
including: ENERGY STAR branding of
commercial products with superior
energy performance and promoting
strategic energy management practices
across the commercial and industrial
sectors. We also work with States to
leverage wider use of such ENERGY
STAR products as commercial roofing
materials, furnaces, and boilers in
commercial settings. States can promote
the purchasing of ENERGY STAR
qualified products in residential multifamily housing and commercial
buildings such as offices, hospitals,
hotels, schools, and warehouses. These
building types comprise the vast
majority of sources that would have
emissions below the proposed 25,000tpy CO2e major source threshold.
Also for these building types, States
can take advantage of EPA tools to
encourage, track and reward
improvements in building efficiency.
Already, States are leveraging such tools
as Portfolio Manager to make disclosure
of building efficiency part of sale/lease
transactions. Many States also use
ENERGY STAR to incentivize adoption
of energy-efficient equipment and
buildings through regulated utilities and
other energy efficiency program
sponsors. Finally, EPA provides
resources to help—or to enable States to
help—manufacturers improve energy
efficiency through a transferable
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platform that States can adopt which
includes sector-targeted energy
efficiency guidance, energy program
development tools, and a national rating
system that scores the energy
performance of plants and enables
documentation of energy improvement
for those interested in demonstrating
change in performance. For additional
information on these programs, visit
https://www.energystar.gov.
Methane and other high-GWP gases,
including PFCs, HFCs, and SF6, are
potent GHGs that contribute to climate
change. In an effort to reduce emissions
of these gases, EPA is working
cooperatively with a variety of
companies and organizations in the
energy, waste management, agriculture,
and industrial sectors to implement
voluntary programs that encourage costeffective emissions reductions. These
programs offer a range of technical and
policy information products and
exchanges and track emissions
reductions in the following key sectors:
landfills, oil and gas systems, animal
waste, coal mines, industrial processes
including aluminum production,
semiconductor manufacturing, electric
power transmission, magnesium
production and processing, and the
production of HCFC–22, and wastewater
from domestic or industrial sources.
Experience and lessons learned through
these programs can be used by States
and EPA for regulatory and
nonregulatory initiatives. For additional
information on the CH4 and high-GWP
programs, visit https://www.epa.gov/
methane/voluntary.html and https://
www.epa.gov/highgwp/voluntary.html.
For more information on opportunities
for GHG reductions at wastewater
treatment facilities, visit https://
www.epa.gov/chp/documents/
wwtf_opportunities.pdf.
VIII. Description and Rationale of
Proposed Action
A. Proposed Permitting Thresholds for
GHGs
Based on the legal rationale of
‘‘absurd results’’ and ‘‘administrative
necessity’’ described in section VI of
this preamble, EPA is proposing with
this action to establish the first phase of
the thresholds for determining
applicability under both the PSD and
title V permitting programs and to set a
significance level for GHGs under the
PSD program. For both PSD and title V
purposes, we are proposing to set the
applicability threshold at 25,000 tpy
CO2e. In addition, for the PSD
significance level, we are proposing a
range from 10,000 to 25,000 tpy CO2e.
Upon finalization of this rule, and based
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on comments received and the
supporting record, we will establish a
singular value for the GHG significance
level.
EPA is also proposing in this action
to commit to evaluating the impact,
effectiveness, and need for these GHG
permitting thresholds as well as other
aspects of the administrative burden for
permitting authorities in a study to be
completed within 5 years from the
promulgation date of the final version of
this rulemaking. Based on the results of
that study, EPA would propose and
promulgate a rulemaking within a year
later that would establish the second
phase of the tailoring program. This
rulemaking would reaffirm the firstphase GHG permitting thresholds or
revise those thresholds, promulgate
other streamlining techniques, and/or
take action consistent with the goal of
expeditiously meeting CAA
requirements in light of the
administrative burden that remains at
that time.
This section of the preamble defines
the GHG metric used for purposes of
determining whether the proposed
thresholds are exceeded, describes the
policy and technical rationale for
selecting the proposed applicability
thresholds for PSD and title V, and
discusses the proposed 5-year threshold
evaluation study.
While the rest of this section
discusses the details of our proposed
approach, we note at the outset that
there may be other ways to structure the
first phase of permit program
applicability for GHGs than the one we
describe as our preferred approach. For
example, we could address the
administrative burden by defining the
sources in the first phase subject to
permitting for GHGs to include only
sources that are or become subject to
title V or PSD permitting obligations
under the existing 100/250 tpy statutory
thresholds on the basis of their
emissions of a non-GHG pollutant.
Under this approach, for example, a
new source that triggered PSD for a nonGHG regulated NSR pollutant and that
also emits GHGs, or an existing source
going through a modification that
triggered PSD for a non-GHG regulated
NSR pollutant and which also increased
its GHG emissions would have to do a
BACT analysis for GHGs. This BACT
process would be expected to identify
control options which are technically
feasible and cost effective for a
particular source based on the tons
emitted, thereby ensuring that the first
phase of permitting would apply to the
largest sources of GHG that are currently
subject to CAA regulation based on
emissions of non-GHG pollutants.
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Sources that do not trigger PSD or title
V for a non-GHG pollutant would not be
subject to these programs solely on the
basis of their GHG emissions. Under
such an approach, we may still need to
establish a significance level for GHG
emissions at sources that are subject to
PSD due to their non-GHG emissions,
but we could consider setting this based
on the 10,000 ton CO2 eq significance
level proposed elsewhere in this
package. We solicit comment on this
approach, and on other potential
variations on our proposal that
commenters believe could address the
administrative concerns in more
effective ways.
B. What is the definition of the GHG
pollutant for the proposed permitting
thresholds?
1. Background on GHG Metrics
The selection of a GHG metric is an
important consideration in developing
the GHG permitting threshold options
because it sets the basis for evaluating
whether a particular source exceeds a
given threshold. As noted in section
IV.A of this preamble, one commonly
utilized metric is to estimate and report
emissions of GHGs as the collective sum
of emissions of the six primary GHGs,
with applicable GWPs applied to the
non-CO2 gases. When GWPs are applied
to the mass emissions of one of the
primary GHGs, the resulting weight is
referred to as CO2e (see section IV.A of
this preamble for a description of CO2e).
Another possible metric would consist
of individual mass-based emissions for
each GHG, without their GWP values
applied. The choice of the GHG metric
can have a significant impact on design
and implementation of the GHG
permitting threshold.
For example, if a source only
evaluated its CO2 emissions against a
permitting threshold, it may fall below
the threshold, but if it evaluated the
sum of all its primary GHG emissions on
a CO2e basis, it may fall above the
threshold. Although there may be a
variety of considerations for including
one GHG metric over another, the
choice of a GHG metric, whether it be
the sum of the CO2e emissions or
individual GHGs, for both PSD and title
V programs, must include any of the
individual GHGs that may be subject to
regulatory action under the CAA, as
discussed in section IV.D of this
preamble.
One of the reasons EPA is undertaking
this rulemaking is because it intends to
propose and finalize a separate rule that
regulates GHG emissions from lightduty motor vehicles and that would
trigger PSD and title V permitting
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requirements for stationary GHG
emissions sources. The light-duty motor
vehicle rule will identify a GHG
pollutant or pollutants subject to
regulation. However, at the time of this
proposal there is uncertainty as to
exactly what GHG metric will ultimately
be finalized in the light-duty motor
vehicle rule. Also, as discussed in the
ANPR, there may be other future
regulatory actions or decisions by EPA
that would determine what form of
GHGs would be subject to regulation
under the CAA, such as new source
performance standards for certain
source categories under CAA section
111. This uncertainty over the form of
the GHG metric in future regulatory
actions is an important factor in our
selection of the GHG metric for the
permitting threshold.
In order to better inform our
consideration of different GHG metrics
for the proposed GHG permitting
thresholds, we also reviewed the GHG
metrics used in two recent EPA
proposals: the endangerment finding
and the GHG mandatory reporting rule.
In the proposed endangerment finding
for GHGs, the Administrator proposed
to define the air pollutant as the
‘‘[c]ollective class of the six greenhouse
gases,’’ and referred to the widespread
use of CO2e as a means to evaluate the
six primary GHGs as a group (74 FR
18886, April 24, 2009). The
Administrator also identified this
collective approach to defining GHGs,
for the contribution test, as most
consistent with the treatment of GHGs
by those studying climate change
science and policy, where it has become
common practice to evaluate GHGs on
collective CO2e basis. However, the
Administrator also recognized in the
proposed finding that each GHG could
be considered a separate air pollutant
and that defining the air pollutant as the
group of six GHGs does not preclude
setting standards that control emissions
of individual GHGs, as constituents of
the group.
Under EPA’s GHG Mandatory
Reporting Rule proposal, the emissionsbased applicability thresholds for
reporting are based on total CO2e
calculated from the sum of a facility’s
emissions of the six primary GHGs plus
other fluorinated GHGs, applying GWP
values to non-CO2 gases (74 FR 16448,
April 10, 2009). However, annual
reporting is required for both total CO2e
and individual GHGs on a mass basis,
with no GWPs applied for non-CO2
gases.
We also note that both domestic
regional cap-and-trade programs (e.g.,
the Regional Greenhouse Gas Initiative)
and international trading programs (e.g.,
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the European Union Emission Trading
Scheme) make use of the CO2e metric
for purposes of offsets accounting and
emissions trading that involves different
GHGs. Under the United Nations
Framework Convention on Climate
Change (UNFCCC), the U.S. and other
countries also report their annual
emissions of the six GHGs in terms of
CO2e units.
2. Rationale for GHG Metric Selection
for Proposed Permitting Thresholds
As discussed elsewhere, EPA
interprets the PSD and title V
requirements to apply to each ‘‘air
pollutant’’ that is ‘‘subject to regulation’’
under other provisions of the CAA. It is
important to determine which GHGs to
treat as the ‘‘air pollutant’’ that is
subject to PSD and title V requirements
and how to measure those GHGs. Taken
together, this is termed the GHG metric.
As noted above, in the proposed
endangerment and cause or contribute
findings under section 202(a) of the
CAA, EPA proposed to define the ‘‘air
pollutant’’ for the contribution analysis
as the class of six GHGs CO2, CH4, N2O,
SF6, HFCs, and PFCs); but EPA also took
comment on the concept of defining
each GHG as a separate air pollutant. In
connection with the light-duty vehicle
rule under CAA § 202(a) that EPA is
proposing at the same time as this
action, four of those six GHGs which are
emitted by light-duty motor vehicles are
proposed to be subject to controls under
the light-duty vehicle rule (all but SF6
and PFCs). As EPA explains in the lightduty vehicle rule and below, EPA has
discretion under section 202(a) to
establish controls at the GHG-specific
level regardless of whether the final
definition of ‘‘air pollutant’’ for the
contribution analysis is the class of six
GHGs or each GHG individually. In light
of the ongoing relevant rulemakings,
this proposal discusses several possible
ways for identifying the GHG metric for
PSD and title V requirements. First, the
metric could address each GHG
individually, or it could address them as
a single GHG group. Second, the metric
could include (whether individually or
as a group) all six of the GHGs, or only
those four GHGs subject to controls in
the light-duty vehicle rule. Third, the
metric could measure the GHGs
(whether individually or as a group) on
the basis of their actual tonnage or their
equivalent tonnage based on global
warming potential (GWP), which we
refer to as CO2 equivalent, or CO2e.
We propose to identify the GHG
metric as the group of six GHGs, on a
CO2e-basis. Using a CO2e basis, a
source’s emissions for any of the six
primary GHGs that are ‘‘subject to
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regulation’’ under the Act, and therefore
considered ‘‘regulated NSR pollutants,’’
are summed on a CO2e basis using their
GWP values. The summed CO2e
emissions would then be compared to
the applicable permitting threshold to
determine whether the source is subject
to PSD and title V requirements. We
solicit comment on whether we should
identify the GHG metric in a different
way, such as one of the options
identified above.
a. Legal Rationale
Because PSD and title V apply to each
‘‘air pollutant’’ subject to regulation, it
is necessary both to examine the
definition of ‘‘air pollutant’’ and to
determine which air pollutant or
pollutants are proposed to be subject to
regulation under CAA § 202(a).
PSD applies to a ‘‘major emitting
facility,’’ under CAA § 165(a), and that
term is defined under CAA § 169(1) as—
any of the following stationary sources of air
pollutants which emit, or have the potential
to emit, one hundred tons per year or more
of any air pollutant from * * * stationary
sources [in 28 listed categories]. * * * Such
term also includes any other source with the
potential to emit two hundred and fifty tons
per year or more of any air pollutant.
(Emphasis added.) Similarly, Title V
requirements apply to ‘‘major
source[]s,’’ under CAA § 502(a), and that
term is defined under CAA § 501(2)(B)
and CAA § 302(j) as—
any stationary facility or source of air
pollutants which directly emits, or has the
potential to emit, one hundred tons per year
or more of any air pollutant * * *.
(Emphasis added.) The term ‘‘air
pollutant,’’ which, as just noted, is
central to the applicability provisions of
both PSD and title V, is defined under
CAA § 302(g) as—
any air pollution agent or combination of
such agents, including any physical,
chemical, biological, radioactive * * *
substance or matter which is emitted into or
otherwise enters the ambient air.
As just noted, EPA treats sources
emitting air pollutants as subject to PSD
and title V requirements only if the air
pollutants are ‘‘subject to regulation’’
under other provisions of the CAA.
EPA’s current interpretation of ‘‘subject
to regulation’’ is found in the PSD
Interpretive Memorandum, which
defines the term as meaning subject to
either a provision in the CAA or a
regulation adopted by EPA under the
CAA that requires actual control of
emissions of that pollutant, and to
exclude pollutants for which EPA
regulations only require monitoring or
reporting. Accordingly, under the PSD
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Interpretive Memorandum, the air
pollutant that is subject to regulation is
the air pollutant for which actual
controls are required under other
provisions of the CAA.
We believe that PSD and title V
requirements will be triggered for GHGs
if EPA completes the rulemaking that
EPA is currently proposing for lightduty vehicles and vehicle engines. That
rule is based on CAA § 202(a).
Paragraph (1) of § 202(a) provides, in
relevant part:
The Administrator shall by regulation
prescribe (and from time to time revise) in
accordance with the provisions of this
section, standards applicable to the emission
of any air pollutant from any class or classes
of new motor vehicles or new motor vehicle
engines, which in his judgment cause, or
contribute to, air pollution which may
reasonably be anticipated to endanger public
health or welfare.
(Emphasis added.) This provision, by its
terms, requires, as a pre-requisite for
regulating an ‘‘air pollutant’’ from the
described mobile sources, that EPA
must make what has come to be called
an ‘‘endangerment finding’’ for that ‘‘air
pollutant;’’ and further requires that
once EPA makes that endangerment
finding, EPA must proceed to ‘‘set
standards [for new motor vehicles]
applicable to the emission of [the] air
pollutant’’ for which the endangerment
and companion cause or contribute
finding was made. EPA has already
proposed an endangerment finding for
the air pollutant comprised of the
collective group of six GHGs: CO2, CH4,
N2O, SF6, HFCs, and PFCs, as well as a
finding that new motor vehicle
emissions of the 6 GHGs, viewed as a
single group air pollutant, contribute to
this endangerment. 74 FR 18886, 18904,
18907 (April 24, 2009).25 Four of these
GHGs are emitted by light-duty motor
vehicles; as a result, concurrently with
this rule, EPA is proposing to set
emissions standards for those four
GHGs. As noted in the light-duty
vehicle rule and below, EPA can set
standards for the specific GHGs emitted
by light-duty motor vehicles versus for
the single air pollutant that is comprised
of the six GHG, and still comply with
the requirement in section 202(a)
regardless of how EPA finally defines
‘‘air pollutant’’ in the final
endangerment and contribution
findings. EPA is proposing to regulate
the GHGs emitted by light-duty vehicles
by establishing separate emission
25 In the proposed endangerment finding, the
Administrator also stated that if each of the four
GHGs emitted by new motor vehicles were treated
as separate air pollutants, she would find that each
of the four contributes individually to the air
pollution that endangers.
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standards that limit emissions of CO2,
CH4, and N2O. EPA would also allow
credit towards the CO2 standard based
on vehicle air conditioner controls that
reduce emissions of HFCs.
In light of how the proposed
endangerment and contribution finding
identifies, and light-duty vehicle rule
regulates, emissions of, the ‘‘air
pollutant’’ under CAA § 202(a), EPA’s
task in this proposal is to identify the
‘‘air pollutant’’ for which PSD and title
V will become applicable under CAA
§§ 165(a)/169(1) and CAA §§ 502(a)/
501(2)/302(j). This ‘‘air pollutant,’’ for
PSD and title V purposes, is the ‘‘air
pollutant’’ that is ‘‘subject to regulation’’
under CAA § 202(a), according to EPA
interpretation.
We are proposing that the relevant
‘‘air pollutant’’ for purposes PSD and
title V applicability is the single air
pollutant that is comprised of the group
of six GHGs, as proposed in the § 202(a)
endangerment and contribution
findings. These six GHGs as a class
comprise the air pollutant that is the
subject of the endangerment finding and
companion contribution finding and
constitute the air pollutant that is
regulated by the light-duty vehicle rule
through measures that address the
components of that air pollutant that are
emitted from the mobile sources. Thus,
although the CAA § 202(a) proposal
establishes controls only with respect to
four GHGs, as a legal matter the
proposal covers the entire set of GHGs
that as a class are the single ‘‘air
pollutant’’ in the proposed
endangerment and contribution
findings.
We also solicit comment on whether
only the four GHGs actually controlled
under the mobile source rule should be
treated as the ‘‘air pollutant’’ subject to
PSD and title V applicability. In
particular, we solicit comment on
whether such an approach would be
consistent with our treatment of other
‘‘air pollutants’’ that are comprised of
numerous individual substances (e.g.,
VOCs or PM), and how it interacts with
EPA’s duty under section 202(a) to sets
standards for emissions of the ‘‘air
pollutant’’ for which a contribution
finding is made under that section.
In addition, we further believe that
the definition of ‘‘air pollutant’’ for PSD
and title V purposes provides for
sufficient flexibility that the form of the
standard—that is, the metric—that EPA
adopts for PSD purposes may differ
from the form that EPA adopts for
purposes of regulation under CAA
§ 202(a). Section 202(a) authorizes EPA
to set ‘‘standards applicable to the
emission of [the] air pollutant.’’ This
provides EPA significant discretion in
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determining how to structure its new
motor vehicle standards, as long as they
are ‘‘applicable to emission’’ of the air
pollutant. How EPA exercises its
discretion under this provision, whether
by separate standards, a collective
standard, or some combination of these,
as has been proposed, does not change
the fact that each of these approaches
has the same result—regulating the air
pollutant which is the subject of the
contribution finding under section
202(a). It is this overall result—
regulation of the air pollutant—that
determines the applicability of PSD and
title V, not the particular form of the
standards adopted under section 202(a).
To reiterate, under 302(g), ‘‘air
pollutant’’ means ‘‘any air pollution
agent or combination of such agents,
including any physical, chemical,
biological, radioactive * * * substance
or matter which is emitted into or
otherwise enters the ambient air.’’ We
believe that as long as the same ‘‘air
pollution agent or combination of such
agents’’ is regulated for PSD and title V
purposes as is regulated under CAA
§ 202(a), then the PSD and title V
applicability requirements are met,
whether or not the structure of the
regulation is the same as employed
under section 202(a). Accordingly, we
believe that as long as the six GHGs that
are the ‘‘air pollutant’’ being regulated
under CAA § 202(a) are subject to PSD
and title V applicability through some
metric, then the precise metric through
which they are subject to PSD and title
V may differ from the precise manner in
which they are regulated under CAA
§ 202(a). Thus, we believe we may treat
the six GHGs as a group for PSD and
title V purposes, and weight them by
their GWP, even though they are
generally regulated individually under
the mobile source rule.
b. Policy and Programmatic Rationale
For individual GHGs, differing CO2
equivalent factors (such as GWP values)
are found in the literature. As noted
earlier in this preamble, the U.S. and
other countries report their annual
emissions of the six GHGs in terms of
CO2e units, following UNFCCC
guidelines. The UNFCCC reporting
guidelines for national inventories, as
updated in 2006, require the use of
GWPs from the IPCC SAR (IPCC 1996)
for CO2e calculations, even though the
IPCC has subsequently updated its GWP
values.26 Consistent with these most
26 ‘‘Inventory of U.S. Greenhouse Gas Emissions
and Sinks: 1990–2007,’’ U.S. Environmental
Protection Agency, EPA 430–R–09–004, April 15,
2009. p. ES–3. See also the SAR GWPs (IPCC 1996)
in table 1–2, p. 1–6. https://www.epa.gov/
climatechange/emissions/usinventoryreport.html.
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recent guidelines, we are proposing to
use the same SAR-derived GWP values,
which are based on the effects of GHGs
over a 100-year time horizon, for
purposes of calculating GHG emissions
in tpy CO2e for this tailoring rule.
We recognize a number of advantages
in the use of a cumulative CO2e measure
(‘‘cumulative’’ here refers to the
summation of emissions of CO2e for all
applicable GHGs) using GWP over an
individual, mass-based metric,
including: (1) A cumulative CO2e
metric, by incorporating the GWP
values, addresses the combined
radiative forcing of the GHGs emitted;
(2) a cumulative CO2e metric by
definition includes any of the six
primary GHGs that are emitted and
therefore would effectively include any
one or combination of the six primary
GHGs that might become subject to
regulation, thus encompassing a greater
variety of possible future regulatory
approaches; (3) a cumulative CO2e
metric would be consistent with the
proposed mandatory reporting rule
thresholds (thereby creating a ‘‘common
currency’’ for recordkeeping for both
industry and permitting authorities);
and (4) a CO2e metric could allow more
flexibility for designing and
implementing control strategies that
maximize reductions across multiple
GHGs and would also likely align better
with possible future regulations that
allow for such flexibility.
We also considered a GHG permitting
threshold metric based on individual
GHGs on a mass basis, with no GWP
applied. The main benefit of an
individual-GHG-based metric is that it
may provide some ability to better
differentiate sources and project
emissions that affect one particular
GHG. Because of this differentiation, it
also may allow for simpler program
implementation with regards to
establishing emissions limits,
establishing BACT, compliance
assessment, and measurement/
monitoring methods. However, we
believe that the benefits in using the
cumulative group of GHGs outweigh
any implementation advantages to using
an individual-GHG-based metric. In
particular, the cumulative-GHG, CO2ebased metric addresses all GHGs and
their radiative forcing potential and
would provide some flexibility to a
source to design and maximize GHG
reductions across the facility.
Conversely, an individual-GHG-based
metric may limit a facility’s flexibility to
maximize GHG reductions across GHGs
and is generally less consistent with the
widespread treatment of GHGs in
inventory, reporting, and emissions
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offset protocols mentioned in section
VIII.B.1 of this preamble.
We solicit comment on the benefits
and limitations of our proposed GHG
PSD and title V permitting threshold
metric based on CO2e. We also request
comments on proposed alternative
metrics (such as individual GHG basis)
and the effect those alternative metrics
would have on setting permitting
thresholds for GHGs.
3. Possible Limitation of Proposed
Metric for PSD and Title V Thresholds
and for PSD Netting Purposes
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a. PSD and title V applicability
thresholds
This proposed metric may also
warrant a limitation for PSD and title V
threshold purposes. In rare instances, it
is possible that a source may emit only
a non-CO2 GHG in very small amounts,
on a mass basis, but one that carries a
very large GWP. In this case, it is
possible that the source may emit the
GHG in amounts that fall below the PSD
statutory applicability threshold of 100/
250 tpy on a mass basis, and fall below
the title V statutory applicability
threshold of 100 tpy on a mass basis, but
exceed the 25,000 CO2e PSD and title V
applicability thresholds (which, as
discussed above, are calculated on a
GWP basis) proposed in this action.
Under these circumstances, the source
would trigger PSD and title V under our
proposed rule even though its GHG
mass emissions would not, in fact,
exceed the statutory triggers.
We seek comment on whether we
should address this case; that is,
whether such a source should be subject
to PSD or title V. Because the PSD and
title V statutory thresholds are
expressed on a mass basis—i.e., tpy—we
are concerned that the metric proposed
with this action could have the effect of
subjecting to PSD or title V
requirements a source whose emissions
fall below the statutory threshold limits
on a mass basis. Accordingly, we seek
comment on whether we should include
some refinements to the CO2e metric,
such as adding a 100- or 250-tpy metric
that is mass-based. Under this
refinement, a source would be subject to
PSD and title V only if its GHG
emissions exceeded the statutory
threshold levels on an actual tonnage
basis and if its GHG emissions exceeded
the first phase threshold emissions
proposed in this notice on a CO2e basis.
However, we are also concerned that
efforts to address this circumstance—for
example, by requiring separate tracking
of individual GHG mass emissions in
addition to CO2e for up to six gases—
would be complex and confusing to
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administer. Similarly, as discussed
above, we are concerned that
implementing permitting only on an
individual gas basis would have several
disadvantages compared to our
proposed CO2e-based approach.
b. Netting
The same issue is also a concern as
the proposal relates to PSD netting. By
way of background, an existing source
becomes subject to PSD when it makes
a major modification, which generally
occurs when the source is a major
emitting facility and makes a physical or
operational change that increases its
emissions of a regulated air pollutant by
a significant amount. In calculating the
amount of the increase in emissions, the
source must add to the increase the
amount of any contemporaneous—
generally, within the previous 5 years—
increases and decreases that resulted
from other changes the source made. If
the total amount, so calculated, does not
exceed the significance level, then the
source is not subject to PSD for the
change, and instead has ‘‘netted out’’ of
PSD.
In rare instances, it is possible that a
source of two or more different types of
GHGs, with different GWPs, may make
two or more contemporaneous changes
that increase its emissions of one type
of GHG and decrease its emissions of
another type of GHG. The effect of those
changes may be that the source will
have decreased its emissions of its
GHGs on a mass basis, but increased its
emissions of GHGs on a CO2e basis
above the significance level. Under
these circumstances, we are seeking
comment on whether that source should
be treated as being subject to PSD due
to its physical or operational change.
We could prevent the source in this
example from becoming subject to PSD
by requiring that for an existing source’s
physical or operational change to be
treated as a modification that triggers
PSD due to its GHG emissions, the
change must, taking into account
contemporaneous changes, increase
GHG emissions on a mass basis by any
amount, and increase GHG emissions on
a CO2e basis by the amount of the
significance level proposed in this
action. However, we are concerned that
efforts to address this circumstance
would be even more complex and
confusing to administer for netting than
it would be for major source
determinations.
We therefore solicit comment on how
best to address these situations
involving new source permitting and
netting in light of our proposed choice
of a GHG PSD and title V permitting
threshold metric based on CO2e. We are
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asking for comment on whether these
rare circumstances should be addressed
in light of the statutory language, and if
so, how. Would a mass-based metric for
each individual GHG be an appropriate
way to address the issue and, if so,
should it be implemented in addition to,
or in place of, our proposed CO2e
metric?
C. What is the rationale for selecting the
proposed GHG permitting thresholds for
PSD?
1. Major Stationary Source Applicability
Threshold for Sources of GHGs
With this action, we are proposing to
establish, for the first phase of the PSD
GHG tailoring program, the PSD major
source threshold at 25,000 tpy CO2e and
the significance level at 10,000 to 25,000
tpy CO2e, based on the legal doctrine of
‘‘absurd results’’ and ‘‘administrative
necessity,’’ as described in section VI of
this preamble. This first phase will be
followed by a study and then
promulgation of additional rulemaking
that will establish the next phase of
requirements. This section provides a
more detailed discussion of the
technical and policy basis for
establishing these threshold levels.
a. Administrative Burdens Associated
With the Statutory Threshold Level and
the Proposed Permitting Threshold
Level
As noted previously, for PSD
purposes, if we do not establish a
different ‘‘major’’ source level for GHG
emitters, the effect would be that the
statutory threshold level would apply,
so that GHG sources in the 28 listed
categories under CAA section 169(1)
would be subject to a 100-tpy threshold,
and all other GHG sources would be
subject to a 250-tpy threshold. Under
this scenario, tens of thousands of
sources each year would undertake
projects that would have to comply with
the PSD program, which would
overwhelm the permitting authorities
and interfere with the issuance of
permits to all sources, whether they
emit GHGs or not.
Accordingly, EPA is proposing a PSD
‘‘major’’ source applicability threshold
of 25,000 tpy CO2e. The rationale for
this level is to reduce the administrative
burden to the point where it is no longer
administratively impossible to
implement the PSD program. Although
requiring permitting authorities to
permit sources of GHG emissions at
25,000 tpy CO2e and higher would
increase the level of PSD permitting and
therefore increase administrative
burdens, compared to current
permitting levels, EPA believes that this
increase would not exceed the capacity
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of permitting authorities to implement
the PSD program.
EPA calculated the administrative
burden of permitting GHG emitters at
the 25,000-tpy CO2e threshold level as
follows: As noted earlier in this
preamble, EPA conducted a threshold
data analysis that provided information
on the numbers of facilities that could
potentially be subject to PSD review
under different CO2e-based emissions
thresholds and the administrative
resources needed to process permits for
these facilities. Through the process
described in this section of the
preamble, we estimate that, at a 25,000tpy CO2e applicability threshold for PSD
major sources, approximately 400
additional new or modified facilities
would be subject to PSD review in a
given year. These include
approximately 130 new facilities and
approximately 270 modifications at
existing major sources that would be
subject to PSD review as major
modifications. Many, but not all, of
these facilities would be subject to PSD
review for other pollutants that they
emit. These estimates compare to the
280 PSD permits that are currently
issued in a typical year.
We acknowledge that our estimates
for both new facilities and modifications
are highly uncertain because they rely
on growth trends in industries and
businesses, which are inherently
difficult to predict, especially under
changing economic conditions.
We developed these estimates as
follows: To estimate the number of new
sources, we identified the various
source or industry categories included
in the threshold data analysis, along
with the number of sources in each
category. We then applied source- or
industry-specific growth rates to
estimate the number of new facilities
that would be added in a year at a given
major source threshold for a source or
industry category. The methodology and
results for estimating new sources is
described in the Technical Support
Document, in the docket for this
rulemaking.27
To estimate the number of
modifications at existing major sources,
EPA first calculated the number of
existing facilities that would be treated
as ‘‘major’’ sources due to their PTEbased CO2e emissions rates. At a 25,000tpy CO2e permitting threshold, EPA
estimates that about 13,600 existing
facilities would be classified as ‘‘major’’
sources. Second, EPA determined the
27 ‘‘Technical Support Document for Greenhouse
Gas Emissions Thresholds Evaluation;’’ Air Quality
Policy Division, Office of Air Quality Policy and
Standards; U.S. Environmental Protection Agency;
July 7, 2009.
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current rate of PSD-permitted
modifications occurring at major
sources nationwide, which is
approximately 2 percent of existing
major sources. The basis for this
modification rate is described in a
technical support document found in
the docket for this rulemaking.28 Then,
we assumed that GHG sources would
modify at the same 2-percent rate. Based
on this assumption, EPA estimates that
approximately 270 modifications would
result from a 25,000-tpy CO2e major
source permitting threshold.
We calculated the additional
administrative burden in workload
hours and costs based on the per-permit
hourly workload estimates and costs for
PSD permitting from the PSD ICR.29 Of
the group of 130 new sources, we
estimated the number of industrial
sources and of commercial or residential
sources. For the industrial sources, we
assumed that permitting authorities
would need to spend 301 hours, on a
per-permit basis, for issuing permits that
cover both the GHG and non-GHG
emissions. This is the same amount of
time that permitting authorities need to
permit non-GHG emissions from
industrial sources. We did not assume
additional workload requirements for
the GHG emissions because permitting
authorities will have some experience
with the emissions units, sources, and
configurations at these facilities. Also,
although there will be new and unique
GHG sources to consider at some of
these facilities, this experience should
provide some administrative efficiencies
in preparing and processing GHG-based
permit applications for these facilities.
Note that some of the 130 new sources
would be sources that are subject to PSD
only because of their GHG emissions.
We estimate that the permitting
authorities would need to spend the
same amount of time and money on
these permits, on a per-permit basis, as
the authorities do on new sources of
non-GHG emissions. For the commercial
or residential sources, we assumed that
permitting authorities would require 20
percent of the time for industrial
sources, or 60 hours, because these
sources tend to be less complex than
industrial sources.
The next group of permittees is the
270 GHG sources that are subject to PSD
each year because they undertake
modifications. For modifications
involving industrial sources, we
28 ‘‘Methodology for Estimating Modified Sources
That Would be Subject to PSD Permitting for
GHGs;’’ Prepared by EPA Staff; August 2009.
29 ‘‘Summary of ICR-based Data Used to Estimate
Avoided Burden and Evaluate Resource
Requirements at Alternative GHG Permitting
Thresholds;’’ Prepared by EPA Staff; August 2009.
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assumed that permitting authorities
would need to expend 301 hours, the
same as for new sources; for
modifications involving commercial or
residential sources, we assumed 60
hours—the same, again, as for new
sources.
All told, the increase in burden for
permitting authorities from including
sources of GHGs at a 25,000-tpy CO2e
level, on a total national basis, would be
approximately 112,000 staff hours at an
additional cost of approximately $8
million. This workload amount
represents an increase of about 1.3
times, or 32 percent, in the current
burden for permitting authorities on a
nationwide basis. We believe that this
additional burden is manageable, but
that it will necessarily pose some
challenge to permitting authorities, and
that to accommodate the additional
burden, permitting authorities may need
to expand their resources or seek
efficiencies in processing permits. We
believe that any threshold lower than
25,000 tpy CO2e, would create undue
administrative burdens. Thus, we
believe that the amount of
administrative burden attendant to a
threshold level of 25,000 tpy CO2e is
consistent with the administrative
necessity case law, which, as described
earlier, we read to limit us to depart
from the statutory requirements to the
smallest extent possible, consistent with
congressional intent.
We request specific comments on our
estimated burden at the 25,000-tpy CO2e
threshold and on whether the additional
workload would be manageable to
permitting authorities.
We also request comment specifically
on the assumptions we used for
calculating the administrative burden
from modifications. As noted earlier,
our estimate for the number of
modifications that would undergo PSD
review as a result of a 25,000-tpy CO2e
permitting threshold is based on the
modification rate at existing major
sources for currently regulated
pollutants, which means that the
estimate assumes that the modification
rate for GHG sources is similar to that
for sources of currently regulated
pollutants despite the potential
difference in types of projects and
significance levels. We acknowledge
that our estimates for modifications are
highly uncertain because they rely on
growth trends in industries and
businesses, which are inherently
difficult to predict, especially under
changing economic conditions. Thus,
there is significant uncertainty in
applying this modification rate and
therefore in predicting not only how
many major sources will undergo
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physical or operational changes in any
given year, but also which of those
changes would result in GHG emissions
increases that would exceed a proposed
GHG significance level. We are therefore
requesting specific comment on our
estimate of modification rates at major
sources and soliciting any additional
information and data that would
improve our estimate of the number of
modifications affecting GHG emissions
at different types of source categories.
b. Administrative Burdens Associated
With Other Permitting Threshold Levels
In addition to the 25,000-tpy
threshold for CO2e, we also considered
major source applicability thresholds for
PSD ranging from 1,000 to 100,000 tpy
CO2e. Using the basic analysis of new
and modified facilities that would
become subject to PSD review as
described above, we estimated the
number of new facilities and
modifications at each of these
thresholds. A summary of these results
is shown in table VIII–1. The results
shown in table VIII–1 are based on
estimates of potential to emit, measured
in short tons of CO2e, from affected
facilities at each threshold level. It
should be noted that the use of short
tons here, while consistent with the
units used for existing major source
thresholds for other pollutants
identified in the CAA and permitting
program rulemakings, differs from the
units of metric tons used in EPA’s GHG
Mandatory Reporting Rule proposal. For
consistency within the permitting
programs, all data and discussion in this
rule are based on short tons.
We believe that the number of new
permits that would be subject to PSD at
the 10,000-tpy-and-below CO2e major
source thresholds would not be
administratively feasible for permitting
authorities. For example, we estimate
that the 10,000-tpy CO2e threshold
would cause an approximately threefold increase in the number of PSD
permits annually (830 compared to 280),
resulting in an additional workload for
permitting authorities of approximately
187,000 hours, or an increase of about
2.2 times over their current PSD
workload. We believe that this increase
in the number of PSD permits and
workload would create insurmountable
resource demands for permitting
agencies in the near term, which would
jeopardize the functioning of the PSD
program. These time demands are due
to not only the increase in number of
permits but also the need to implement
BACT determinations, GHG emissions
evaluations, and other evaluations
required under the PSD program for a
wide variety of formerly unpermitted
sources, including significant numbers
and varieties of small manufacturing
and commercial establishments.
Permitting authorities would confront
substantial challenges because the
authorities have little experience with
these sources and their GHG emissions.
We request comment on our
assessment of the impact of major
source GHG thresholds lower than
25,000 tpy CO2e on PSD program
administration, including any
additional information on the number of
sources and modification projects that
might be affected at these lower
thresholds for different GHG source
categories. We also request comment on
our conclusion that the 10,000-tpy
threshold (or a lower threshold) would
be too low to sufficiently address the
administrative concerns.
TABLE VIII–1—ESTIMATED NUMBER OF EXISTING FACILITIES AND ANNUAL NUMBER OF NEWLY CONSTRUCTED FACILITIES
AND MODIFICATIONS POTENTIALLY SUBJECT TO PSD REVIEW AT DIFFERENT GHG MAJOR SOURCE THRESHOLDS
Number of existing facilities
exceeding
threshold
Major stationary source threshold level
(tpy CO2e)
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1,000 ................................................................................................................................
5,000 ................................................................................................................................
10,000 ..............................................................................................................................
25,000 ..............................................................................................................................
50,000 ..............................................................................................................................
100,000 ............................................................................................................................
At the 50,000-tpy CO2e threshold, we
estimate approximately 220 PSD permit
actions due to GHG emissions. We do
not believe that this level of permit
activity would challenge the capacity of
permitting authorities to properly
administer the PSD program to the
extent we described above for the
25,000-tpy CO2e threshold. As noted
elsewhere in the legal discussion of the
absurd results and administrative
necessity doctrines, we are foreclosed
from adopting higher thresholds when
we believe a lower threshold would be
possible to implement. We request
comment on our assessment of the
impact of major source GHG thresholds
higher than 25,000 tpy CO2e on PSD
program administration, including any
additional information on the number of
sources and modification projects that
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might be affected at these higher
thresholds for different GHG source
categories. We also request comment on
our determination that this assessment
supports a conclusion that the 25,000tpy threshold is administrable and thus
we do not need to adopt a threshold of
50,000 tpy. We note that the 50,000-tpy
level does involve about 6,400 fewer
major sources than the 25,000-tpy level,
including about 1,600 sources that
would have been newly defined as
major (e.g., landfills, hospitals, offices,
hotels). In light of this, we specifically
ask for comment on whether a 50,000tpy level, which would exclude these
sources, is administratively necessary.
c. Emissions Impacts
We also evaluated the amount of GHG
emissions emitted by facilities that
PO 00000
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Sfmt 4702
Number of new
facilities that
would exceed
threshold
(facilities/yr)
278,340
52,888
26,898
13,661
7,245
4,850
4,330
532
289
128
77
66
Number of modifications at existing facilities that
would exceed
threshold
(modifications/yr)
5,567
1,058
538
273
145
97
would be subject to PSD requirements at
the proposed thresholds, although,
strictly speaking, this information is not
relevant to the administrative-necessity
basis for selecting the proposed major
source threshold level for CO2e. The
objective of the emissions evaluation
was to generally assess the extent to
which, on a national basis, GHG
emissions sources would be covered at
the proposed thresholds. The basis for
this evaluation, with a detailed
summary of the results, is provided in
the docket for this rulemaking.30
We estimate that a 25,000-tpy CO2e
threshold captures approximately 68
30 ‘‘Technical Support Document for Greenhouse
Gas Emissions Thresholds Evaluation; Air Quality
Policy Division, Office of Air Quality Policy and
Standards; U.S. Environmental Protection Agency’’;
July 7, 2009.
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percent of national CO2e stationary
source GHG emissions (including
approximately 87 percent of CO2). This
emissions coverage is comparable to
national stationary source NOX
emissions coverage of 72 percent at the
existing PSD major source permitting
threshold of 250 tpy NOX. Lowering the
CO2e threshold to 10,000 tpy increases
the amount of emissions covered by
only 2 percent compared to the 25,000-
tpy threshold but almost doubles the
number of facilities covered. We
estimate that a 10,000-tpy CO2e
threshold would also affect
approximately 7,000 commercial and
multi-family residential sources. A
50,000-tpy CO2e threshold would
virtually eliminate all of the
commercial/residential sector from
being affected for GHG but would fail to
capture some high emitters within key
55333
GHG categories (for example, iron/steel,
refineries, electric generation, pulp and
paper, petrochemical) and would reduce
emissions coverage by about 2 percent
compared to 25,000 tpy CO2e. A
summary of the percentage of national
stationary source GHG emissions
associated with the affected facilities at
different GHG emission thresholds is
shown in Table VIII–2.
TABLE VIII–2—PERCENTAGE OF NATIONAL STATIONARY SOURCE GHG EMISSIONS FROM AFFECTED FACILITIES AT
DIFFERENT GHG EMISSION THRESHOLDS
Number of existing facilities
exceeding
threshold
Major stationary source threshold level
(tpy CO2e)
1,000 ................................................................................................................................................................
5,000 ................................................................................................................................................................
10,000 ..............................................................................................................................................................
25,000 ..............................................................................................................................................................
50,000 ..............................................................................................................................................................
100,000 ............................................................................................................................................................
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Estimates of emissions coverage at
different thresholds are not the same as
estimates of the actual quantities of
emissions that would be reduced
through the PSD permitting program at
these permitting thresholds; however,
they do illustrate that at the proposed
25,000-tpy CO2e source threshold, the
most significant contributors to
stationary source GHG emissions would
still be covered by the PSD program as
major sources, and therefore any
modifications or new additions at these
source categories would potentially be
subject to PSD requirements, including
BACT.
2. Significance Levels
With this action, we are also
proposing a temporary, first phase GHG
PSD significance level threshold based
on administrative necessity. As noted
previously, there are no existing PSD
significance levels set for any of the
GHG pollutants.
Until we establish significance levels
for these pollutants, those levels in
effect remain at zero tpy, so that any
physical or operational change that
increases GHG emissions by any amount
would constitute a modification and
therefore would be subject to PSD.
Thus, for any major source, any minor
change that increases fuel combustion
even slightly would increase GHG
emissions and, as a result, potentially
trigger PSD review. As with
administrative burdens associated with
the statutory major source PSD
applicability threshold, the burdens
associated with the hundreds of
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thousands of modification projects that
would have to comply with the PSD
program under these circumstances
would be enormous, at least in the short
term. They would overwhelm the
permitting authorities as well as the
regulated community, and would
interfere with the issuance of PSD
permits to sources of all types, whether
emitting GHGs or not.
As a result, we believe that the same
legal doctrines of absurd results and
administrative necessity apply for
establishing the significance level. We
need to phase in a significance level for
GHGs by establishing, in the first phase,
a reasonable significance level based on
administrative necessity, and then by
conducting a study and promulgating
further rulemaking to establish the
requirements for the second phase.
To do so, we need information
concerning the number of modification
projects occurring at a facility level for
different source categories that would
exceed various possible significance
levels for GHGs in any given year.
However, it is very difficult to acquire
or develop this information—and
therefore there is great uncertainty in
calculating specific administrative
burdens associated with
modifications—for several reasons.
First, information is not available across
sectors and source categories on the
types and numbers of specific physical
and operational changes that would
result in emissions increases in amounts
that can be estimated and that therefore
can be compared to various GHG
emissions significance levels. Second,
PO 00000
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278,340
52,888
26,898
13,661
7,245
4,850
Percent of national stationary
source GHG
emissions
(percent)
73
71
70
68
65
64
there is general uncertainty in how
many project modifications will occur
within any given year because decisions
on these projects are driven by facilityand sector-based growth patterns and
business planning decisions. Lastly,
some source categories and units that
emit GHGs have not previously been
subject to any type of permitting or
reporting requirements; as a result, for
these sources, there is very little
historical record for use in estimating
the number and types of projects that
would occur at these sources and, in
turn, establish an appropriate
significance level for GHGs.
Absent comprehensive information on
the types and numbers of modification
projects nationally that result in
increases in GHG emissions, we are
proposing and soliciting comment on a
range of possible significance levels for
CO2e. Our proposed range starts at
10,000 tpy CO2e, which reflects, subject
to the uncertainty noted above, our
current estimate of what would
constitute a GHG significance level
below which permitting authorities
would be unable to adequately
administer PSD, and goes up to 25,000
tpy CO2e, which is our proposed major
source applicability threshold for GHGs
under PSD. We believe that a 25,000-tpy
CO2e significance level for GHGs would
be the highest level we could consider
because it is not reasonable to propose
a significance level that is higher than
the proposed major source threshold.
We selected the GHG significance
level at the lower end of the proposed
range by analyzing inventory
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information for key source categories
that would have a substantial number of
modification projects potentially subject
to PSD permitting requirements for
GHGs. Most importantly, depending on
the significance level for CO2e, small
fossil fuel-fired combustion units,
which are numerous and ubiquitous,
could have a substantial number of
modifications that would be subject to
PSD. Our threshold data analysis shows
that almost 80 percent of the facilities
that exceed the 25,000-tpy CO2e major
source threshold do so because of fossil
fuel combustion units that emit CO2.
Also, the U.S. national GHG inventory
shows that approximately 80 percent of
all GHG emissions result from fossil fuel
combustion sources. The prevalence of
combustion units across all affected
sectors, and the dominant contribution
of CO2 fuel combustion-related
emissions to their GHG emissions total,
leads us to conclude that an
administrative necessity-based
significance level for CO2e should be
based on modifications that involve
these combustion units.
Thus, we analyzed sales data for two
of the most affected categories of units:
Boilers and stationary engines. Our
analysis indicates that, on a yearly basis,
almost 2,000 of these new combustion
units would emit more than 10,000 tpy
CO2e. The exact number of PSD permits
that would result from modifications
involving these new emissions units
would likely be less than 2,000,
depending on whether these units are
located at a major source facility,
whether multiple units are aggregated at
one facility or the units are placed at
different facilities, and whether they are
considered new additions/new capacity
or one-for-one replacements. However,
we believe these data on combustion
unit sales suggest that the significance
level should be at least 10,000 tpy CO2e
because, while the estimated population
of new units with the potential to trigger
PSD is something below 2,000 per year,
that is still likely well above the current
number of modifications (fewer than
300) that are currently subject to PSD
each year. Any lower level would risk
enormous numbers of permit
applications that would be
administratively impossible to process,
and therefore we do not propose a GHG
significance level lower than 10,000 tpy
CO2e. Further support for the 10,000-tpy
CO2e level is the fact that the
combustion units in the industrial
sector that emit GHGs at this rate tend
to be larger units: boiler-type units with
an approximate heat input rating of 15–
20 MMBtu/hr (depending on fuel type);
and stationary internal combustion (IC)
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or compression ignition (CI) engines
with a rating of greater than 2,000
horsepower. Units of this size provide a
good representation of combustion units
utilized in the industrial sector that
should be subject to PSD. At the same
time it does not capture an enormous
number of very small combustion units
that would overwhelm permitting
authorities from an administrative
standpoint. For example, using the same
sales information referenced above on
combustion units, we estimate that
approximately 29,000 new boilers and
stationary engines would exceed a 250tpy CO2e level. A summary of our
significance level analysis for CO2e is
provided in the docket for this
rulemaking.31
Although our significance level range
is driven by our analysis of CO2
combustion units, we believe that the
level of 10,000 tpy CO2e should be
administratively feasible for other
sources of GHG emissions. Our
threshold data analysis shows
approximately 3,000 facilities that
would have the potential to emit
amounts of non-CO2 GHGs exceeding a
25,000-tpy CO2e major source threshold
based on their non-CO2 emissions alone.
Although this estimate is not directly
related to the number of possible
modification projects that may exceed a
10,000-tpy CO2e significance level for
non-CO2 emissions alone, this estimate
provides a relative sense of the number
of facilities emitting non-CO2 emissions
at rates that approximate the 10,000-tpy
CO2e level, only a portion of which may
actually undergo modifications that
would potentially be subject to PSD
review. For example, if the 3,000
facilities are assumed to have a
modification rate of 2 percent, as
described above, and each modification
results in emissions increases of at least
10,000 tpy CO2e (in, again, non-CO2
GHG emissions), then approximately 60
modification projects would come
under PSD review just for principally
non-CO2 sources. This alone would be
an approximate 20- to 25-percent
increase above the current level of 280
annual permits. We believe that an
additional PSD permit increase of this
magnitude, on top of the modifications
resulting from CO2 emissions from
combustion-related projects, may stretch
the capacity of, but may not necessarily
create an unadministrable burden for,
permitting authorities.
Although we believe 10,000 tpy CO2e
represents a reasonable lower bound for
the range we are proposing for the GHG
31 ‘‘Summary of Administrative Necessity Basis
for a CO2-e Significance Level’’; Prepared by EPA
Staff; August 2009.
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significance level, we specifically
request comments on whether: (1) A
level lower than 10,000 tpy CO2e would
still be administratively feasible; (2) a
level higher than 25,000 CO2e is
necessary to avoid an administratively
overwhelming number of modification
projects becoming subject to PSD
permitting due solely to their GHG
emissions; and (3) there are data
suggesting an appropriate number we
should select within the 10,000- to
25,000-tpy range. In suggesting
alternative thresholds, we request that
commenters submit any available
information and data that would allow
us to better characterize the number and
types of modification projects that
would become subject to the PSD
program at different GHG significance
levels and for different types of source
categories.
We note that this basis contrasts with
that of our prior significance levels
determinations, which were based on de
minimis emissions levels.
D. What is the rationale for selecting the
proposed first phase GHG permitting
threshold for title V?
With this action, we are proposing a
temporary, first phase GHG title V major
source threshold of 25,000 tpy CO2e,
based on the administrative imperatives
that underly both the absurd results and
administrative necessity legal doctrines.
As noted earlier, if we do not
establish a different ‘‘major source’’
level under title V for GHG sources,
those sources would become subject to
the statutory 100-tpy threshold. Under
these circumstances, we estimate that
6.1 million sources would have to
comply with the title V permitting
program. The resulting administrative
burdens would be enormous in the short
term and would overwhelm the
permitting authorities, as well as posing
severe burdens on the regulated
community. Accordingly, we need to
phase in title V applicability by
establishing, in the first phase, an
administrable permitting threshold, and
then by conducting a study and
promulgating further rulemaking to
establish the requirements for the
second phase.
The criterion for establishing the title
V major source threshold is to reduce
administrative burdens to the point at
which the title V program can be
implemented. Our analyses, discussed
in detail later in this preamble, establish
this threshold at 25,000 tpy CO2e.
Although this level would likely see an
increase in the volume of title V
permitting, compared to current
permitting levels, and although this
increase would pose some challenges to
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permitting authorities, EPA believes that
this increase would not exceed the
capacity of permitting authorities to
implement the program.
The title V permitting program
requires all existing major sources to
obtain operating permits, as compared
to the PSD program, which requires
permits only for newly constructed
major source facilities and major
modifications at existing major sources.
Therefore, to evaluate permitting
thresholds for title V, we analyzed the
number of existing facilities that would
exceed a given GHG threshold. We
considered alternative major source
thresholds ranging from 1,000 to
100,000 tpy CO2e.
Our estimates for the existing number
of facilities whose emissions would
exceed different GHG thresholds are
summarized in table VIII–1 and
discussed in more detail in the
Technical Support Document in the
docket for this rulemaking.32 For
comparison purposes, note that
currently there are approximately
14,700 title V operating permits
nationwide. We estimate that at a
25,000-tpy CO2e permitting threshold,
about 13,600 existing facilities would be
classified as ‘‘major sources’’ for their
PTE-based CO2e emissions. As
discussed later in this preamble, these
13,600 facilities present additional
workload demands on permitting
authorities, either because they are not
currently required to obtain a title V
permit (because their non-GHG
emissions fall below the ‘‘major source’’
threshold) or because, although they
already are required to obtain a title V
permit (due to their non-GHG
emissions), their permits would need to
be revised to cover their GHG emissions.
In contrast, at a 10,000-tpy CO2e
threshold the number of existing
facilities exceeding the threshold jumps
to almost 27,000. At a 50,000-tpy CO2e
threshold, the number of existing
facilities exceeding the threshold falls to
about 7,200. We believe, based on these
estimates, that a 25,000-tpy CO2e major
source threshold is appropriate because
it renders the title V program
administrable, albeit with additional
workload requirements. As discussed
later in this preamble, as we move
below the 25,000-tpy CO2e threshold,
we believe the administrative burdens
related to the increasing number of
facilities covered, as well as to the
variation in the type of facilities
covered, become insuperable. At both
32 ‘‘Technical Support Document for Greenhouse
Gas Emissions Thresholds Evaluation; Air Quality
Policy Division, Office of Air Quality Policy and
Standards; U.S. Environmental Protection Agency’’;
July 7, 2009.
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the 50,000- and 100,000-tpy CO2e
thresholds, however, we do not believe
that the potential level of permit activity
would fill the capacity of permitting
authorities to properly administer the
title V program, and similar to PSD
considerations, we believe it would
potentially exclude some high-emitting
facilities within key GHG source
categories.
Although we believe a 25,000-tpy
CO2e threshold would add an additional
permitting burden to permitting
authorities, we believe that this
additional burden could be adequately
administered. We expect that many of
the 13,600 existing facilities that would
exceed the proposed 25,000-tpy CO2e
threshold—the majority of which
consist of electric generating units and
industrial facilities—already have a title
V operating permit for other regulated
pollutants, and thus would potentially
require only a permit revision or
modification to address GHGs. We
believe that these permit revisions or
modifications under title V would
initially be limited due to the lack of
new applicable GHG requirements to
include in the permits, but would
increase in complexity and content as
facilities move through PSD permitting
processes and as other possible
stationary source requirements emerge.
In addition, with a 25,000-tpy CO2e
threshold, some of the 13,600 existing
facilities are not currently subject to title
V requirements and therefore would
require new title V permits. These
facilities constitute primarily additional
landfills (we estimate approximately
1,700 landfills may be added to the title
V program) and some large commercial
facilities, primarily large hospitals.
These facilities number approximately
800, but the number of new permits
they would need would be less than this
because approximately 180 are currently
subject to permitting under title V for
pollutants currently subject to
regulation under the Act. Permitting the
newly subject sources would not solely
involve GHG requirements but may also
involve other pollutants emitted by the
source.
We estimate that the combination of
title V permit revisions, modifications,
and new permits that would result from
a 25,000-tpy CO2e applicability
threshold would require an estimated
additional 492 FTEs by permitting
authorities nationwide, or an estimated
50-percent increase over current title V
staffing levels, to meet the initial
permitting requirements that would
apply at the time title V applicability is
triggered for GHG sources. We do not
believe this 50-percent increase in
resources would be administratively
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55335
impossible to achieve, given that title V
is self-funded, and that there are
efficiencies gained in revisiting existing
title V permits and sources with which
the permitting staff are familiar.
In contrast, at a 10,000-tpy CO2e
threshold, we estimate that an
additional 1,357 FTEs (an estimated
135-percent increase over current title V
staffing levels) would be required by
permitting agencies nationwide (again,
based on initial permitting
requirements). In addition, there would
be substantial influx of new title V
permits—greater than 13,000—that
would need to be processed and issued.
This would include over 7,000 newly
permitted commercial and residential
sources covering a wide variety of
source types, including office buildings,
retail malls, hotels, apartment buildings
and educational facilities. The new
variety of sources included at the lower
threshold also would require additional
training for permitting staff to become
familiar with the configuration and
emissions from those sources. For these
reasons, we believe that at threshold
levels below 25,000 tpy CO2e, even
considering the capability of permitting
authorities to eventually add additional
staff funded through permitting fees,
permitting authorities would not be
capable of ensuring reasonable
processing times for both new permits
and revisions resulting from the
additions of GHG emitters to the
program.
We request specific comment on our
estimated burden at the 25,000-tpy CO2e
major source threshold for title V and on
whether the additional workload would
be manageable to permitting authorities.
We also request specific comment on
our assessments of the impact of title V
major source GHG thresholds higher
and lower than 25,000 tpy CO2e on title
V program administration, including
any additional information on the
number of sources affected and the
permitting burdens created at these
thresholds. We further request comment
on our conclusion that the 10,000-tpy
threshold (or a lower threshold) would
be too low to address the administrative
necessity concerns, that the 25,000-tpy
threshold is administrable, and that
there is therefore no need to adopt a
threshold of 50,000 tpy.
There are additional policy and
programmatic considerations that, while
not part of the administrative-necessity
basis, also support establishing the
major source GHG threshold for title V
at 25,000 tpy CO2e. Most importantly,
this level would result in consistency
between the PSD and title V permitting
threshold for GHG sources. Historically,
there has been a strong measure of
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consistency in the PSD and title V
permitting levels since there is a
generally applicable 100-tpy ‘‘major
source’’ applicability threshold in title V
and there is a 100-tpy ‘‘major emitting
facility’’ applicability threshold applied
in PSD for sources in 28 key industrial
source classifications. In addition, there
is a strong programmatic incentive for
the programs to share a common
permitting threshold. Because at least
initially GHG requirements from the
PSD permitting process would
constitute the only applicable
requirements to be included in the title
V permits for many sources, a title V
permitting threshold lower than the PSD
threshold would create numerous
‘‘empty’’ or ‘‘hollow’’ permits, that is,
permits that do not include any
applicable requirements, and many
previously unpermitted commercial
sources would be required to obtain
these hollow permits. Permits hollow in
this respect may be viewed as
unnecessary and wasteful by the
permitting authorities and regulated
community. Further, requiring such
permits may be at tension with a
primary purpose of title V to promote
compliance and facilitate enforcement
by gathering into one document the
requirements that apply to a particular
source. See CAA Section 504(a) (each
title V permit must contain terms
‘‘necessary to assure compliance with
applicable requirements’’ of the CAA),
H.R. Rep. No. 101–490, at 351 (1990)
(‘‘It should be emphasized that the
operating permit to be issued under this
title is intended by the Administration
to be the single document or source of
all of the requirements under the Act
applicable to the source.’’).
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E. How will EPA assess the GHG
permitting thresholds in the first phase
of the tailoring program, and how will
EPA develop the second phase?
1. Assessment To Be Performed Within
5 Years Following Promulgation of the
First Phase
We consider the actions proposed in
this rulemaking to set higher GHG major
source applicability thresholds for PSD
and title V, and to establish a GHG PSD
significance level, as interim measures
that will need to be reassessed in terms
of their administrative necessity.
Therefore, as part of this proposed
action, we are committing to evaluate
the effectiveness of the first phase of the
tailoring program, which consists of the
proposed GHG thresholds, to enable
PSD and title V permitting authorities to
adequately administer their programs
with the inclusion of GHG emissions
sources. We are proposing to complete
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this evaluation within 5 years from the
effective date of this final rulemaking.
The results of this study will form the
basis for further regulatory action that
will constitute the second phase, which
may include continuing or lowering the
GHG applicability thresholds for PSD
and/or title V set in the first phase,
adoption of other streamlining
techniques that more accurately reflect
the administrative capabilities of
permitting authorities to address GHG
sources during the second phase, and/
or taking other actions consistent with
the goal of expeditiously meeting CAA
requirements in light of the
administrative burden that remains at
that time.
We believe a 5-year period is
necessary for the evaluation of the first
phase of the tailoring program to
provide an adequate period of time for
permitting authorities to implement the
proposed GHG permitting thresholds
and for a sufficient record of
implementation experience to be
compiled. We also believe a number of
important activities undertaken by EPA
and the States over the 5-year evaluation
period could potentially impact
permitting authorities’ administrative
capabilities to address GHG emissions
sources, and we need sufficient time to
implement those activities and assess
that impact. These activities will
include the following:
• The first activity is the development
of streamlining tools to specifically
address GHG sources. As discussed in
section VII.A of this preamble, several
permit streamlining techniques may
have applications for GHG emissions
sources. However, EPA needs an
estimated 3 to 4 years to fully develop
some of these techniques. Because many
of these techniques are source-specific,
or at least source category-specific—e.g.,
presumptive BACT determinations—
EPA may not be able to develop them
for all affected sources within the
evaluation period. However, we
anticipate that EPA may make sufficient
progress on enough streamlining
techniques to impact the administrative
capabilities of permitting authorities to
address GHG emissions sources.
• The second activity during the 5year period involves the ability of
permitting authorities to add more staff
to their permitting programs, especially
the title V program for which additional
fees for GHG emissions may support the
addition of new staff. Based on the
summary of State data on impacts of
GHG emissions permitting, it is likely
that even under the best-case scenarios,
at least a 3- to 4-year period is necessary
for most permitting authorities to add
and adequately train staff for permitting
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duties involving GHG emitters.
Therefore, we expect that the impact of
increased staffing on the administrative
capabilities of permitting authorities
will be better known by the fifth year of
the threshold evaluation period.
• The third activity is the collection
of more detailed emissions information
resulting from implementation of the
proposed GHG mandatory reporting
rule. Many permitting authorities have
not had any experience to date with
quantifying or evaluating emissions and
controls of GHG source categories.
EPA’s proposed GHG mandatory
reporting rule will produce significant
information about key GHG emissions
source categories that will help
permitting authorities and EPA better
understand the characteristics and
quantities of GHG emissions,
particularly at the facility level.
Reporting facilities will begin to submit
data in the year 2011, and we expect a
substantial record of emissions data to
be collected during the evaluation
period. We believe that these facilitylevel GHG data will be an important
component to increasing permitting staff
knowledge of GHG emissions sources
and will have a positive impact on the
permitting staff’s ability to address GHG
emissions in their programs. We also
believe this information will provide
additional insight into the level and
types of GHG emissions occurring at
different facility types that should
support EPA’s reevaluation of the first
phase GHG permitting thresholds.
• The fourth activity during the 5year assessment period is the
development of background information
on control technologies and costs for
GHG emissions source categories. As
discussed in more detail in section X of
this preamble, one of the administrative
constraints is the fact that permitting
authorities must apply BACT to GHG
sources subject to PSD, but that
endeavor would be highly resourceintensive. The 5-year assessment period
will allow EPA and the States to
develop information to evaluate GHG
control techniques and costs, which, in
turn, will be the basis for BACT
determinations involving GHG
emissions sources.
The 5-year period will serve other
purposes, too, including allowing EPA
to analyze the impacts of permitting
smaller GHG sources to develop
methods to mitigate those impacts. To
date, EPA has collected very little
information on the site-specific
configuration and GHG emissions
characteristics of many of the smaller
industrial and commercial source
categories. As a result, it is difficult to
fully assess the impact of GHG
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emissions permitting on these sources.
We believe the 5-year evaluation period
will provide EPA the opportunity to
develop a more comprehensive profile
of these smaller GHG source categories,
which will allow a better assessment of
the impacts on the small business
community and, in turn, ways to
mitigate those impacts.
Although we believe there are
sufficient reasons to justify a 5-year
evaluation period, we ask for comment
on whether the activities described
above—or at least some portion of them
sufficient to begin administering permit
programs for significant numbers of
sources below the proposed 25,000-tpy
CO2e threshold—could be accomplished
in a shorter time frame than our initial
estimates. For example, we ask for
comment on whether 3 years would be
a sufficient evaluation period. We are
especially interested in understanding
the basis for such an alternative time
period and what activities would need
to occur during the period.
We further note that, for the proposed
applicability thresholds as described
above, we did consider a step-down
approach for phasing in GHG permitting
thresholds for PSD and title V programs.
Under a step-down approach,
applicability thresholds for GHGs would
be lowered to predetermined step-down
levels at specified intervals, such as
every 2 years or more. However, we
rejected the step-down approach on the
basis that, without having established
sufficient information on source-specific
emissions and absent a record of
experience with permitting GHG
emissions sources on the part of
permitting authorities, we were not in
position to establish and support
specific step-down thresholds. We
believe that establishing further specific
step-downs prior to evaluating the
impact of the proposed GHG thresholds
included in this rulemaking, as well as
the impact of the proposed streamlining
techniques, would prematurely
determine what is administratively
feasible for permitting authorities to
undertake in terms of permitting GHG
sources. Nonetheless, in light of the
necessity of ultimately achieving
compliance with the statute, we solicit
comment on whether such an approach,
coupled with regular examination of
whether the administrative situation is
improving, is an appropriate way to
achieve compliance while taking into
account the administrative imperatives.
If so, we ask for suggestions on how we
could structure such an approach (e.g.,
when future phases should begin, how
we should determine the appropriate
thresholds for each phase, etc.)
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2. Rulemaking Based on Threshold
Evaluation for Second Phase of
Tailoring Program
We propose to commit, by rule, that
by 6 years after promulgation of the first
phase of the tailoring program, and
following completion of the threshold
evaluation study, we will promulgate a
follow-up rulemaking that will establish
the second phase of the program. This
rulemaking will either confirm the
continued use of the GHG permitting
thresholds implemented for the first
phase, or promulgate alternative GHG
permitting thresholds or other
streamlining techniques. The results of
the 5-year threshold evaluation study
will form the basis for determining what
thresholds or other techniques will be
promulgated in the second phase
rulemaking.
At this time, we cannot anticipate
specifically what the second phase of
this tailoring program will consist of.
The situation that we confront is
unprecedented. However, we believe
the process of establishing the first
phase and then assessing it, combined
with the development of other
streamlining techniques to the extent
possible, will provide a sufficient basis
for EPA to propose a rulemaking to
establish the second phase. Of course,
that rulemaking will provide ample
opportunity for affected parties to
comment on their experiences with the
administrative burden at current GHG
permitting thresholds and to make
recommendations for any changes in the
thresholds, for adoption of other
streamlining techniques, and/or for
actions consistent with the goal of
expeditiously meeting CAA
requirements in light of the
administrative burden that remains at
that time.
IX. What would be the economic
impacts of the proposed rule?
This section of the preamble examines
the economic impacts of the proposed
rule including the expected benefits and
costs of the proposed rule on affected
entities. This proposed rule lifts, for a
period of 6 years, the burden to obtain
a title V operating permit required by
the CAA for smaller sources of GHGs
and the burden of PSD requirements for
smaller new or modifying sources of
GHGs. Thus, this rule provides
regulatory relief rather than regulatory
requirements for these smaller GHG
sources for a period of 6 years. For
larger sources of GHGs, there are no
direct economic burdens or costs as a
result of this proposed rule, because
requirements to obtain a title V
operating permit or to adhere to PSD
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55337
requirements of the CAA are already
mandated by the Act and by existing
rules and are not imposed as a result of
this proposed rulemaking.
The regulatory impact analysis (RIA)
conducted for this proposed rule
provides details of the benefits or
regulatory relief that smaller GHG
sources will experience in terms of costs
avoided as a result of this proposed rule
and the potential for social costs in
terms of foregone environment benefits
during this 6-year period. Complete
details of the regulatory impact analysis
conducted for this proposed rule may be
found in the document ‘‘Regulatory
Impact Analysis for the Proposed
Greenhouse Gas Tailoring Rule,’’ in the
docket for this rulemaking.
This rulemaking provides permitting
thresholds for sources of GHGs that
exceed levels contained in the CAA.
Specifically, sources with the potential
to emit less than 25,000 tpy CO2e are
not required to obtain an operating
permit or PSD permit for a period of at
least 5 years at which time a study will
be conducted and the decision revisited
after 6 years. In the 6 years following
promulgation of this rule, the EPA
estimates that, compared to baseline
estimates that do not include the effects
of this rule, over six million sources of
GHG emissions will be allowed to
operate without a title V operating
permit and tens of thousands of new
sources or modifying sources per year
will not be subject to PSD requirements
for GHGs. For this large number of
smaller sources, this rule alleviates the
regulatory burden associated with
obtaining an operating or PSD permit or
complying with NSR BACT
requirements. Therefore, this proposed
action may be considered beneficial to
these small entities as it provides relief
from regulation that would otherwise be
required.
This decision does potentially have
environmental consequences in the
form of lesser emission reductions
during the 6-year period of time. Given
that sources between 250 and 25,000
tons per year account for an estimated
7 percent of the six directly emitted
GHGs nationally from industrial,
commercial, and residential source
categories, while representing over 95
percent of the total number of sources
potentially requiring an operating or
PSD permit for GHGs under current
permitting thresholds in the CAA, the
EPA believes this is a prudent decision.
Requiring such a large number of small
sources to obtain permits for the first
time would overtax the permitting
authorities’ abilities to process new
permits without commensurate benefits.
Moreover, as described in section VII.C
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of this preamble, reductions from these
small sources will still be occurring,
notwithstanding the fact that permitting
requirements would not apply to them.
These smaller sources of GHG will be
the focus of voluntary emission
reduction programs and energy
efficiency measures that lead to
reductions in GHGs. The EPA will also
reevaluate this decision after a 6-year
period and complete a study of the
implications of permitting smaller GHG
sources for those sources and permitting
authorities.
A. What entities are affected by this
rule?
As previously stated, this proposed
rule is essentially providing regulatory
relief and does not include direct
regulatory provisions for any industrial,
commercial, or residential entities. An
analysis is presented for smaller sources
expected to experience regulatory relief
from this rule. This proposal increases
the threshold to obtain a title V
operating permit to PTE levels of 25,000
tpy CO2e or greater annual emissions.
New sources of GHG emissions with the
potential to emit less than 25,000 tpy
CO2e that would otherwise be subject to
PSD are not required to obtain a PSD
permit or to comply with BACT
regulatory requirements as a result of
this proposed rule. The significance
levels for major modifications at sources
of GHG emissions are also increased in
this proposal allowing small sources to
forego obtaining a PSD permit and to
avoid BACT regulatory requirements,
when the projected emissions increase
from such modification is less than the
PSD significant level (with the
promulgated level to be selected from a
proposed range of values between
10,000 and 25,000 tpy CO2e). The
industry, agricultural, residential and
commercial categories anticipated to
experience regulatory relief are shown
in table IX–1. As table IX–1 shows, this
proposal lifts permitting requirements
for over six million potential title V
sources and tens of thousands of
potential PSD new sources that would
be otherwise required by the CAA to
obtain permits.
TABLE IX–1—ESTIMATED NUMBER OF AFFECTED SOURCES EXPERIENCING REGULATORY RELIEF*
Number of sources experiencing regulatory relief
Sector
Title V
New PSD
(annually)
Electricity ..........................................................................................................................................................................
Industrial ..........................................................................................................................................................................
Energy ..............................................................................................................................................................................
Waste Treatment .............................................................................................................................................................
Agriculture ........................................................................................................................................................................
Commercial ......................................................................................................................................................................
Residential—
Multifamily .................................................................................................................................................................
Residential—
Single Family ............................................................................................................................................................
161
156,545
3,644
1,431
37,351
1,354,760
20
303
35
0
299
12,034
610,340
6,397
3,925,000
515
Totals .................................................................................................................................................................
6,089,232
19,603
pwalker on DSK8KYBLC1PROD with PROPOSALS2
* Number of sources is determined on a potential to emit basis for small sources below 25,000 tpy CO2e threshold. Estimates for PSD sources
are for newly constructed facilities and do not include modifications at existing facilities that may also be subject to PSD requirements.
B. What are the estimated benefits to
small sources due to regulatory relief?
EPA estimated the benefits or avoided
costs for sources that are likely to
experience regulatory relief from this
proposal. This analysis focuses upon the
burdens that are being lifted for smaller
sources as a result of this proposed rule.
In addition, an accounting of the
benefits from this proposal as measured
by avoided costs for State, local, and
tribal permitting authorities is provided.
These avoided costs relate specifically
to information collection costs or
burden costs postponed for smaller
sources of GHG emissions otherwise
required to obtain an operating permit
under title V or required to modify an
existing permit to address GHG
emissions. Avoided costs shown also
include information collection
requirements for additional PSD permits
postponed for new or modifying smaller
sources of GHGs, as well as the avoided
costs to State, local and tribal permitting
authorities.
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1. What are estimated benefits or
avoided burden costs for title V permits?
Table IX–2 shows that the estimated
first-year information collection cost
avoided as a result of this proposal by
an industrial source required to obtain
a title V operating permit is
approximately $46.4 thousand (2007$)
per permit. The EPA estimates that over
195 thousand sources will avoid
incurring these permitting costs for a
period of at least 6 years as a result of
this proposal. The avoided burden cost
to obtain a new commercial or multifamily residential operating permit is
estimated to be approximately $5.0
thousand (2007$) per permit with over
5.9 million sources benefitting by not
incurring these costs due to this
proposed rule. In total, EPA estimates
that more than $38 billion (2007$) in
expenditures relating to title V
permitting will be avoided by small
sources of GHG for a period of 6 years
as a result of this proposal. Much of this
burden would have been incurred
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during the first year following the lightduty vehicle rule because sources have
1 year from the date of becoming subject
to title V. However, some ongoing
burden for new sources coming into the
program would be incurred each
subsequent year. State, local, and tribal
permitting authorities will also benefit
in terms of avoided permitting
administrative costs by over $15 billion
(2007$) as a result of the decisions
proposed in this action. This burden
would not all have been incurred during
the first year following the light-duty
vehicle rule, but much of it would
generally have been incurred within the
first 2 to 3 years. This is because under
the part 70 regulations, permitting
authorities are required to act on
applications within 18 months of
receipt. There would also be some
ongoing burden in each subsequent year
due to new sources coming into the
program.
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TABLE IX–2—REGULATORY RELIEF PROVIDED FOR SMALL GHG SOURCES AND PERMITTING AUTHORITIES
Small GHG sources not covered during
first phase < 25,000 tpy
Program/affected entities
Per-permit
cost
(2007$)
Source
Title V:
New Industrial ...................................................................................................................................
New Commercial/Residential ...........................................................................................................
Number of
permits
Total cost
(millions
2007$)
46,350
4,986
195,895
5,956,513
9,079.7
29,699.2
Subtotal Title V Permits ............................................................................................................
PSD Permits:
New Industrial ...................................................................................................................................
New Commercial/Residential ...........................................................................................................
....................
....................
38,778.9
84,530
16,887
3,299
37,197
278.9
628.1
Subtotal PSD Permits ...............................................................................................................
....................
....................
907.0
Total Source Costs ............................................................................................................
Permitting Authority
....................
....................
39,685.9
Title V:
New Industrial ...................................................................................................................................
New Commercial/Residential ...........................................................................................................
19,688
1,978
195,895
5,956,513
3,856.8
11,781.9
Subtotal Title V Permits ............................................................................................................
PSD Permits:
New Industrial ...................................................................................................................................
New Commercial/Residential ...........................................................................................................
....................
....................
15,638.7
23,243
4,633
3,299
37,197
76.7
172.3
Subtotal PSD permits ................................................................................................................
....................
....................
249.0
Total Permitting Authority Costs ........................................................................................
....................
....................
15,887.7
Total Source and Permitting Authority Costs ....................................................................
184.3
....................
55,573.6
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Notes: (1) Costs shown in ‘‘Sources Not Covered During First Phase’’ represent estimates of the regulatory burden relief proposed by this rule.
Title V operating permit costs represent one time costs, but these permits are subject to renewals every 5 years. New and modified PSD permits
reflect the estimated annual number of new and modifying sources requiring permits and the associated costs.
(2) Sums may not add due to rounding.
(3) All costs are shown in 2007 dollars.
2. What are avoided burden costs
associated with regulatory relief for
small PSD sources?
Table IX–2 summarizes the estimated
burden costs avoided by sources and
permitting authorities with this tailoring
rule. The estimated avoided burden or
reporting and recordkeeping cost
associated with requiring new industrial
sources to obtain permits is estimated to
be $84.5 thousand for new or modified
industrial sources and $16.9 thousand
for new or modified commercial or
multi-family residential sources (2007$).
This represents avoided annual costs of
over $900 million (2007$) for new and
modifying small sources of GHG. State,
local, and tribal permitting authorities
are expected to avoid $249 million
(2007$) annually in administrative
expenditures associated with
postponing PSD program requirements
for small GHG sources.
C. What are the economic impacts of
this rulemaking?
This proposed rulemaking does not
impose economic burdens or costs on
any sources or permitting authorities,
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but should be viewed as regulatory
relief for smaller GHG emission sources
and for permitting authorities. Although
sources above the thresholds proposed
in this rule will become subject to
permitting when the light-duty vehicle
rule is promulgated, those impacts are
not attributable to the present
rulemaking. Rather they are mandated
by the CAA and existing regulations and
automatically take effect independent of
this proposal.
In addition to considering the
regulatory relief expected for affected
entities as a result of this proposed rule,
the EPA considered the impact of this
rulemaking to small entities (small
businesses, governments and non-profit
organizations) as required by RFA and
SBREFA. For informational purposes,
the RIA includes the Small Business
Administration (SBA) definition of
small entities by industry categories for
stationary sources of GHGs and
potential regulatory relief from title V
and NSR permitting programs for small
sources of GHG. Since this rule does not
impose regulatory requirements but
rather lessens the regulatory burden of
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the CAA requirements to smaller
sources of GHGs, no economic costs are
imposed upon small sources of GHGs as
a result of this proposed rule. Rather
this proposal provides regulatory relief
for small sources. These avoided costs
or benefits accrue because small sources
of GHGs are not required to obtain a title
V permit and new or modifying small
sources of GHGs are not required to
meet PSD requirements for a period of
6 years. Some portion of the small
sources may be small entities, and these
entities will benefit from the regulatory
relief proposed in this rule.33
D. What are the costs of the proposed
rule for society?
EPA examined the social costs of this
proposed rule. These social costs
33 We note that some of the sources that remain
subject to permitting above the proposed threshold
in this rule may nonetheless be small businesses.
Elsewhere in this preamble, we discuss our intent
to convene a discretionary panel to examine the
small business impacts of GHG regulation through
PSD, although such impacts are not imposed as a
result of this proposed action. The RIA provides a
discussion of these impacts for informational
purposes.
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represent the foregone environmental
benefits that would occur if regulatory
relief were offered to small sources of
GHG emissions as proposed. This
proposal is one such regulatory relief
since it increases the emissions
thresholds for the title V and PSD
programs, as they apply to sources of
GHG emissions, to levels above those in
the CAA. In this preamble section, the
benefits or avoided regulatory costs of
such relief are discussed, but there is
also a social cost imposed by such relief
because this rule may forego some of the
possible benefits associated with title V
and PSD programs for sources of GHG
emissions below 25,000 tpy CO2e but
above the statutory 100/250 tpy levels.
These benefits are those attributed to
title V and PSD permitting programs in
general. These benefits are based upon
the relevance of these programs to
policymaking, transparency issues, and
market efficiency, and therefore are very
difficult to quantify and monetize. For
title V, they include the benefits of
improved compliance with CAA
requirements that stem from (1)
improved clarity regarding applicability
of requirements, (2) discovery and
required correction of noncompliance
prior to receiving a permit, (3)
improving monitoring, recordkeeping,
and reporting concerning compliance
status, (4) self-certification of
compliance with applicable
requirements initially and annually, and
prompt reporting of deviations from
permit requirements, (5) enhanced
opportunity for the public to understand
and monitor sources’ compliance
obligations, and (6) improved ability of
EPA, permitting authorities, and the
public to enforce CAA requirements.
However, it is important to remember
that a title V permit does not add new
requirements for pollution control itself,
but rather collects all of a facility’s
applicable requirements under the CAA
in one permit. Therefore, the
compliance benefits above are less when
title V permits contains few or no CAA
applicable requirements. During the first
phase under this proposal, when the
title V threshold is 25,000 tpy, we
expect that the vast majority of sources
excluded from title V would be sources
that have no CAA applicable
requirements for GHG emissions and
few or no requirements for other
pollutants because their emissions of
those pollutants are so small. For this
reason while it is extremely difficult to
measure the degree of improved
compliance, if any, that would be
foregone, or to quantify the social costs
that would be imposed, we expect that
they would be negligible.
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For PSD, the primary social cost
imposed by the tailoring rule stems from
the foregone benefit of applying BACT
to the tens of thousands of small new
sources and modifications that will be
below our proposed thresholds during
the first phase. This social cost
potentially weighs against the cost
savings described above that stem (in
part) from avoiding the administrative
and control costs of applying BACT to
these sources. The BACT requirement
assures that new and modified sources,
when they increase their emissions are
using state-of-the-art emission controls
and affords the public an opportunity to
comment on the control decision. It
does not prohibit increases but it
assures that such controls are applied.
Delaying the BACT requirement for
numerous small sources during the first
phase of this proposed rule could allow
increases from these smaller sources
that are greater than they would be if
BACT were applied. A detailed analysis
of this difference is beyond the scope of
this rule because we do not have
detailed information on the universe of
these tens of thousands of small PSD
actions, the candidate BACT
technologies for each of them, how
permitting authorities would make the
BACT decisions, and how the BACT
limit would compare to what would
otherwise be installed absent BACT.
It is not possible at this time to
quantify the social costs of avoided
BACT. However we note that the
universe of possible emissions that
would be regulated by sources excluded
under the tailoring rule is small
compared to those that would remain
subject to PSD. The sources excluded in
the first phase of this proposal comprise
only 7 percent of total stationary source
GHG emissions, while 68 percent
remain subject to regulation.
Furthermore, we expect the emissions
differences due to BACT controls for
such sources to be relatively small due
to the lack of available capture and
control technologies for GHG at such
sources that are akin to those that exist
for conventional pollutants and sources,
as well as the likelihood that even in the
absence of BACT such sources would
already be installing relatively efficient
GHG technologies to save on fuel costs.
Thus, while potential benefits would be
foregone by excluding smaller sources
from the permitting programs, these
benefits are likely to be small. Under the
tailoring rule, we will be working
during the 6-year period to greatly
improve our understanding of both the
administrative costs of regulating and
the social costs of not regulating smaller
sources under PSD and title V, and we
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will be relying on that information to
support our future threshold analyses
called for under the proposal.
In reaching the decisions for this GHG
tailoring rule, the EPA recognizes that
GHG emissions can remain in the
atmosphere for decades to centuries,
meaning that their concentrations
become well-mixed throughout the
global atmosphere regardless of
emission origin, and their effects on
climate are long lasting and significant.
A detailed explanation of climate
change and its impact on health,
society, and the environment is
included in EPA’s technical support
document for the endangerment finding
proposal (Docket ID No. EPA–HQ–
OAR–2009–0171). The EPA recognizes
the importance of reducing climate
change emissions for all sources of GHG
emissions including those sources
afforded regulatory relief in this rule
and plans to address potential emission
reductions from these small sources
using voluntary and energy efficiency
approaches. Elsewhere, we have
discussed EPA’s interest in continuing
to use regulatory and/or non-regulatory
tools for reducing emissions from
smaller GHG sources because we believe
that these tools will likely result in more
efficient and cost-effective regulation
than would case-by-case permitting.
X. What implementation issues are
related to this proposal?
In this action, EPA is proposing
certain steps to ensure that smaller
sources (meaning sources emitting
GHGs at lower rates) will not become
subject to PSD or title V upon EPA’s
completion of a rulemaking that
regulates GHG emissions. Absent those
steps, such a rule would trigger PSD and
title V for many of these smaller
sources. This is because both the CAA
PSD provisions and the title V
provisions are self-effectuating, that is,
they each apply by their terms to require
sources to undergo permitting
requirements. In addition, federally
approved State law provisions
implement both the CAA PSD
provisions and title V provisions. Those
State law provisions consist of the
various SIPs and State operating permit
programs, respectively. In order to limit
PSD and title V applicability to sources
that emit at or above the thresholds
proposed in this action, and to ensure
that these limits apply at the time a
rulemaking regulating GHG emissions is
promulgated—which will trigger PSD
and title V applicability—EPA is
proposing to establish threshold levels
on the basis that the administrative
necessity doctrine overlays the CAA
PSD and title V requirements, so that it
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is the proposed threshold levels, and
not the statutory threshold levels, that
apply to sources of GHG emissions.
Moreover, EPA is proposing a process,
consisting of several components, for
conforming the EPA-approved SIPs and
title V programs to reflect those
threshold levels. This section of the
preamble provides a detailed
description of this process, first for the
SIP PSD provisions, and then for the
title V State operating permit program
provisions.
A. CAA Provisions Concerning SIP
Requirements for PSD Programs, State
Submittal Requirements, and EPA
Action
Before describing EPA’s proposed
action for PSD SIP implementation, it is
useful to review the relevant
background concerning the CAA
requirements for what SIPs must
include, the process for State submittals
of SIPs, and requirements for EPA
action on SIPs and SIP revisions.
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1. SIP Requirements for State PSD
Programs and Adequate Resources
CAA section 110(a)(1) requires that
States adopt and submit to EPA for
approval SIPs that implement the
national ambient air quality standards.
CAA section 110(a)(2) contains a
detailed list of requirements that all
SIPs must include to be approvable by
EPA. Of particular relevance for this
action, subparagraph (J) of section
110(a)(2) of the CAA imposes the
requirement that the SIP must ‘‘meet the
applicable requirements of * * * part C
* * * (relating to prevention of
significant deterioration of air quality
* * *).’’ Under this provision, States
must submit SIPs or SIP revisions that
meet the federally mandated
requirements for PSD programs.
In addition, and also of particular
relevance for this action, subparagraph
(E)(i) of section 110(a)(2) of the CAA
provides that SIPs must ‘‘provide * * *
necessary assurances that the State
* * * will have adequate personnel
* * * [and] funding * * * to carry out
such implementation plan * * *.’’ As
applicable to PSD programs, this
provision means that EPA may approve
the SIP PSD provisions only if EPA is
satisfied that the State will have
adequate personnel and funding to
administer the PSD program, including
conducting the appropriate analyses for
new and existing sources, issuing the
permits, conducting enforcement, and
taking other necessary administrative
action.
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2. SIP Requirements for State
Submittals, EPA Action, and FIPs
As noted above, under CAA section
110(a)(1)–(2), States must submit for
EPA approval SIPs that meet the
requirements of section 110(a). If a State
does not submit a SIP or SIP revision as
required, EPA is authorized to make a
finding that the State has failed to make
a required SIP submittal, under CAA
section 179(a), and if EPA makes such
a finding, then, under CAA section
110(a)(2)(C), ‘‘[t]he Administrator shall
promulgate a Federal implementation
plan [(FIP)] at any time within 2 years
after’’ the date of the finding, unless the
State corrects the deficiency, and the
Administrator approves the plan or plan
revision.
After a SIP or SIP revision has been
submitted, EPA is authorized to act on
it under CAA section 110(k)(3)–(4).
Those provisions authorize a full
approval or, if the SIP or SIP revision
meets some but not all of the applicable
requirements, a conditional approval, a
partial approval and disapproval, or a
full disapproval. If EPA disapproves a
SIP or SIP revision, then EPA must
promulgate a FIP at any time within 2
years after the disapproval, unless the
State corrects the deficiency within that
period of time by submitting an
approvable SIP revision.34
Once EPA has approved a SIP, if EPA
determines that its action in doing so
was in error, then, under CAA section
110(k)(6), EPA may conduct a
rulemaking to correct the error without
requiring any further action, such as
submission of a request or a SIP
revision, from the State. Specifically,
section 110(k)(6) provides:
Whenever the Administrator determines
that the Administrator’s action approving,
disapproving, or promulgating any plan or
plan revision (or part thereof), area
designation, redesignation, classification, or
reclassification was in error, the
Administrator may in the same manner as the
approval, disapproval, or promulgation
revise such action as appropriate without
requiring any further submission from the
State. Such determination and the basis
thereof shall be provided to the State and
public.
EPA also has authority to revise its
previous action on a SIP through EPA’s
inherent authority, under CAA section
301(a), to reconsider prior rulemaking
actions, as well as under Administrative
Procedure Act (APA) section 553(e),
which requires EPA to give interested
persons ‘‘the right to petition for the
34 States are subject to sanctions for failure to
submit, or for EPA disapproval of, SIPs for
nonattainment areas, under CAA section 179. These
sanctions provisions are not relevant for this
proposal because they do not apply to PSD SIPs.
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issuance, amendment, or repeal of a
rule.’’
In addition, CAA section 110(k)(5)
gives EPA authority to issue what is
commonly called a ‘‘SIP Call’’ when
EPA determines that the SIP is
inadequate to meet CAA requirements.
The SIP Call notifies a State of the
inadequacies in its current SIP and
requires that the State submit a revised
SIP for EPA approval. Specifically,
section 110(k)(5) provides:
Whenever the Administrator finds that the
applicable implementation plan for any area
is substantially inadequate to [meet certain
section 110 requirements] or to otherwise
comply with any requirement of this Act, the
Administrator shall require the State to revise
the plan as necessary to correct such
inadequacies. The Administrator shall notify
the State of the inadequacies, and may
establish reasonable deadlines (not to exceed
18 months after the date of such notice) for
the submission of such plan revisions.
B. What PSD-specific implementation
considerations are there?
Three different requirements of the
CAA PSD provisions and the PSD SIPs
are at issue for this action. The SIPs vary
in certain ways with respect to these
requirements, so that EPA must take
different actions for different SIPs.
These three requirements concern the
threshold level for applicability, the
significance level, and the pollutants
subject to PSD. The first two—threshold
and significance levels—may be treated
similarly and are discussed immediately
below. The third is discussed after that.
1. Requirements for Thresholds and
Significance Levels in PSD Provisions
and PSD SIPs
a. EPA’s proposed action: Revision of
Federal regulations and limitation of
approval of SIPs.
As discussed elsewhere in this action,
the CAA PSD provisions apply to new
sources at or above 100/250-tpy
thresholds. CAA sections 165(a), 169(1).
These requirements are included in EPA
regulations in 40 CFR 52.21, which
indicate what States should include in
their SIPs. The CAA PSD provisions
apply to existing sources that modify
when those modifications increase
emissions by any amount, CAA section
165(a), 169(2)(C), 111(a)(4), unless EPA
promulgates higher levels—which we
term ‘‘significance levels’’—based on
reasons of de minimis emissions or
administrative necessity. Alabama
Power v. Costle, 636 F.2d 323 (D.C. Cir.
1980). This requirement is included in
EPA regulations in 40 CFR 52.21. Until
EPA acts to establish a significance level
for GHG emissions, the level in effect
remains at zero for any newly regulated
pollutants.
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Most jurisdictions are covered by
EPA-approved PSD SIPs. Based on a
review of these EPA-approved PSD SIPs,
virtually all of them establish the PSD
permitting threshold at the 100/250-tpy
level, although a few States have
adopted lower permitting threshold
levels. In addition, virtually all EPAapproved SIPs establish the significance
level for any new pollutants that it
covers—including GHG emissions, if
covered—at zero. Only a few EPA
approved SIPs take a slightly different
approach by adopting significance
levels at values other than zero and up
to the permitting thresholds. Some
jurisdictions are not covered by EPAapproved SIPs, and instead are covered
by EPA regulations at 40 CFR 52.21 that
EPA implements (in which case, the
EPA regulations act as a FIP) or that the
State implements through authority
delegated to it by EPA. For these States,
the PSD threshold level is 100/250 tpy
and the significance level for new
pollutants, including GHG emissions, is,
in effect, zero.
As discussed elsewhere, this action
proposes to establish the PSD thresholds
for GHG emissions at 25,000 tpy CO2e,
and proposes to establish the PSD
significance levels at [10,000–25,000]
tpy CO2e. EPA plans the following
process to revise its regulations and to
conform the EPA-approved SIPs to
reflect these levels.
First, with respect to EPA regulations,
EPA proposes to revise its regulations to
establish the permitting threshold at
25,000 tpy CO2e, at 40 CFR 52.21, and
to establish the significance level at
[10,000 to 25,000] tpy CO2e, at 40 CFR
52.21, based on the administrative
necessity doctrine discussed in section
VI.C of this preamble.
Second, with respect to the EPAapproved SIPs, although EPA previously
fully approved the permitting threshold
level provisions and the significance
level provisions in those SIPs, EPA
proposes to limit its approval of those
provisions in part. Specifically, EPA
proposes to limit its approval of (i) the
permitting threshold level provisions to
the extent those provisions require
permits for sources whose GHG
emissions equal or exceed the 100/250tpy CO2e levels but are less than 25,000
tpy CO2e for PSD thresholds; and (ii) of
the significance level provisions to the
extent those provisions apply to GHG
emissions less than [10,000 to 25,000]
tpy CO2e. As discussed below, EPA’s
authority for these limitations of
approval is based on its authority under
CAA section 301(a), which incorporates
the inherent authority of an agency to
reconsider its actions, as well as under
APA section 553. Even so, EPA is also
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proposing, in the alternative, to limit its
approval through the error correction
provisions of CAA section 110(k)(6).
EPA does not propose to take any
further action on the permitting
threshold or significance level
provisions for which EPA is limiting its
approval; that is, EPA is not proposing
to disapprove those provisions. Thus,
the limitation of approval for those
provisions does not trigger an obligation
on the part of the State to revise and
resubmit for approval the affected PSD
SIP provisions and does not trigger a FIP
obligation.
The permitting threshold PSD SIP
provisions that apply to sources with
GHG emissions at 25,000 tpy CO2e or
higher, and the significance level
provisions that apply to sources with
GHG emissions at [10,000 to 25,000] tpy
CO2e or higher, remain fully approved.
As a drafting matter, EPA proposes to
accomplish the limitations of approval
by adding to the record of its action on
each SIP, as found in the subparts to 40
CFR 51.21, the boilerplate statements
that (i) EPA limits its approval of the
PSD permitting threshold provisions to
the extent those provisions require
permits for sources of GHG emissions
that equal or exceed 100 tpy CO2e for
sources in the 28 categories identified in
CAA section 169(1), and 250 tpy CO2e
for all other sources, but that are less
than 25,000 tpy CO2e; and (ii) EPA
limits its approval of the PSD
significance level provisions to the
extent those provisions treat as
significant GHG emissions increases
that are less than [10,000 to 25,000] tpy
CO2e.
b. Authority for limitation of
approval.
EPA is limiting its approval through
its authority under CAA section 301(a)
‘‘to prescribe such regulations as are
necessary to carry out [EPA’s]
functions’’ under the CAA. This
provision confers general regulatory
authority upon the Administrator, and
incorporates the Agency’s inherent
authority to reconsider prior rulemaking
actions. Additional authority for EPA to
limit its approval is found in APA
section 553(e), which requires EPA to
give interested persons ‘‘the right to
petition for the issuance, amendment, or
repeal of a rule.’’
An administrative agency has the
inherent authority to reconsider its
decisions, unless Congress specifically
proscribes the agency’s discretion to do
so. The D.C. Circuit recently affirmed
this authority in New Jersey v. EPA, 517
F.3d 574 (D.C. Cir. 2008), where it
explained that an agency normally can
change its position and reverse a prior
decision but that in the case before it,
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Congress limited EPA’s ability to
remove sources from the list of HAP
source categories, once listed, by
requiring EPA to follow the specific
delisting process at CAA section
112(c)(9). See, e.g., Gun South, Inc. v.
Brady, 877 F.2d 858, 862 (11th Cir.
1989) (holding that agencies have
implied authority to reconsider and
rectify errors even though the applicable
statute and regulations do not provide
expressly for such reconsideration);
Trujillo v. General Electric Co., 621 F.2d
1084, 1086 (10th Cir. 1980)
(‘‘Administrative agencies have an
inherent authority to reconsider their
own decisions, since the power to
decide in the first instance carries with
it the power to reconsider’’). CAA
section 307(b)(1), a judicial review
provision that applies to all SIP actions,
provides some confirmation because it
expressly contemplates the ‘‘filing of a
petition of reconsideration by the
Administrator of any otherwise final
rule or action.’’
EPA recently applied this approach in
connection with California conformity
SIPs. EPA had approved the SIPs based
on a mobile source model that was
current at the time of EPA’s approval.
EPA proceeded to update the mobile
source model, but under the previous
SIP approvals, conformity decisions
would continue to be made on the basis
of those previous SIP approvals, and
would not take into account the updates
to the mobile source model. To rectify
this problem, EPA conducted a
rulemaking that revised the previous
SIP approvals so that they were limited
to the period before States submitted,
and EPA found adequate, the mobile
source budgets in new SIPs based upon
the update of the mobile source model.
Similarly, in this action, EPA is
proposing to limit its previous approval
to, in effect, a portion of the State PSD
program, which is the permitting
requirements that apply to sources of
GHG emissions at or above 25,000 tpy
CO2e (for permitting thresholds) and
[10,000 to 25,000] tpy CO2e (for
significance levels), respectively. The
reason is that in light of the requirement
under CAA section 110(a)(2)(E) that
SIPs provide necessary assurances of
adequate personnel and funding, the
previous approvals of the PSD programs
were overly broad. Specifically, EPA
approved PSD programs that applied to
all sources of regulated NSR pollutants
above the 100/250-tpy statutory levels.
At the time of the EPA approvals, the
sources emitting the pollutants covered
by the PSD programs, so approved, may
have been in sufficiently limited
numbers so that State resources were
adequate to fully administer the PSD
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program. However, the breadth of the
applicability requirements that EPA
approved meant that if new pollutants
were regulated in the future, and if
those new pollutants were emitted at
the levels of 100/250 tpy or higher by
large numbers of sources, then the
States’ PSD programs would become
much larger and State resources
accordingly will not be adequate to
administer the program. The SIP failed
to provide necessary assurances that the
State would have sufficient personnel
and funding to cover this possible
expansion of the PSD program. In fact,
those events are unfolding now: EPA is
in the process of regulating GHG
emissions and thereby triggering PSD
applicability for GHG sources, and, at
the applicability levels in the SIPs, State
PSD programs will become too large for
States to administer with their current
levels of personnel and funding. For
these reasons, EPA is limiting its
previous approvals, as described above.
c. Proposed alternative action: Error
correction.
EPA is also proposing in the
alternative to revise its approval of the
SIP threshold and significance level
provisions through a CAA section
110(k)(6) error correction. As noted
above, CAA section 110(k)(6) authorizes
EPA to correct its actions concerning
SIPs and certain other actions through a
simplified procedure. For the reasons
described immediately above, EPA
believes that the SIPs did not provide
the necessary assurances, as required
under CAA section 110(a)(2)(E), that the
permitting authorities would have
personnel and funding adequate to
implement the extensive SIP PSD
programs that could result from the
broadly applicable PSD threshold
provisions and significance level
provisions as approved. Therefore,
under this alternative proposal, EPA
erred in approving those provisions.
Rather, EPA should have approved
those provisions only in part, and not
taken action on the rest of the
provisions.
As a result, EPA proposes to correct
those errors, under the authority of CAA
section 110(k)(6), by limiting its
approval of the PSD threshold
provisions to the extent they apply PSD
requirements to sources of GHG
emissions between 100/250 tpy CO2e
and 25,000 tpy CO2e, and the PSD
significance level provisions to the
extent they apply to sources that emit
GHGs at a rate below [10,000 to 25,000]
tpy CO2e. In accordance with CAA
section 110(k)(6), EPA is proposing to
conduct its limitation of approval
through notice-and-comment
rulemaking under APA section 553,
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which is ‘‘the same manner as [EPA
conducted] the approval,’’ and EPA is
not requiring any further submission
from the State.
d. State response.
For purposes of the federally
approved SIP, this proposed action does
not require States to submit any SIP
revision. That is, if EPA finalizes this
proposal, each federally approved PSD
program will have a PSD threshold level
for GHG emissions of 25,000 tpy CO2e
and a significance levels for GHG
emissions of [10,000 to 25,000] tpy
CO2e; and although each State PSD
program—as established by the State
law provisions that comprise the SIP—
will have a lower threshold and
significance level, those lower levels
will not be federally approved and
therefore not federally enforceable. To
reiterate, EPA is not proposing to
disapprove those provisions; rather,
EPA will take no further action with
respect to them. As a result, no further
action by the State, including no SIP
revision, is necessary for Federal
purposes.
Even so, it should be noted that the
lower thresholds remain on the books
under State law, and sources therefore
remain subject to them as a matter of
State law. As a result, States may wish
to consider revising those State law
provisions. In addition, the fact that
these provisions remain on the books
under State law may create some
confusion as to whether they are part of
the federally approved SIP (again, with
this proposed action, they would not
be), and for this purpose too of avoiding
this confusion, States may wish to
consider revising those State law
provisions.
On the other hand, if a State wants to
implement PSD permitting requirements
at a threshold level lower than 25,000
tpy CO2e, or implement a significance
level lower than [10,000 to 25,000] tpy
CO2e, for GHG emitters, the State may
submit a SIP revision that identifies the
lower thresholds and provides the
necessary assurances, under CAA
section 110(a)(2)(E), that it has adequate
personnel and funding to permit at this
level. If the SIP revision meets the CAA
section 110(a)(2)(E) requirement, EPA
will proceed to approve it. Permitting
for this State would then cover such
smaller sources. For reasons described
elsewhere in this notice, the EPA has
determined based on its national
analysis that, absent additional
streamlining measures, the PSD program
will initially be impossible to
implement at such lower levels. A State
seeking to adopt lower levels should
therefore be prepared to describe in its
submittal the administrative burden that
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will be added at the proposed lower
levels, and the measures it will take to
make the program implementable at
those levels.
It should be noted that EPA
considered, but is not proposing or
soliciting comment on, issuing a SIP call
under CAA section 110(k)(5) to require
States to either demonstrate that they
have adequate personnel and funding to
administer their PSD programs at the
100/250-tpy CO2e threshold level for
GHG emitters, or to submit a SIP
revision that raises the threshold to
25,000 tpy CO2e or some other level
commensurate with their personnel and
funding. EPA decided against this
approach for several reasons. First, a SIP
call under section 110(k)(5) takes
significantly more time than actions
taken under EPA’s other authorities. For
a SIP call, EPA first undertakes a noticeand-comment process in order to make
the finding that a SIP is inadequate and
to set a schedule for a new SIP
submission by a State (which can be up
to 18 months after EPA’s
determination). Then, EPA must
provide notice and opportunity for
comment regarding whether or not the
Agency should approve the SIP revision
submitted by a State in response to the
SIP call. By contrast, the reconsideration
of a SIP approval can be undertaken in
much less time. Reconsideration of a
SIP approval may lead to a more speedy
and efficient resolution in a situation
(such as the present) where there is no
need for a further SIP submission to be
developed and submitted to EPA by the
State.
2. PSD SIP Provisions Identifying the
Pollutants
A handful of EPA-approved SIPs fail
to include provisions that would subject
GHG emissions to their PSD
requirements when EPA promulgates
regulations that regulate GHGs and
thereby trigger the applicability of PSD.
For these SIPs, EPA intends to take
separate regulatory action, as discussed
in this section of this preamble.
a. Regulatory background.
By way of background, in 1978, after
Congress enacted the PSD program in
the 1977 CAA Amendments, EPA
promulgated a rulemaking to implement
the program. 43 FR 26380 (June 19,
1978). This rulemaking required that the
PSD program apply to ‘‘each pollutant
subject to regulation’’ under the CAA.
Id. at 26403, 26406 (promulgating 40
CFR 51.21(b)(1)(i)).35 In 2002, EPA
35 After challenges by industry and
environmental organizations, parts of this
rulemaking were remanded by the D.C. Circuit in
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promulgated a rulemaking that revised
parts of the PSD and nonattainment
NSR programs, which is generally
known as the ‘‘NSR Reform’’
rulemaking, and there, EPA revised this
terminology so that PSD requirements
apply to ‘‘regulated NSR pollutants.’’ 67
FR 80186 (Dec. 31, 2002); see 40 CFR
52.21(b)(50).
After the 1978 rulemaking, most
States submitted SIPs with provisions
that incorporated the requirement to
apply PSD requirements to ‘‘each
pollutant subject to regulation,’’ or used
comparable terminology, and EPA
approved those provisions. Following
the 2002 NSR Reform rule, many,
although not all, of these States
submitted SIPs that EPA has approved
and that have replaced that terminology
with the requirement that PSD
requirements apply to ‘‘NSR regulated
pollutants.’’
However, a few SIPs do not have
provisions that apply the PSD
requirements to ‘‘regulated NSR
pollutants’’ or ‘‘pollutants subject to
regulation’’ under the CAA, or use
comparable terminology. Rather, these
SIPs specifically list the pollutants to
which the PSD programs apply, and do
not include GHGs.
b. EPA’s plan of separate regulatory
action.
It is EPA’s understanding that each of
the SIPs that cover either ‘‘NSR
regulated pollutants’’ or ‘‘pollutants
subject to regulation’’ under the CAA, or
that use comparable terminology, will
apply the PSD requirements to sources
that emit GHGs, at the appropriate
threshold levels, when EPA promulgates
rules regulating GHGs and thereby
triggering PSD requirements. This is
because these SIP provisions employ
broad enough terminology to encompass
newly regulated pollutants, such as
GHGs.36 As a result, for these SIPs, no
Alabama Power v. Costle, 636 F.2d 323 (D.C. Cir.
1980), and EPA promulgated revised requirements
in 1980. 45 FR 52676 (August 7, 1980). The
requirement that the PSD program apply to ‘‘each
pollutant subject to regulation’’ under the Act was
not at issue in Alabama Power and was not revised
in the rule revisions that followed that decision.
36 It should be noted that if any State with these
SIP provisions interprets their provisions to cover
only pollutants regulated (or subject to regulation)
at the time of SIP submission or approval, so that
the provisions would not cover GHG emissions,
then the State should so indicate during the
comment period. EPA will take steps to resolve the
proper interpretation of the provision. EPA
proposes in this action that if EPA agrees that the
SIP provision cannot be interpreted to cover sources
of GHG emissions, then EPA will treat the State in
the same manner as States that specifically list
pollutants as subject to PSD requirements and do
not include GHGs, as discussed below.
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further action by EPA in this proposal
is necessary.37
However, the story is different for the
few SIPs that do not have provisions
that apply the PSD requirements to
‘‘regulated NSR pollutants’’ or
‘‘pollutants subject to regulation’’ under
the CAA, and that instead specifically
list the pollutants to which the PSD
programs apply, and do not include
GHGs. Although EPA approved them,
these SIPs were, and remain, deficient
because by subjecting to the PSD
requirements only the pollutants
specifically listed, they fail to reflect the
EPA’s longstanding requirements that
PSD requirements apply to all
pollutants subject to regulation under
the CAA, which necessarily includes
any newly regulated pollutants beyond
those specifically listed.
Importantly, for present purposes,
these SIPs do not require that GHG
emitters obtain PSD permits. However,
CAA section 165(a), by its terms,
prohibits a source that is subject to PSD
from constructing or modifying without
a permit. As noted elsewhere, as a result
of the proposed light-duty vehicle rule,
expected to be promulgated at the end
of March 2010, sources of GHG
emissions in those States will be subject
to the requirement of CAA section
165(a) to obtain a preconstruction PSD
permit.
EPA recognizes the problems that
arise from this situation. Accordingly,
EPA intends a separate regulatory action
in the very near future that will identify
the SIPs in question and address them.
EPA expects this regulatory action to be
completed and to take effect by the time
EPA promulgates the light-duty vehicle
rule at the end of March 2010.
C. What title V-specific implementation
issues are there?
Some of the title V-specific
implementation issues parallel the PSD
SIP implementation issues. Thus, the
process EPA is proposing, described
below, to conform the EPA-approved
title V programs to reflect the title V
applicability threshold level for GHG
emissions of 25,000 tpy CO2e parallels
in certain respects the process described
above for conforming the EPA-approved
SIP PSD programs.
37 It should be noted that in this action, EPA is
not addressing in any way any other issue that may
arise concerning any of these States that do not
have approved PSD programs incorporating all of
the requirements of the NSR Reform rule.
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1. CAA Provisions Concerning Title V
Requirements for State Programs, State
Submittal Requirements, and EPA
Action
Before describing EPA’s proposed
action for title V implementation, it is
useful to review the relevant
background concerning the CAA
requirements for title V State operating
permit programs, State submittals of
those programs, and EPA action on State
title V programs.
a. CAA requirements under title V for
State permitting programs.
CAA section 502(d)(1) requires that
each State adopt and submit to EPA for
approval an operating permit program
under State or local law that meets the
requirements of title V. CAA section
502(b) contains a detailed list of
requirements that all State permit
programs must include to be approvable
by EPA. Of particular relevance for this
action, paragraph (4) of section 502(b)
provides that the permit program must
include ‘‘[r]equirements for adequate
personnel and funding to administer the
program.’’ This provision means that
EPA may approve the State permit
program only if EPA is satisfied that the
State will have adequate personnel and
funding to administer the program,
including issuing the permits,
conducting enforcement, and taking
other necessary administrative action.
b. State permit program submittal
requirements and Federal plans.
As noted above, under CAA section
502(d), States must submit for EPA
approval State permit programs that
meet the requirements of CAA section
502(b). If a State does not submit a
permit program as required, or if EPA
disapproves a program submitted, in
whole or in part, then the Administrator
‘‘shall, 2 years after the date required for
submission of such a program * * *,
promulgate, administer, and enforce a
[title V] program * * * for that State,’’
under CAA section 502(d)(3).38
c. EPA action on, and revision of
action for, State permit programs.
After a State permit program has been
submitted, EPA must approve or
disapprove it in whole or in part. CAA
section 502(d)(1). Those provisions
authorize EPA to approve the program
to the extent that it meets the
requirements of title V.
38 In addition, if EPA disapproves a title V
program due to failures by the State concerning an
area in the State and air pollutants for which that
area is in nonattainment, then mandatory sanctions
apply, under CAA section 502(d)(2)(B)–(C).
Sanctions regarding offsets would not be relevant
for purposes of this action because GHGs are not
criteria air pollutants under CAA section 108(a) and
no areas are designated nonattainment for them.
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Once EPA has approved a permit
program, EPA retains the authority to
revise its action through its inherent
authority to reconsider prior rulemaking
actions, as well as under APA section
553(e), which requires EPA to give
interested persons ‘‘the right to petition
for the issuance, amendment, or repeal
of a rule.’’ 39
In addition, CAA section 502(i)(1)
gives EPA authority to issue what is
commonly called a ‘‘notice of
deficiency’’ (NOD) when EPA
determines that the permitting authority
‘‘is not adequately administering and
enforcing a program, or portion
thereof.’’ The NOD notifies a State of the
inadequacies in its current permit
program and requires that EPA
promulgate, administer, and enforce a
permit program under title V within 2
years after issuing the notice unless the
State has corrected the deficiency,
under section 502(i)(4). See also CAA
sections 502(i)(2)–(3) regarding
sanctions.
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2. What title V-specific implementation
considerations are there?
Two different requirements of the
CAA title V permit programs are at issue
for this action. The permit programs are
similar with respect to these
requirements, so that EPA’s action is the
same for each of the permit programs.
These two requirements concern the
threshold level for applicability and the
pollutants subject to title V permitting
requirements.
a. Requirements for threshold level in
title V Federal regulatory provisions and
title V State plans.
(i) EPA’s proposed action: Revision of
Federal regulations and limitation of
approval of SIPs.
As discussed elsewhere in this action,
the CAA title V requirements, as
interpreted by EPA, generally apply to
existing sources that emit 100 tpy or
more of any air pollutant.40 CAA
sections 502(a), 501(2)(B). These
requirements are included in EPA
regulations in 40 CFR 70.3.
Most jurisdictions are covered by
EPA-approved State title V permit
programs. It appears that each EPAapproved title V permit program
establishes the permitting threshold at,
in general, 100 tpy. Some jurisdictions
are not covered by EPA-approved State
39 Title V does not include a provision for an error
correction that is comparable to CAA section
110(k)(6), which concerns SIPs.
40 Title V requirements also apply to sources
defined as major sources under CAA section 112 on
the basis of their emissions of HAP, and these
sources may be covered by title V even though they
emit less than the 100-tpy threshold that generally
applies.
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programs, and instead are covered by
regulations at 40 CFR 71 that EPA
implements. For these jurisdictions, the
PSD threshold level is 100 tpy.
As discussed elsewhere, in this
action, EPA proposes to establish the
title V permitting threshold for GHG
emissions at 25,000 tpy CO2e. EPA
plans the following process to revise its
regulations and to conform the EPAapproved State title V programs to
reflect these levels. This action parallels
EPA’s action to revise its PSD
regulations and conform the EPAapproved State PSD programs to the
revised PSD regulations, discussed
above. First, with respect to its EPA
regulations, EPA proposes to revise its
regulations to establish the permitting
threshold for GHGs at 25,000 tpy CO2e,
at 40 CFR 70.2. Second, with respect to
the EPA-approved State permitting
programs, although EPA previously
fully approved the permitting threshold
level provisions in those programs, EPA
proposes to limit its approval of the
permitting threshold level provisions to
the extent those provisions require
permits for sources whose emissions of
GHGs equal or exceed 100 tpy CO2e but
are less than 25,000 tpy CO2e. EPA’s
authority for this limitation of approval
is based on CAA section 301(a), which
incorporates the inherent authority of an
agency to reconsider its actions, as well
as on APA section 553.
EPA does not propose to take any
further action on the permitting
threshold provisions for which EPA is
limiting its approval; that is, EPA is not
proposing to disapprove those
provisions. Thus, the limitation of
approval for those provisions does not
trigger an obligation on the part of the
State to revise and resubmit for approval
the affected permitting program
provisions and does not trigger any
Federal plan obligation.
The State permitting threshold
provisions that apply to sources with
GHG emissions at 25,000 tpy CO2e or
higher remain fully approved.
As a drafting matter, EPA proposes to
accomplish the limitations of approval
by adding to the record of its action on
each State permit program the
boilerplate statement that EPA limits its
approval of the State permitting
threshold provisions to the extent those
provisions require permits for sources of
GHG emissions that equal or exceed 100
tpy CO2e but that are less than 25,000
tpy CO2e.
(ii) Authority for limitation of
approval.
As with its action concerning the PSD
program, discussed above, EPA is
limiting its approval under CAA section
301(a), which reflects its inherent
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authority to reconsider prior rulemaking
actions, as well as under APA section
553(e). This authority is described in
detail above in connection with EPA’s
proposed parallel action concerning
PSD SIP provisions.
(iii) State response.
For purposes of the federally
approved State permit program, this
proposed action does not require States
to submit any revision or take any
further action. That is, if EPA finalizes
this proposal, each federally approved
title V program will have an
applicability threshold level of 25,000
tpy CO2e. Although the State permitting
program—as established by the State
law provisions—may have a lower
threshold, that lower level will not be
federally approved and will therefore
not be federally enforceable. To
reiterate, EPA is not proposing to
disapprove those provisions; rather,
EPA will take no further action with
respect to them. As a result, no further
action by the State, including no
program revision, is necessary for
Federal purposes.
Even so, the lower thresholds remain
on the books under State law, and
sources therefore remain subject to them
as a matter of State law. As a result,
States may wish to consider revising
those state law provisions. In addition,
the fact that these provisions remain on
the books under State law may create
some confusion as to whether they are
part of the federally approved title V
program (again, with this proposed
action, they would not be), and for this
purpose too of avoiding this confusion,
States may wish to consider revising
those state law provisions.
On the other hand, if a state wants to
implement its operating permit
requirements at a threshold level lower
than 25,000 tpy CO2e for GHG emitters,
the state may submit an operating
permit program revision that identifies
the lower thresholds and provides the
necessary assurances, under CAA
section 502(b)(4), that it has adequate
personnel and funding. If the program
revision meets the CAA section
502(b)(4) requirement, EPA will proceed
to approve it.
It should be noted that EPA
considered, but is not proposing or
soliciting comment on, issuing a NOD
under CAA section 502(i)(1) to require
States to either demonstrate that they
have adequate personnel and funding to
administer their operating permit
programs at the 100-tpy CO2e threshold
level for GHG emitters, or to submit a
permit program revision that raises the
threshold to 25,000 tpy CO2e or some
other level commensurate with state
personnel and funding. EPA decided
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against this approach for several
reasons. First, a NOD under section
502(i)(1) takes significantly more time
than actions taken under EPA’s other
authorities. The first step in this process
is publication of a NOD in the Federal
Register that sets forth EPA’s findings as
to the deficiencies in the state program.
This notice requires the state to take
significant action within 90 days, and
identifies several actions, such as
program withdrawal and
implementation of a Federal permitting
program, that EPA may take if
significant action is not taken by the
state. If the state has not corrected the
deficiency within 18 months after the
finding described above, EPA will
promulgate, administer and enforce a
Federal program within 2 years of the
finding. In contrast, the reconsideration
of a permit program approval can be
undertaken in much less time.
Reconsideration of a permit program
approval may lead to a more speedy and
efficient resolution in a situation (such
as the present) where there is no need
for a further permit program submission
to be developed and submitted to EPA
by the state.
b. Requirement that title V permit
programs apply to any air pollutant.
It appears that most title V-approved
state permit programs apply to 100-tpyor-more sources of any pollutant. As
discussed elsewhere, EPA interprets
these provisions to cover only
pollutants that are actually regulated
under other CAA provisions. These title
V programs will include sources of GHG
emissions when EPA promulgates
regulations for GHG emissions, which
EPA expects at the end of March 2010.
For those title V programs, no further
action concerning these provisions is
needed.
However, EPA believes that some title
V programs may apply to 100-tpy-ormore sources of only pollutants
specifically identified in the program
provisions and that these title V
programs do not include a provision
that automatically updates title V
applicability to include any new
pollutant for which EPA promulgates
controls. Thus, these title V programs
would not include GHG emitters. These
programs are similar, for title V
purposes, to the SIPs described above
that specifically list pollutants subject to
PSD that do not include a provision that
automatically updates PSD applicability
to include any new pollutant for which
EPA promulgates controls. Thus, these
title V programs carry the same
deficiency that the SIPs do. As with the
SIPs, EPA intends to undertake separate
regulatory action in the near future to
address these title V programs, which
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EPA intends to be completed and take
effect by the end of March 2010, when
EPA promulgates the light-duty vehicle
rule that triggers title V applicability for
sources of GHG emissions.
D. GHGs and Title V Permit Fees
Under title V, section 502(b)(3) of the
Act, permitting authorities (including
State and local agencies, tribes, and
EPA) are required to collect fees
‘‘sufficient to cover all reasonable
(direct and indirect) costs required to
develop and administer the permit
program requirements.’’ The final part
70 rule grants States wide discretion in
collecting fees from individual sources
through establishment of fee schedules
in their permit programs, provided the
total fees collected from all sources are
sufficient to cover the title V costs. See
§ 70.9(a), and § 70.9(b)(1) and (b)(3). The
initial permit program submittal to EPA
is required to include a demonstration
that the fee schedule will be sufficient
to cover the program costs and an
estimate of the program cost during the
early years of implementation. See
§ 70.4(b)(7) and (8). Also, at any time,
EPA may require States to provide a
detailed accounting of fee schedule
adequacy, including when serious
questions are raised about adequacy.
See § 70.9(b)(5) and § 70.9(c). Thus, title
V and part 70 place primary
responsibility on the permitting
authorities to raise adequate fees and on
EPA to perform oversight of this
responsibility.
The activities related to regulation of
GHGs that would increase permitting
authority workloads can be grouped into
the following two categories: (1)
Changing existing permits to add any
necessary provisions to address GHGs,
and (2) issuing new permits to sources
newly subject to permitting solely
because their regulated GHGs exceed
the major source threshold.
Thus, we need to consider the impact
of this proposal and any future
regulation of GHGs on the fee
requirements of the permit programs,
and if any revisions are needed to parts
70 and 71 in response to ensure
collection of adequate fees to fund the
permit programs.
1. How are the fee rates set in the permit
programs?
The part 70 rule provided a shortcut
to ease the level of detail otherwise
required in States’ fee adequacy
demonstrations by providing a
‘‘presumptive minimum fee,’’ which
was specified in section 502(b)(3)(B) of
the Act. The final part 70 rule provides
a rebuttable presumption that the fees
charged by a state are sufficient to cover
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program costs if they collect an amount
equal to or greater than the presumptive
minimum fee multiplied by the actual
tons of ‘‘regulated pollutants (for
presumptive fee calculation),’’ as
defined in § 70.2. The part 70
presumptive fee was initially set at $25/
ton. This amount is adjusted for
inflation, annually. See § 70.9(b)(2). The
current presumptive minimum fee,
effective through September 2009, is
$43.75. EPA calculates the inflationadjusted part 70 presumptive minimum
fee in October of each year and places
a memorandum announcing the fee on
a Web site it maintains for this purpose.
See https://www.epa.gov/air/oaqps/
permits/fees.html. Also, EPA notes that
it believes there are currently a minority
of States that base their fees on the
presumptive minimum, perhaps at most
17 out of 112 State and local part 70
permits programs.
Since the use of the presumptive
minimum fee is not mandatory for
States, States were free to set either
lower or higher fees rates, based on a
more detailed fee adequacy
demonstration. See § 70.9(b)(5). States
were not required to set emissions-based
fees though most did in combination
with other approaches. Emissions-based
fees on state fee schedules range from
less than $10 per ton in a rural State to
over $100 ton in a large urban area.
Examples of other fee schedule
approaches include processing fees,
such as fees for applications, renewals
and modifications, charges for time and
material, and fees that vary depending
on source category, equipment types,
regulated air pollutant, business size,
and many other factors. See § 71.9(b)(3).
The part 71 permit program,
administered by EPA and delegate
agencies, charges a ‘‘part 71 annual fee,’’
for every actual ton of ‘‘regulated air
pollutant (for fee calculation),’’ as
defined in § 71.2. Also see fee schedule
at § 71.9(c). The final rule for part 71 set
this rate at $32/ton. Adjusted for
inflation, the part 71 annual fee through
calendar year 2009 is $45.25 per ton.
The final rule based the $32/ton fee on
a detailed fee demonstration performed
by EPA, placed in the docket prior to
promulgation of the final rule, showing
slightly higher costs for EPA versus state
implementation of a title V program.
The annual inflation adjustment is
performed in October of each year and
is announced on the same Web site as
the part 70 presumptive minimum.
2. Which pollutants are subject to
permit fees?
The terms ‘‘regulated pollutant (for
presumptive fee calculation)’’ under
part 70 and ‘‘regulated pollutant (for fee
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calculation)’’ under part 71 are defined
essentially the same in both programs.
These terms are both currently defined
to mean any ‘‘regulated air pollutant’’
except: (1) Carbon monoxide, (2) any
pollutant that is a regulated air pollutant
solely because it is a Class I or II
substance subject to a standard
promulgated or established under title
VI of the Act, or (3) any pollutant that
is a regulated air pollutant solely
because it is subject to a standard or
regulation under section 112(r) of the
Act. The part 70 fee pollutant definition
specifies which regulated air pollutants
must be considered in presumptive
minimum analyses, while the part 71
fee pollutant definition specifies which
regulated air pollutants are the basis for
fees for part 71 sources. The term
‘‘regulated air pollutant’’ in parts 70 and
71 means the following:
(1) Nitrogen oxides or any volatile
organic compounds;
(2) Any pollutant for which a NAAQS
has been promulgated;
(3) Any pollutant that is subject to any
standard promulgated under section 111
of the Act;
(4) Any Class I or II substance subject
to a standard promulgated under or
established by title VI of the Act; or
(5) Any pollutant subject to a standard
promulgated under section 112 or other
requirements established under section
112 of the Act, including sections
112(g), (j), and (r) of the Act, including
the following: (i) Any pollutant subject
to requirements under section 112(j) of
the Act. If the Administrator fails to
promulgate a standard by the date
established in section 112(e), any
pollutant for which a subject source
would be major shall be considered
regulated 18 months after the section
112(e) date; and (ii) Any pollutant for
which the requirements of section
112(g)(2) of the Act have been met, but
only with respect to the individual
source subject to the requirement.
Note that GHGs are not currently
included in either definition for fee
purposes because they are not
‘‘regulated air pollutants,’’ but GHGs
may be covered in the future.
Also note that section 502(b)(3) of the
Act, upon which these fee regulations
are based, does not specifically require
fees for GHGs, and it does not
specifically require fees for every
regulated air pollutant, even those that
may cause the source to be defined as
a major source; it just requires adequate
fees to cover costs. Thus, we believe the
Act provides us with some discretion in
how we treat GHGs for permit fee
purposes. This discretion also would
potentially include revising the part 70
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and 71 rules to address workload
associated with GHGs.
3. Proposal for Fees in State Part 70
Programs
The permitting of GHGs has the
potential to create overwhelming
resource burdens on State part 70
programs. These burdens would be
significantly reduced under this
proposal, through raising the title V
major source thresholds for GHGs,
which will reduce the number of
sources subject to permitting.
Nonetheless, as noted above, there will
be some remaining additional activity
associated with GHG permitting that
will likely require States to increase
revenue to cover the expected increase
in level of activity. At this time, we
believe that the best approach to address
this situation is for States to assess their
increased workload and determine
whether their current fee regulations
need to be amended to cover any
expected revenue shortfall. If so, States
have a wide variety of possible options
regarding what pollutants and sources
to cover, and what fee structure to
adopt.
The EPA is not proposing at this time
to amend its regulations to establish a
presumptive fee approach that would
involve specifically charging fees for
GHGs. We are also not proposing at this
time to calculate a new presumptive
minimum fee under the existing
presumptive fee approach to take GHGs
into account, or to mandate revisions to
fee regulations for GHGs in States that
did not adopt the presumptive fee
approach. We believe that the best
approach at this time is to allow each
State to determine how best to satisfy
the fee adequacy requirement under the
existing process, for EPA to monitor the
situation, and be prepared to exercise
oversight authority if necessary.
Due to the large quantity of GHGs
emitted relative to criteria pollutants,
for example at a combustion source
where GHGs may be from several
hundred times to over one thousand
times the emissions of other combustion
pollutants, EPA has decided not to
propose to amend its regulations to
establish a presumptive fee approach
that would treat GHGs similarly to
current fee pollutants. Such an
approach would result in greatly
excessive revenues because agency
workloads are not necessarily
proportional to emissions for sources
and GHG emissions are orders of
magnitude larger than other emissions
for many source categories. Thus we
have rejected that approach as an
option. Similarly, we considered and
rejected proposing to require a different,
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55347
significantly reduced presumptive
minimum fee for GHG [e.g., by revising
§ 70.9(b)(2)]. This is not required by the
Act, provided States can raise revenues
in the aggregate that are adequate to
cover program costs. We also believe we
would need better data to establish the
appropriate basis for the GHG
presumptive minimum. We expect our
data will improve over time as EPA and
permitting authorities gain experience
with GHG permitting programs, but at
present there are large uncertainties in
our estimates of the additional GHG
workload at the 25,000 ton CO2 level,
the level of effort needed to incorporate
future regulations for GHGs into
permits, and the additional revenue that
would come in from fees paid for
emissions other than GHG from newly
covered sources under existing fee
schedules. Also, for similar reasons, we
have decided not to issue NODs under
§ 70.10(b) for State failure to adequate
implement and enforce their part 70
programs on the basis of failure to date
to revise their fee schedules to cover any
existing or anticipated workload for
GHGs (for example, the workload
associated with planning for future
regulation, conducting emissions
inventories of GHGs, and similar
activities directly or indirectly related to
part 70 permitting).
Although we do not believe it is
necessary to revise our part 70
regulations to implement the fee
requirements for GHGs, EPA intends to
closely monitor State programs to
ensure that incorporating GHGs into
permits do not result in fee shortfalls
serious enough to imperil the
implementation and enforcement of the
part 70 program. EPA has adequate
authority under § 70.9(b)(5) to perform
audits of State fees at any time, at our
own initiative or whenever any serious
questions are raised about fee adequacy,
and we have done so in the past. During
any such audit, EPA would focus its
review on the program support test of
§ 70.9(b)(1) in order to assure that fees
are adequate to support the program.
There is also authority in § 70.4(i)(3) for
EPA or the State to initiate a program
revision when relevant Federal or State
regulations are modified or
supplemented, such as when EPA takes
a future action to regulate GHGs or
when EPA has reason to believe that a
State is not adequately administering its
program, which could occur if a fee
audit uncovers a need to increase a
State’s fees. This provision specifically
authorizes EPA to request additional
documents or information, such as a
revised fee demonstration. We also have
authority to take action for a State’s
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failure to adequately administer and
enforce a part 70 permits program under
§ 70.10(b). This process includes the
issuance of a NOD and could result
ultimately in withdrawal of the part 70
program and imposition of a Federal
part 71 program in its place, if
appropriate and timely part 70 program
revisions are not made (e.g., NODs on
questions of fee adequacy: (1) 69 FR
10167, March 4, 2004, https://
edocket.access.gpo.gov/2004/044822.htm; and (2) 71 FR 67061,
November 20, 2006, https://
www.epa.gov/EPA-AIR/2006/November/
Day-20/a19555.htm). There are other
examples where EPA has performed
oversight of fee adequacy over State or
local part 70 programs that did not
ultimately result in the issuance of an
NOD (i.e., see a December 13, 2001,
letter from EPA Region 10 to a
concerned citizen, https://www.epa.gov/
region7/programs/artd/air/title5/
t5memos/aktrust.pdf; and a September
23, 2002, letter from EPA Region 3 to a
concerned citizen, https://www.epa.gov/
air/oaqps/permits/response/
maryland.pdf.
For these reasons we are proposing a
recommendation that each State, local,
or tribal part 70 program review its
expected resource needs for
implementing GHGs and its fee
schedule with the aim of determining if
its fee revenues will be adequate to
cover the direct and indirect costs of
implementing its program once GHGs
are brought into the program. If they
would not be adequate, States using the
presumptive fee approach should be
proactive in raising fees on current
‘‘regulated pollutants (for presumptive
fee calculation)’’ or developing other
alternative approaches to meet the
shortfall. We may officially require
submittal of fee analyses for GHGs at
any time in the future, but we do not
believe we need to do so at this time.
This approach is consistent with how
we have treated past Federal regulations
that could have potentially affected title
V program resources and fees, including
final rules that resulted in new
applicable requirements in permits and
that changed the number of sources
required to get permits (e.g., we did not
require new fee demonstrations in
response to promulgation of a large
number of part 63 emissions standards,
nor in response to part 63 standards that
required title V permits for minor
sources). In those situations, we did not
alter the Federal fee regulations or
require changes to the fee regulations in
State programs, but the requirement for
adequate revenues still applied.
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4. GHGs and Part 71 Fees
Similar to the explanation for part 70
above, after GHGs become regulated for
CAA purposes, we note that increased
burdens will likely fall on part 71
permitting authorities (EPA and
delegate agencies), resulting in the need
for EPA to review the part 71 fee
schedule to ensure there are adequate
fees to cover program costs. We are also
not proposing at this time to establish a
presumptive fee approach that would
treat GHGs similarly to current fee
pollutants nor to adjust the fee schedule
of § 71.9(c) with respect to these
expected burdens for similar reasons we
explained above for part 70. EPA has
not determined that existing part 71 fee
structure will be inadequate to fund the
part 71 program costs in the next few
years with GHG permitting included.
We will examine the increases in part
71 burden due to GHG-related
permitting activity and in fees collected
from part 71 sources to assess whether
part 71 fees remain adequate. Section
71.9(c)(7) requires EPA to revise the fee
schedule by rule if it does not reflect the
costs of program administration, while
§ 71.9(n)(2) requires the Administrator
to review the fees schedule every 2
years and to revise it if necessary.
E. Implementation Assistance and
Support
In addition to the development of
permit streamlining techniques during
the threshold evaluation period to
address administrative capacity issues,
EPA also plans to compile and make
available technical and background
information on GHG emission factors,
control technologies, strategies and
measurement and monitoring
methodologies for key GHG source
categories. This information will be
particularly helpful to permitting
authorities in making BACT
determinations for GHG for sources that
trigger PSD during the phase-in period.
We plan to make the information
available at such time as necessary to
support permitting agencies in their
BACT determinations (e.g., on or before
EPA completes an action that triggers
PSD for GHGs). In addition, we will
pursue using this information to
develop presumptive BACT levels for
selected source categories.
We intend to focus our support effort
on the largest emitting GHG source
categories, those that would likely
exceed the temporary major source GHG
threshold adopted as part of this action.
At this time, we believe that power
plants, petroleum refineries, pulp and
paper mills, iron and steel facilities and
portland cement plants are some of the
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source categories for which such
information would initially prove most
useful to permitting agencies. A key
objective of this support effort will be to
help permitting authorities find cost
effective ways to achieve GHG controls
under the BACT requirement. In
addition, the information may be useful
to permit applicants in preparing BACT
analyses as well as providing other
stakeholders with an understanding of
how GHG emissions may be mitigated.
As an example, the information
would include EPA’s industrial energy
management resources for energy
intensive industries available through
its ENERGY STAR program (see https://
www.energystar.gov/index.cfm?c=in_
focus.bus_industries_focus). We intend
to work closely with stakeholders in
developing the support effort and
information. This will help assure that,
to the extent possible, the information
developed supports consistency and
certainty in BACT determinations. In
planning this effort, EPA seeks comment
on the following: (1) Given time and
resource constraints, which specific
source categories or sectors, including
emission units, should EPA prioritize,
(2) what specific information (e.g.,
emission factors, control technologies,
collateral impacts, cost information,
etc.) and what format would be most
helpful to permitting agencies in
carrying out the provisions of the PSD
and title V programs as they would
apply to GHGs, and (3) what other types
of support or assistance can EPA
provide to initially help air pollution
control agencies with the permitting of
GHGs?
XI. Statutory and Executive Order
Reviews
A. Executive Order 12866—Regulatory
Planning and Review
Under Executive Order (EO) 12866
(58 FR 51735, October 4, 1993), this
action is a ‘‘significant regulatory
action’’ because it raises novel legal or
policy issues. Accordingly, EPA
submitted this action to the Office of
Management and Budget (OMB) for
review under EO 12866 and any
changes made in response to OMB
recommendations have been
documented in the docket for this
action.
In addition, EPA prepared an analysis
of the potential costs and benefits
associated with this action. This
analysis is provided in the docket for
this action and the analysis is briefly
summarized in section IX of this
preamble.
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B. Paperwork Reduction Act
This action does not impose any new
information collection burden. Instead,
this proposed action would significantly
reduce costs incurred by sources and
permitting authorities relative to the
costs that would be incurred if EPA did
not revise the rule. Based on our GHG
threshold data analysis, we estimated
that over 40,000 new and modified
facilities per year would be subject to
PSD review based on applying a GHG
emissions threshold of 250 tpy using a
CO2e metric. This is compared to 280
PSD permits currently issued per year,
which is an increase of more than 140fold. Similarly, for title V, we estimated
that over six million new sources would
be affected at the 100-tpy threshold for
GHGs using the CO2e metric. By
increasing the volume of permits by
over 400 times, the administrative
burden would be unmanageable without
this rule. Despite this reduction of
burden, 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 respectively.
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
APA 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 proposed action on small
entities, small entity is defined as: (1) A
small business that is a small industrial
entity as defined in the U.S. Small
Business Administration (SBA) size
standards (see 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; or (3) a
small organization that is any not-forprofit enterprise that is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of this proposed action on small
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entities, I certify that this proposed
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 analysis 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 proposed action
will relieve the regulatory burden
associated with the major PSD and title
V operating permits programs for new or
modified major sources that emit GHGs,
including small businesses. This is
because the proposed action would raise
major source applicability thresholds for
these programs for sources that emit
GHGs at rates below 25,000 tpy CO2e.
As a result, the program changes
provided in the proposed rule are not
expected to result in any increases in
expenditure by any small entity.
We have therefore concluded that this
proposed rule would relieve regulatory
burden for a substantial number of small
entities, and thus I certify that it will not
have a significant economic impact on
a substantial number of small entities.
However, EPA recognizes that some
small entities continue to be concerned
about the potential impacts of the
statutory imposition of PSD
requirements that may occur given the
various EPA rulemakings currently
under consideration concerning GHG
emissions. Accordingly, EPA will use
the discretion afforded to it under the
RFA to consult with OMB and SBA,
with input from outreach to small
entities, regarding the potential impacts
of PSD regulatory requirements that
might occur as EPA considers
regulations of GHGs. EPA is not
required to consult in this manner when
it has certified that a rule will not have
a significant economic impact on a
substantial number of small entities, but
we believe that engaging in such
consultation before finalization of this
rule will help us to better understand
and address the potential PSD
regulatory concerns of small entities
that might experience such impacts.
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55349
D. Unfunded Mandates Reform Act
This proposed action 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 1 year. Although this proposed
action would result in a small increase
in the burden imposed upon permitting
authorities by requiring States to revise
their SIPs to incorporate the changes,
the revisions would ultimately reduce
the PSD and title V program
administrative burden that would
otherwise occur in the absence of this
rulemaking. Thus, this proposed action
is not subject to the requirements of
sections 202 or 205 of UMRA.
This action 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. EPA
has determined that this proposed
action contains no regulatory
requirements that may significantly or
uniquely affect small governments,
including tribal governments. However,
in developing this proposed action, EPA
consulted with small governments
pursuant to a plan established under
section 203 of UMRA to address impacts
of regulatory requirements in the rule
that might significantly or uniquely
affect small governments. As stated in
sections XI.E and F of this preamble,
EPA consulted with State, local, and
tribal officials early in the process of
developing the proposed regulation to
permit them to have timely and
meaningful input into its development
by publishing an ANPR (73 FR 44354,
July 30, 2008) that included PSD GHG
tailoring options for regulating GHGs
under the CAA. As a result, EPA
received comments from these entities
and took them into consideration when
developing this proposal.
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
Executive Order 13132. These proposed
amendments would ultimately simplify
and reduce the burden on State and
local agencies associated with
implementing the PSD and title V
operating permits programs, by
providing that a source whose GHG
emissions are below the proposed levels
will not have to obtain a PSD permit or
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title V permit. Thus, Executive Order
13132 does not apply to this action.
Consistent with EPA policy, EPA
nonetheless consulted with State and
local officials early in the process of
developing the proposed regulation to
permit them to have meaningful and
timely input into its development by
publishing an advance notice of
proposed rulemaking (ANPR) [73 FR
44354, July 30, 2008] that included PSD
GHG tailoring options for regulating
GHGs under the CAA. As a result of the
ANPR, EPA received several comments
from State and local government
agencies on differing PSD GHG tailoring
options presented in the ANPR which
were considered in this proposal.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local governments, EPA
specifically solicits comment on this
proposed rule from State and local
officials.
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F. Executive Order 13175—Consultation
and Coordination With Indian Tribal
Governments
Subject to the Executive Order 13175,
entitled ‘‘Consultation and Coordination
with Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), EPA may not
issue a regulation that has tribal
implications, that imposes substantial
direct compliance costs, and that is not
required by statute, unless the Federal
government provides the funds
necessary to pay the direct compliance
costs incurred by tribal governments, or
EPA consults with tribal officials early
in the process of developing the
proposed regulation and develops a
tribal summary impact statement.
EPA has concluded that this action
may have tribal implications. However,
it will neither impose substantial direct
compliance costs on tribal governments
nor preempt tribal law. There are no
tribal authorities currently issuing major
NSR permits; however, this may change
in the future.
EPA consulted with tribal officials
early in the process of developing this
regulation to permit them to have
meaningful and timely input into its
development by publishing an ANPR
that included PSD GHG tailoring
options for regulating GHGs under the
CAA. [73 FR 44354, July 30, 2008]. As
a result of the ANPR, EPA received
several comments from tribal officials
on differing PSD GHG tailoring options
presented in the ANPR which were
considered in this proposal.
Although Executive Order 13175 does
not apply to this proposed rule, EPA
specifically solicits additional comment
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G. Executive Order 13045—Protection of
Children From Environmental Health
Risks and Safety Risks
This action is not subject to EO 13045
(62 FR 19885, April 23, 1997) because
the Agency does not believe the
environmental health or safety risks
addressed by this action present a
disproportionate risk to children. We do
not believe this action creates any
environmental health or safety risks.
The public is invited to submit
comments or identify peer-reviewed
studies and data that assess effects of
early life exposure to GHGs.
H. Executive Order 13211—Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use’’ (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.
This action will not create any new
requirements for sources in the energy
supply, distribution, or use sectors.
Federal agencies, to the greatest extent
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.
EPA has determined that this
proposed rule will not have
disproportionately high and adverse
human health or environmental effects
on minority or low-income populations
because 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. Determination Under Section 307(d)
Pursuant to sections 307(d)(1)(E) and
307(d)(1)(V) of the CAA, the
Administrator determines that this
action is subject to the provisions of
section 307(d). Section 307(d)(1)(V)
provides that the provisions of section
307(d) apply to ‘‘such other actions as
the Administrator may determine.’’
on this proposed action from tribal
officials.
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, 12(d) (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. NTTAA directs EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards.
This proposed rulemaking 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
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XII. Statutory Authority
The statutory authority for this action
is provided by sections 307(d)(7)(B),
101, 111, 114, 116, and 301 of the CAA
as amended (42 U.S.C. 7401, 7411, 7414,
7416, and 7601). This action is also
subject to section 307(d) of the CAA (42
U.S.C. 7407(d)).
List of Subjects
40 CFR Part 51
Administrative practice and
procedure, Air pollution control, Carbon
dioxide, Carbon dioxide equivalents,
Environmental protection, Greenhouse
gases, Hydrofluorocarbons,
Intergovernmental relations, Methane,
Nitrous oxide, Perfluorocarbons,
Reporting and recordkeeping
requirements, Sulfur hexafluoride.
40 CFR Part 52
Air pollution control, Carbon dioxide,
Carbon dioxide equivalents,
Environmental protection, Greenhouse
gases, Hydrofluorocarbons,
Intergovernmental relations, Methane,
Nitrous oxide, Perfluorocarbons,
Reporting and recordkeeping
requirements, Sulfur hexafluoride.
40 CFR Part 70
Administrative practice and
procedure, Air pollution control, Carbon
dioxide, Carbon dioxide equivalents,
Environmental protection, Greenhouse
gases, Hydrofluorocarbons,
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Intergovernmental relations, Methane,
Nitrous oxide, Perfluorocarbons,
Reporting and recordkeeping
requirements, Sulfur hexafluoride.
Administrative practice and
procedure, Air pollution control, Carbon
dioxide, Carbon dioxide equivalents,
Environmental protection, Greenhouse
gases, Hydrofluorocarbons, Methane,
Nitrous oxide, Perfluorocarbons,
Reporting and recordkeeping
requirements, Sulfur hexafluoride.
Dated: September 30, 2009.
Lisa P. Jackson,
Administrator.
For reasons stated in the preamble,
title 40, chapter I of the Code of Federal
Regulations is proposed to be amended
as set forth below.
PART 51—[AMENDED]
1. The authority citation for part 51
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
Subpart I—[Amended]
2. Section 51.166 is amended:
a. By revising paragraphs (b)(1)(i)(a),
and (b)(1)(i)(b);
b. By adding paragraph (b)(1)(i)(d);
c. By revising paragraph (b)(23)(i); and
d. By adding paragraphs (b)(57) and
(b)(58).
The revisions and additions read as
follows:
§ 51.166 Prevention of significant
deterioration of air quality.
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*
Pollutant and Emissions Rate
*
*
*
*
(b) * * *
(1)(i) * * *
(a) Any of the following stationary
sources of air pollutants which emits, or
has the potential to emit, 100 tons per
year or more of any regulated NSR
pollutant (except for greenhouse gases
(as defined under paragraph (b)(57) of
this section), except as provided under
paragraph (b)(1)(i)(d) of this section):
Fossil fuel-fired steam electric plants of
more than 250 million British thermal
units per hour heat input, coal cleaning
plants (with thermal dryers), kraft pulp
mills, portland cement plants, primary
zinc smelters, iron and steel mill plants,
primary aluminum ore reduction plants
(with thermal dryers), primary copper
smelters, municipal incinerators capable
of charging more than 250 tons of refuse
per day, hydrofluoric, sulfuric, and
nitric acid plants, petroleum refineries,
lime plants, phosphate rock processing
plants, coke oven batteries, sulfur
recovery plants, carbon black plants
(furnace process), primary lead smelters,
fuel conversion plants, sintering plants,
secondary metal production plants,
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chemical process plants (which does not
include ethanol production facilities
that produce ethanol by natural
fermentation included in NAICS codes
325193 or 312140), fossil-fuel boilers (or
combinations thereof) totaling more
than 250 million British thermal units
per hour heat input, petroleum storage
and transfer units with a total storage
capacity exceeding 300,000 barrels,
taconite ore processing plants, glass
fiber processing plants, and charcoal
production plants;
(b) Notwithstanding the stationary
source size specified in paragraph
(b)(1)(i)(a) of this section, any stationary
source which emits, or has the potential
to emit, 250 tons per year or more of a
regulated pollutant (except for
greenhouse gases (as defined under
paragraph (b)(57) of this section), except
as provided under paragraph (b)(1)(i)(d)
of this section); or
*
*
*
*
*
(d) Notwithstanding any provision to
the contrary in this section, any
stationary source which emits, or has
the potential to emit, at least 25,000 tpy
CO2e of greenhouse gases, as defined
under paragraph (b)(58) of this section.
*
*
*
*
*
(23)(i) Significant means, in reference
to a net emissions increase or the
potential of a source to emit any of the
following pollutants, a rate of emissions
that would equal or exceed any of the
following rates:
Carbon monoxide: 100 tons per year
(tpy)
Nitrogen oxides: 40 tpy
Sulfur dioxide: 40 tpy
Particulate matter: 25 tpy of particulate
matter emissions. 15 tpy of PM10
emissions.
PM2.5: 10 tpy of direct PM2.5 emissions;
40 tpy of sulfur dioxide emissions; 40
tpy of nitrogen oxide emissions unless
demonstrated not to be a PM2.5
precursor under paragraph (b)(49) of
this section
Ozone: 40 tpy of volatile organic
compounds or nitrogen oxides
Lead: 0.6 tpy
Fluorides: 3 tpy
Sulfuric acid mist: 7 tpy
Hydrogen sulfide (H2S): 10 tpy
Total reduced sulfur (including H2S): 10
tpy
Reduced sulfur compounds (including
H2S): 10 tpy
Municipal waste combustor organics
(measured as total tetra- through octachlorinated dibenzo-p-dioxins and
dibenzofurans): 3.2 × 10¥6 megagrams
per year (3.5 × 10¥6 tpy)
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Municipal waste combustor metals
(measured as particulate matter): 14
megagrams per year (15 tpy)
Municipal waste combustor acid gases
(measured as sulfur dioxide and
hydrogen chloride): 36 megagrams per
year (40 tpy)
Municipal solid waste landfill
emissions (measured as nonmethane
organic compounds): 45 megagrams
per year (50 tpy)
Greenhouse gases: [10,000 to 25,000]
CO2e
*
*
*
*
*
(57) Greenhouse gas, or GHG, means
carbon dioxide (CO2), methane (CH4),
nitrous oxide (N2O), sulfur hexafluoride
(SF6), hydrofluorocarbons (HFCs), and
perfluorocarbons (PFCs).
(58) Carbon dioxide equivalent, or
CO2e, means a metric used to compare
the emissions from various greenhouse
gases based upon their global warming
potential (GWP). The CO2e for a gas is
determined by multiplying the mass of
the gas by the associated GWP. The
applicable GWPs and guidance on how
to calculate a source’s GHG emissions in
tpy CO2e can be found in EPA’s
‘‘Inventory of U.S. Greenhouse Gas
Emissions and Sinks,’’ which is updated
annually under existing commitment
under the United Nations Framework
Convention on Climate Change
(UNFCCC).
*
*
*
*
*
PART 52—[AMENDED]
3. The authority citation for part 52
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
4. Section 52.21 is amended:
a. By revising paragraphs (b)(1)(i)(a)
and (b)(1)(i)(b);
b. By adding paragraph (b)(1)(i)(d);
c. By revising paragraph (b)(23)(i); and
d. By adding paragraphs (b)(59) and
(b)(60).
The revisions and additions read as
follows:
§ 52.21 Prevention of significant
deterioration of air quality.
*
*
*
*
*
(b) * * *
(1)(i) * * *
(a) Any of the following stationary
sources of air pollutants which emits, or
has the potential to emit, 100 tons per
year or more of any regulated NSR
pollutant (except for greenhouse gases
(as defined under paragraph (b)(59) of
this section), except as provided under
paragraph (b)(1)(i)(d) of this section):
Fossil fuel-fired steam electric plants of
more than 250 million British thermal
units per hour heat input, coal cleaning
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Ozone: 40 tpy of volatile organic
compounds or nitrogen oxides
Lead: 0.6 tpy
Fluorides: 3 tpy
Sulfuric acid mist: 7 tpy
Hydrogen sulfide (H2S): 10 tpy
Total reduced sulfur (including H2S): 10
tpy
Reduced sulfur compounds (including
H2S): 10 tpy
Municipal waste combustor organics
(measured as total tetra- through octachlorinated dibenzo-p-dioxins and
dibenzofurans): 3.2 × 10¥6 megagrams
per year (3.5 × 10¥6 tpy)
Municipal waste combustor metals
(measured as particulate matter): 14
megagrams per year (15 tpy)
Municipal waste combustor acid gases
(measured as sulfur dioxide and
hydrogen chloride): 36 megagrams per
year (40 tpy)
Municipal solid waste landfill
emissions (measured as nonmethane
organic compounds): 45 megagrams
per year (50 tpy)
Greenhouse gases: [10,000 to 25,000]
CO2e
*
*
*
*
*
(59) Greenhouse gas, or GHG, means
carbon dioxide (CO2), methane (CH4),
nitrous oxide (N2O), sulfur hexafluoride
(SF6), hydrofluorocarbons (HFCs), and
perfluorocarbons (PFCs).
(60) Carbon dioxide equivalent, or
CO2e, means a metric used to compare
the emissions from various greenhouse
gases based upon their global warming
potential (GWP). The CO2e for a gas is
determined by multiplying the mass of
the gas by the associated GWP. The
applicable GWPs and guidance on how
to calculate a source’s GHG emissions in
tpy CO2e can be found in EPA’s
‘‘Inventory of U.S. Greenhouse Gas
Emissions and Sinks,’’ which is updated
annually under existing commitment
under the United Nations Framework
Convention on Climate Change
(UNFCCC).
*
*
*
*
*
5. Section 52.53 is revised to read as
follows:
Pollutant and Emissions Rate
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plants (with thermal dryers), kraft pulp
mills, portland cement plants, primary
zinc smelters, iron and steel mill plants,
primary aluminum ore reduction plants
(with thermal dryers), primary copper
smelters, municipal incinerators capable
of charging more than 250 tons of refuse
per day, hydrofluoric, sulfuric, and
nitric acid plants, petroleum refineries,
lime plants, phosphate rock processing
plants, coke oven batteries, sulfur
recovery plants, carbon black plants
(furnace process), primary lead smelters,
fuel conversion plants, sintering plants,
secondary metal production plants,
chemical process plants (which does not
include ethanol production facilities
that produce ethanol by natural
fermentation included in NAICS codes
325193 or 312140), fossil-fuel boilers (or
combinations thereof) totaling more
than 250 million British thermal units
per hour heat input, petroleum storage
and transfer units with a total storage
capacity exceeding 300,000 barrels,
taconite ore processing plants, glass
fiber processing plants, and charcoal
production plants;
(b) Notwithstanding the stationary
source size specified in paragraph
(b)(1)(i) of this section, any stationary
source which emits, or has the potential
to emit, 250 tons per year or more of a
regulated NSR pollutant (except for
greenhouse gases (as defined under
paragraph (b)(59) of this section), except
as provided under paragraph (b)(1)(i)(d)
of this section); or
*
*
*
*
*
(d) Notwithstanding any provision to
the contrary in this section, any
stationary source of air pollutants which
emits, or has the potential to emit,
25,000 tpy CO2e of greenhouse gases, as
defined under paragraph (b)(60) of this
section.
*
*
*
*
*
(23)(i) Significant means, in reference
to a net emissions increase or the
potential of a source to emit any of the
following pollutants, a rate of emissions
that would equal or exceed any of the
following rates:
§ 52.53
Carbon monoxide: 100 tons per year
(tpy)
Nitrogen oxides: 40 tpy
Sulfur dioxide: 40 tpy
Particulate matter: 25 tpy of particulate
matter emissions
PM10: 15 tpy
PM2.5: 10 tpy of direct PM2.5 emissions;
40 tpy of sulfur dioxide emissions; 40
tpy of nitrogen oxide emissions unless
demonstrated not to be a PM2.5
precursor under paragraph (b)(50) of
this section
(a) With the exceptions set forth in
this subpart, the Administrator approves
Alabama’s plans for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
the plans satisfy all requirements of Part
D, Title I, of the Clean Air Act as
amended in 1977. In addition,
continued satisfaction of the
requirements of Part D for the ozone
portion of the SIP depends on the
adoption and submittal of RACT
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Approval status.
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requirements by July 1, 1980 for the
sources covered by CTGs issued
between January 1978 and January 1979
and adoption and submittal by each
subsequent January of additional RACT
requirements for sources covered by
CTGs issued by the previous January.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
6. Section 52.72 is revised to read as
follows:
§ 52.72
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Alaska’s plan for the attainment and
maintenance of the national standards.
The State included in the plan a
regulation prohibiting idling of
unattended motor vehicles. However,
the plan stated that this regulation was
included for informational purposes
only, and was not to be considered part
of the control strategy to implement the
national standards for carbon monoxide.
Accordingly, this regulation is not
considered a part of the applicable plan.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
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7. Section 52.123 is amended by
adding paragraph (l) to read as follows:
§ 52.123
Approval status.
*
*
*
*
*
(l)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
8. Section 52.172 is revised to read as
follows:
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§ 52.172
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Arkansas’ plan for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Further, the Administrator finds that the
plan satisfies all requirements of Part D
of the Clean Air Act, as amended in
1977, except as noted below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
9. Section 52.223 is amended by
adding paragraph (f) to read as follows:
§ 52.223
Approval status.
*
*
*
*
*
(f)(1) Insofar as the PSD permitting
threshold provisions concern sources of
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GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
10. Section 52.323 is revised to read
as follows:
§ 52.323
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Colorado’s plan for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
that the plan satisfies all requirements
of Part D, Title 1, of the Clean Air Act
as amended in 1977, except as noted
below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
11. Section 52.373 is amended by
adding paragraph (c) to read as follows:
§ 52.373
Approval status.
*
*
*
*
*
(c)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
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55353
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
12. Section 52.422 is amended by
adding paragraph (c) to read as follows:
§ 52.422
Approval status.
*
*
*
*
*
(c)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
13. Section 52.472 is amended by
adding paragraph (g) to read as follows:
§ 52.472
Approval status.
*
*
*
*
*
(g)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
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14. Section 52.522 is revised to read
as follows:
§ 52.522
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Florida’s plans for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
the plans satisfy all requirements of Part
D, Title I, of the Clean Air Act as
amended in 1977, except as noted
below. In addition, continued
satisfaction of the requirements of Part
D, for the ozone portion of the SIP
depends on the adoption and submittal
of RACT requirements by July 1, 1980
for those sources covered by CTGs
issued between January 1978 and
January 1979 and adoption and
submittal by each subsequent January of
additional RACT requirements for
sources covered by CTGs issued by the
previous January.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
15. Section 52.572 is revised to read
as follows:
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§ 52.572
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Georgia’s plans for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
the plans satisfy all requirements of Part
D, Title I, of the Clean Air Act as
amended in 1977, except as noted
below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
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to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
16. Section 52.623 is revised to read
as follows:
§ 52.623
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Hawaii’s plan for attainment and
maintenance of the national standards.
The State included various provisions
in its plan to provide for the attainment
of State ambient air quality standards.
As described in the Governor’s letters of
January 28, May 8, and May 22, 1972,
these provisions were included for
information purposes only and were not
to be considered a part of the plan to
implement national standards.
Accordingly, these additional
provisions are not considered a part of
the applicable plan.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
17. Section 52.673 is revised to read
as follows:
§ 52.673
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Idaho’s plan for the attainment and
maintenance of the national standards.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
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GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
18. Section 52.722 is amended by
adding paragraph (d) to read as follows:
§ 52.722
Approval status.
*
*
*
*
*
(d)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
19. Section 52.773 is amended by
adding paragraph (k) to read as follows:
§ 52.773
Approval status.
*
*
*
*
*
(k)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
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significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
20. Section 52.822 is amended by
adding paragraph (b) to read as follows:
§ 52.822
Approval status.
*
*
*
*
*
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
21. Section 52.873 is amended by
adding paragraph (d) to read as follows:
§ 52.873
Approval status.
*
*
*
*
*
(d)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
22. Section 52.923 is amended by
adding paragraph (c) to read as follows:
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§ 52.923
Approval status.
*
*
*
*
*
(c)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
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to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
23. Section 52.986 is amended by
adding paragraph (c) to read as follows:
§ 52.986
quality.
Significant deterioration of air
*
*
*
*
*
(c)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
24. Section 52.1022 is revised to read
as follows:
§ 52.1022
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Maine’s plan, as identified in § 52.1020,
for the attainment and maintenance of
the national standards under section
110 of the Clean Air Act.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
PO 00000
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55355
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
25. Section 52.1073 is amended by
adding paragraph (h) to read as follows:
§ 52.1073
Approval status.
*
*
*
*
*
(h)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
26. Section 52.1123 is amended by
adding paragraph (c) to read as follows:
§ 52.1123
Approval status.
*
*
*
*
*
(c)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
27. Section 52.1172 is revised to read
as follows:
§ 52.1172
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Michigan’s plan for the attainment and
maintenance of the National Ambient
Air Quality Standards under section 110
of the Clean Air Act. Furthermore, the
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Administrator finds the plan satisfies all
requirements of Part D, Title I of the
Clean Air Act as amended in 1977,
except as noted below. In addition,
continued satisfaction of the
requirements of Part D for the ozone
portion of the SIP depends on the
adoption and submittal of RACT
requirements by July 1, 1980 for the
sources covered by CTGs between
January 1978 and January 1979 and
adoption and submittal by each
subsequent January of additional RACT
requirements for sources covered by
CTGs issued by the previous January.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
28. Section 52.1223 is revised to read
as follows:
pwalker on DSK8KYBLC1PROD with PROPOSALS2
§ 52.1223
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Minnesota’s plans for the attainment
and maintenance of the national
standards under section 110 of the
Clean Air Act. Furthermore, the
Administrator finds the plan satisfies all
requirements of Part D, Title 1, of the
Clean Air Act as amended in 1977,
except as noted below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
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no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
29. Section 52.1272 is revised to read
as follows:
§ 52.1272
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Mississippi’s plan for the attainment
and maintenance of national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
the plans satisfy all requirements of Part
D, Title I, of the Clean Air Act as
amended in 1977.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
30. Section 52.1323 is amended by
adding paragraph (n) to read as follows:
§ 52.1323
Approval status.
*
*
*
*
*
(n)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
31. Section 52.1372 is revised to read
as follows:
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Fmt 4701
Sfmt 4702
§ 52.1372
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Montana’s plans for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
the plans satisfy all requirements of Part
D, Title I, of the Clean Air Act as
amended in 1977, except as noted
below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
32. Section 52.1422 is revised to read
as follows:
§ 52.1422
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Nebraska’s plan for the attainment and
maintenance of the national standards.
No action is taken on the new source
review regulations to comply with
section 172(b)(6) and section 173 of the
Clean Air Act as amended in 1977, and
40 CFR 51.18(j).
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
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33. Section 52.1472 is amended by
adding paragraph (d) to read as follows:
§ 52.1472
Approval status.
*
*
*
*
*
(d)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
34. Section 52.1522 is amended by
adding paragraph (c) to read as follows:
§ 52.1522
Approval status.
*
*
*
*
*
(c)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
35. Section 52.1573 is revised to read
as follows:
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§ 52.1573
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
New Jersey’s plans for attainment and
maintenance of the national ambient air
quality standards under section 110 of
the Clean Air Act. Furthermore, the
Administrator finds that the plan
satisfies all requirements of Part D, Title
I, of the Clean Air Act, as amended in
1977, except as noted below in
§ 52.1581. In addition, continued
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satisfaction of the requirements of Part
D for the ozone portion of the SIP
depends on the adoption and submittal
of RACT requirements by July 1, 1980
for the sources covered by CTGs issued
between January 1978 and January 1979
and adoption and submittal by each
subsequent January of additional RACT
requirements for sources covered by
CTGs issued by the previous January.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
36. Section 52.1622 is revised to read
as follows:
§ 52.1622
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
New Mexico’s plan for the attainment
and maintenance of the national
standards under section 110 of the
Clean Air Act. Further, the
Administrator finds that the plan
satisfies all requirements of Part D of the
Clean Air Act, as amended in 1977,
except as noted below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
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55357
37. Section 52.1673 is amended by
adding paragraph (b) to read as follows:
§ 52.1673
Approval status.
*
*
*
*
*
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
38. Section 52.1772 is amended by
adding paragraph (c) to read as follows:
§ 52.1772
Approval status.
*
*
*
*
*
(c)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
39. Section 52.1822 is revised to read
as follows:
§ 52.1822
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
the North Dakota plan for the attainment
and maintenance of the national
standards.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
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25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
40. Section 52.1873 is revised to read
as follows:
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§ 52.1873
Approval status.
(a) With the exceptions set forth in
this subpart the Administrator approves
Ohio’s plan for the attainment and
maintenance of the National Ambient
Air Quality Standards under section 110
of the Clean Air Act. Furthermore, the
Administrator finds the plan satisfies all
the requirements of Part D, Title 1 of the
Clean Air Act as amended in 1977,
except as noted below. In addition,
continued satisfaction of the
requirements of Part D for the ozone
portion of the SIP depends on the
adoption and submittal of RACT
requirements by January 1, 1981 for the
sources covered by CTGs between
January 1978 and January 1979 and
adoption and submittal by each
subsequent January of additional RACT
requirements for sources covered by
CTGs issued by the previous January.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
41. Section 52.1922 is revised to read
as follows:
§ 52.1922
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
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Oklahoma’s plan for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
that the plan satisfies all requirements
of Part D, Title 1, of the Clean Air Act
as amended in 1977, except as noted
below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
42. Section 52.1972 is revised to read
as follows:
§ 52.1972
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Oregon’s plan for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
43. Section 52.2023 is amended by
adding paragraph (l) to read as follows:
§ 52.2023
Approval status.
*
*
*
*
*
(l)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
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Fmt 4701
Sfmt 4702
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
44. Section 52.2072 is revised to read
as follows:
§ 52.2072
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Rhode Island’s plan, as identified in
§ 52.2070 of this subpart, for the
attainment and maintenance of the
national standards under section 110 of
the Clean Air Act. Furthermore, the
Administrator finds the plan satisfies all
requirements of Part D, Title I, of the
Clean Air Act, as amended in 1977,
except as noted below. In addition,
continued satisfaction of the
requirements of Part D for the ozone
portion of the SIP depends on the
adoption and submittal of RACT
requirements by January 1, 1981 for the
sources covered by CTGs issued
between January 1978 and January 1979
and adoption and submittal by each
subsequent January as additional RACT
requirements for sources covered by
CTGs issued by the previous January.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
45. Section 52.2122 is amended by
adding paragraph (c) to read as follows:
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§ 52.2122
Approval status.
*
*
*
*
*
(c)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
46. Section 52.2172 is revised to read
as follows:
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§ 52.2172
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
South Dakota’s plan as meeting the
requirements of section 110 of the Clean
Air Act, as amended in 1977.
Furthermore, the Administrator finds
that the plan satisfies all requirements
of Part D of the Clean Air Act, as
amended in 1977.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
47. Section 52.2222 is amended by
adding paragraph (d) to read as follows:
§ 52.2222
Approval status.
*
*
*
*
*
(d)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
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GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
48. Section 52.2273 is revised to read
as follows:
§ 52.2273
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Texas’ plan for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
that the plan satisfies all requirements
of Part D, Title 1, of the Clean Air Act
as amended in 1977, except as noted
below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
49. Section 52.2323 is revised to read
as follows:
§ 52.2323
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Utah’s plan as meeting the requirements
of section 110 of the Clean Air Act as
amended in 1977. Furthermore, the
Administrator finds that the plan
satisfies all requirements of Part D, Title
1, of the Clean Air Act as amended in
1977, except as noted below.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
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55359
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
50. Section 52.2372 is revised to read
as follows:
§ 52.2372
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Vermont’s plan as identified in
§ 52.2370 for the attainment and
maintenance of the national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
the plans satisfy all requirements of Part
D, Title I, of the Clean Air Act, as
amended in 1977, except as noted
below. In addition, continued
satisfaction of the requirements of Part
D for the ozone portion of the SIP
depends on the adoption and submittal
of RACT requirements by July 1, 1980
for the sources covered by CTGs issued
between January, 1978 and January,
1979 and adoption and submittal by
each subsequent January of additional
RACT requirements for sources covered
by CTGs issued by the previous January.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
51. Section 52.2423 is amended by
adding paragraph (t) to read as follows:
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§ 52.2423
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Approval status.
*
*
*
*
*
(t)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
52. Section 52.2473 is revised to read
as follows:
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§ 52.2473
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Washington’s plan for the attainment
and maintenance of National Standards
under section 110 of the Clean Air Act.
The regulations included in the SIP (see
Table 52.2479) are applicable statewide
unless otherwise noted in the regulation
itself. Furthermore, the Administrator
finds that the plan as identified in
§ 52.2470 satisfies requirements of Part
D, Title 1, of the Clean Air act as
amended in 1977, except as noted in the
following sections. Continued
satisfaction of the requirements of Part
D for the ozone portion of the SIP
depends on the adoption and submittal
of RACT requirements by July 1, 1980
for the sources covered by CTGs issued
between January 1978 and January 1979
and adoption and submittal by each
subsequent January of additional RACT
requirements for sources covered by
CTGs issued by the previous January.
New source review permits pursuant to
section 173 of CAA will not be deemed
valid by EPA unless the provisions of
section V of the emission offset
interpretive rule published on January
16, 1979 (44 FR 3274) are met.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
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(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
53. Section 52.2522 is amended by
adding paragraph (j) to read as follows:
§ 52.2522
Approval status.
*
*
*
*
*
(j)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
54. Section 52.2572 is revised to read
as follows:
§ 52.2572
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Wisconsin’s plans for the attainment
and maintenance of the National
Ambient Air Quality Standards under
section 110 of the Clean Air Act.
Furthermore, the Administrator finds
the plans satisfy all requirements of Part
D, Title I, of the Clean Air Act as
amended in 1977, except as noted
below. In addition, continued
satisfaction of the requirements of Part
D for the Ozone portion of the State
Implementation Plan depends on the
adoption and submittal of RACT
requirements on:
(1) Group III Control Techniques
Guideline sources within 1 year after
January 1st following the issuance of
each Group III control technique
guideline; and
(2) Major (actual emissions equal or
greater than 100 tons VOC per year)
non-control technique guideline sources
in accordance with the State’s schedule
contained in the 1982 Ozone SIP
revision for Southeastern Wisconsin.
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(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
55. Section 52.2622 is revised to read
as follows:
§ 52.2622
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Wyoming’s plans as meeting the
requirements of section 110 of the Clean
Air Act, as amended in 1977.
Furthermore, the Administrator finds
that the plans satisfy the requirements
of Part D, Title I, of the Clean Air Act.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
56. Section 52.2672 is revised to read
as follows:
§ 52.2672
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Guam’s plan for the attainment and
maintenance of the National Standards.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
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GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
57. Section 52.2722 is revised to read
as follows:
§ 52.2722
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
Puerto Rico’s plans for the attainment
and maintenance of national standards
under section 110 of the Clean Air Act.
Furthermore, the Administrator finds
that the plan satisfies all requirements
of Part D, Title I, of the Clean Air Act,
as amended in 1977.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
58. Section 52.2772 is revised to read
as follows:
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§ 52.2772
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
the U.S. Virgin Islands plan for
attainment and maintenance of the
national standards.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
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to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
59. Section 52.2822 is revised to read
as follows:
§ 52.2822
Approval status.
(a) With the exceptions set forth in
this subpart, the Administrator approves
American Samoa’s plan for the
attainment and maintenance of the
national standards.
(b)(1) Insofar as the PSD permitting
threshold provisions concern sources of
GHG emissions, EPA limits its approval
of such provisions to the extent they
subject to PSD requirements sources of
GHG emissions that equal or exceed
25,000 tpy CO2e. EPA takes no action on
the PSD permitting threshold provisions
to the extent they subject to PSD
requirements sources of GHG emissions
that are less than 25,000 tpy CO2e.
(2) Insofar as the PSD significance
levels concern sources of GHG
emissions, EPA limits its approval of
such provisions to the extent those
provisions treat as significant GHG
emissions increases that equal or exceed
[10,000 to 25,000] tpy CO2e. EPA takes
no action on the PSD significance level
provisions to the extent they treat as
significant GHG emissions increases less
than [10,000 to 25,000] tpy CO2e.
PART 70—[AMENDED]
60. The authority citation for part 70
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
61. Section 70.2 is amended to read as
follows:
a. By adding definitions in
alphabetical order for carbon dioxide
equivalent and greenhouse gas;
b. By revising paragraph (2) of the
definition for major source; and
c. By adding paragraph (4) to the
definition for major source.
§ 70.2
Definitions.
*
*
*
*
*
Carbon dioxide equivalent, or CO2e,
means a metric used to compare the
emissions from various greenhouse
gases based upon their global warming
potential (GWP). The CO2e for a gas is
determined by multiplying the mass of
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the gas by the associated GWP. The
applicable GWPs and guidance on how
to calculate a source’s GHG emissions in
tpy CO2e can be found in EPA’s
‘‘Inventory of U.S. Greenhouse Gas
Emissions and Sinks,’’ which is updated
annually under existing commitment
under the United Nations Framework
Convention on Climate Change
(UNFCCC).
*
*
*
*
*
Greenhouse gas, or GHG, means
carbon dioxide (CO2), methane (CH4),
nitrous oxide (N2O), sulfur hexafluoride
(SF6), hydrofluorocarbons (HFCs), and
perfluorocarbons (PFCs).
*
*
*
*
*
Major source * * *
(2) A major stationary source of air
pollutants (except for greenhouse gases,
except as otherwise provided in this
section) as defined in section 302 of the
Act, that directly emits, or has the
potential to emit, 100 tpy or more of any
air pollutant (including any major
source of fugitive emissions of any such
pollutant, as determined by rule by the
Administrator). The fugitive emissions
of a stationary source shall not be
considered in determining whether it is
a major stationary source for the
purposes of section 302(j) of the Act,
unless the source belongs to one of the
following categories of stationary
source:
*
*
*
*
*
(4) A stationary source that directly
emits, or has the potential to emit,
25,000 tpy CO2e or more of greenhouse
gases that are subject to regulation
under the Act.
*
*
*
*
*
62. Appendix A to Part 70 is amended
as follows:
a. By revising the introductory text;
b. By adding paragraph (d) under
Alabama;
c. By adding paragraph (c) under
Alaska;
d. By adding paragraph (e) under
Arizona;
e. By adding paragraph (d) under
Arkansas;
f. By adding paragraph (jj) under
California;
g. By adding paragraph (c) under
Colorado;
h. By adding paragraph (c) under
Connecticut;
i. By adding paragraph (d) under
Delaware;
j. By adding paragraph (d) under
District of Columbia;
k. By adding paragraph (c) under
Florida;
l. By adding paragraph (c) under
Georgia;
m. By adding paragraph (d) under
Hawaii;
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n. By adding paragraph (c) under
Idaho;
o. By adding paragraph (c) under
Illinois;
p. By adding paragraph (d) under
Indiana;
q. By adding paragraph (k) under
Iowa;
r. By adding paragraph (e) under
Kansas;
s. By adding paragraph (c) under
Kentucky;
t. By adding paragraph (c) under
Louisiana;
u. By adding paragraph (c) under
Maine;
v. By adding paragraph (d) under
Maryland;
w. By adding paragraph (c) under
Massachusetts;
x. By adding paragraph (c) under
Michigan;
y. By adding paragraph (d) under
Minnesota;
z. By adding paragraph (c) under
Mississippi;
aa. By adding paragraph (x) under
Missouri;
bb. By adding paragraph (c) under
Montana;
cc. By adding paragraph (j) under
Nebraska, City of Omaha, LincolnLancaster County Health Department;
dd. By adding paragraph (d) under
Nevada;
ee. By adding paragraph (c) under
New Hampshire;
ff. By adding paragraph (e) under New
Jersey;
gg. By adding paragraph (g) under
New Mexico;
hh. By adding paragraph (e) under
New York;
ii. By adding paragraph (e) under
North Carolina;
jj. By adding paragraph (d) under
North Dakota;
kk. By adding paragraph (d) under
Ohio;
ll. By adding paragraph (c) under
Oklahoma;
mm. By adding paragraph (c) under
Oregon;
nn. By adding paragraph (c) under
Pennsylvania;
oo. By adding paragraph (c) under
Puerto Rico;
pp. By adding paragraph (c) under
South Carolina;
qq. By adding paragraph (c) under
Rhode Island;
rr. By adding paragraph (c) under
South Dakota;
ss. By adding paragraph (f) under
Tennessee;
tt. By adding paragraph (d) under
Texas;
uu. By adding paragraph (c) under
Utah;
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vv. By adding paragraph (c) under
Vermont;
ww. By adding paragraph (c) under
the Virgin Islands;
xx. By adding paragraph (c) under
Virginia;
yy. By adding paragraph (j) under
Washington;
zz. By adding paragraph (f) under
West Virginia;
aaa. By adding paragraph (c) under
Wisconsin; and
bbb. By adding paragraph (c) under
Wyoming.
Appendix A to Part 70—Approval of
State and Local Operating Permits
This appendix provides information on the
approval status of State and Local operating
Permit Programs. An approved State part 70
program applies to all part 70 sources, as
defined in that approved program, within
such State, except for any source of air
pollution over which a federally recognized
Indian Tribe has jurisdiction. EPA limits its
approval of the State permitting threshold
provisions to the extent those provisions
require permits for sources of GHG emissions
that equal or exceed 100 tpy CO2e.
Alabama
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Alaska
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Arizona
*
*
*
*
*
(e) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Arkansas
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
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California
*
*
*
*
*
(jj) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Colorado
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Connecticut
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Delaware
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
District of Columbia
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Florida
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Georgia
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
E:\FR\FM\27OCP2.SGM
27OCP2
Federal Register / Vol. 74, No. 206 / Tuesday, October 27, 2009 / Proposed Rules
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Hawaii
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Idaho
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Illinois
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Indiana
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Iowa
*
*
*
*
*
(k) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
pwalker on DSK8KYBLC1PROD with PROPOSALS2
Kansas
*
*
*
*
*
(e) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
VerDate Nov<24>2008
16:46 Oct 26, 2009
Jkt 220001
Kentucky
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Louisiana
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Maine
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Maryland
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Massachusetts
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Michigan
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Minnesota
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
PO 00000
Frm 00073
Fmt 4701
Sfmt 4702
55363
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Mississippi
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Missouri
*
*
*
*
*
(x) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Montana
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Nebraska; City of Omaha; Lincoln-Lancaster
County Health Department
*
*
*
*
*
(j) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Nevada
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
New Hampshire
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
E:\FR\FM\27OCP2.SGM
27OCP2
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Federal Register / Vol. 74, No. 206 / Tuesday, October 27, 2009 / Proposed Rules
New Jersey
*
*
*
*
*
(e) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
New Mexico
*
*
*
*
*
(g) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
New York
*
*
*
*
*
(e) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
North Carolina
*
*
*
*
*
(e) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
North Dakota
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Ohio
pwalker on DSK8KYBLC1PROD with PROPOSALS2
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Oklahoma
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
VerDate Nov<24>2008
16:46 Oct 26, 2009
Jkt 220001
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Oregon
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Pennsylvania
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Puerto Rico
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Rhode Island
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
South Carolina
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
South Dakota
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
PO 00000
Frm 00074
Fmt 4701
Sfmt 4702
Tennessee
*
*
*
*
*
(f) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Texas
*
*
*
*
*
(d) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Utah
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Vermont
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Virgin Islands
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Virginia
*
*
*
*
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Washington
*
*
*
*
*
(j) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
E:\FR\FM\27OCP2.SGM
27OCP2
Federal Register / Vol. 74, No. 206 / Tuesday, October 27, 2009 / Proposed Rules
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
West Virginia
PART 71—[AMENDED]
*
64. Section 71.2 is amended to
follows:
a. By adding definitions in
alphabetical order for carbon dioxide
equivalent and greenhouse gas;
b. By revising paragraph (2) of the
definition for major source; and
c. By adding paragraph (4) to the
definition for major source.
*
*
*
*
(f) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Wisconsin
*
*
*
*
*
*
*
*
pwalker on DSK8KYBLC1PROD with PROPOSALS2
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e
VerDate Nov<24>2008
16:46 Oct 26, 2009
Authority: 42 U.S.C. 7401, et seq.
§ 71.2
*
(c) Insofar as the State permitting threshold
provisions concern sources of GHG
emissions, EPA limits its approval of such
provisions to the extent they require permits
for sources of GHG emissions that equal or
exceed 25,000 tpy CO2e. EPA takes no action
on such provisions to the extent they require
permits for sources of GHG emissions that are
less than 25,000 tpy CO2e.
Wyoming
*
63. The authority citation for part 71
continues to read as follows:
Jkt 220001
Definitions.
*
*
*
*
*
Carbon dioxide equivalent, or CO2e,
means a metric used to compare the
emissions from various greenhouse
gases based upon their global warming
potential (GWP). The CO2e for a gas is
determined by multiplying the mass of
the gas by the associated GWP. The
applicable GWPs and guidance on how
to calculate a source’s GHG emissions in
tpy CO2e can be found in EPA’s
‘‘Inventory of U.S. Greenhouse Gas
Emissions and Sinks,’’ which is updated
annually under existing commitment
under the United Nations Framework
Convention on Climate Change
(UNFCCC).
*
*
*
*
*
PO 00000
Frm 00075
Fmt 4701
Sfmt 4702
55365
Greenhouse gas, or GHG, means
carbon dioxide (CO2), methane (CH4),
nitrous oxide (N2O), sulfur hexafluoride
(SF6), hydrofluorocarbons (HFCs), and
perfluorocarbons (PFCs).
*
*
*
*
*
Major source * * *
(2) A major stationary source of air
pollutants (except for greenhouse gases,
except as otherwise provided in this
section), as defined in section 302 of the
Act, that directly emits or has the
potential to emit, 100 tpy or more of any
air pollutant (including any major
source of fugitive emissions of any such
pollutant, as determined by rule by the
Administrator). The fugitive emissions
of a stationary source shall not be
considered in determining whether it is
a major stationary source for the
purposes of section 302(j) of the Act,
unless the source belongs to one of the
following categories of stationary
source:
*
*
*
*
*
(4) A stationary source that directly
emits, or has the potential to emit,
25,000 tpy CO2e or more of greenhouse
gases that are subject to regulation
under the Act.
*
*
*
*
*
[FR Doc. E9–24163 Filed 10–23–09; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\27OCP2.SGM
27OCP2
Agencies
[Federal Register Volume 74, Number 206 (Tuesday, October 27, 2009)]
[Proposed Rules]
[Pages 55292-55365]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-24163]
[[Page 55291]]
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Part II
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Parts 51, 52, 70, et al.
Prevention of Significant Deterioration and Title V Greenhouse Gas
Tailoring Rule; Proposed Rule
Federal Register / Vol. 74, No. 206 / Tuesday, October 27, 2009 /
Proposed Rules
[[Page 55292]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 51, 52, 70, and 71
[EPA-HQ-OAR-2009-0517; FRL-8966-7]
RIN 2060-AP86
Prevention of Significant Deterioration and Title V Greenhouse
Gas Tailoring Rule
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to tailor the major source applicability
thresholds for greenhouse gas (GHG) emissions under the Prevention of
Significant Deterioration (PSD) and title V programs of the Clean Air
Act (CAA or Act) and to set a PSD significance level for GHG emissions.
This proposal is necessary because EPA expects soon to promulgate
regulations under the CAA to control GHG emissions and, as a result,
trigger PSD and title V applicability requirements for GHG emissions.
If PSD and title V requirements apply at the applicability levels
provided under the CAA, State permitting authorities would be paralyzed
by permit applications in numbers that are orders of magnitude greater
than their current administrative resources could accommodate. On the
basis of the legal doctrines of ``absurd results'' and ``administrative
necessity,'' this proposed rule would phase in the applicability
thresholds for both the PSD and title V programs for sources of GHG
emissions. The first phase, which would last 6 years, would establish a
temporary level for the PSD and title V applicability thresholds at
25,000 tons per year (tpy), on a ``carbon dioxide equivalent''
(CO2e) basis, and a temporary PSD significance level for GHG
emissions of between 10,000 and 25,000 tpy CO2e. EPA would
also take other streamlining actions during this time. Within 5 years
of the final version of this rule, EPA would conduct a study to assess
the administrability issues. Then, EPA would conduct another
rulemaking, to be completed by the end of the sixth year, that would
promulgate, as the second phase, revised applicability and significance
level thresholds and other streamlining techniques, as appropriate.
DATES: Comments. Comments must be received on or before December 28,
2009. Under the Paperwork Reduction Act, comments on the information
collection provisions are best assured of having full effect if the
Office of Management and Budget (OMB) receives a copy of your comments
on or before November 27, 2009.
Public Hearing: If anyone contacts us requesting to speak at a
public hearing on or before November 16, 2009, we will hold a public
hearing approximately 30 days after date of publication in the Federal
Register.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2009-0517 by one of the following methods:
https://www.regulations.gov. Follow the online instructions
for submitting comments. Attention Docket ID No. EPA-HQ-OAR-2009-0517.
E-mail: a-and-r-docket@epa.gov. Attention Docket ID No.
EPA-HQ-OAR-2009-0517.
Fax: (202) 566-9744. Attention Docket ID No. EPA-HQ-OAR-
2009-0517.
Mail: EPA Docket Center, EPA West (Air Docket), Attention
Docket ID No. EPA-HQ-OAR-2009-0517, U.S. Environmental Protection
Agency, Mailcode: 2822T, 1200 Pennsylvania Avenue, NW., Washington, DC
20460. Please include a total of 2 copies. In addition, please mail a
copy of your comments on the information collection provisions to the
Office of Information and Regulatory Affairs, Office of Management and
Budget (OMB), Attn: Desk Officer for EPA, 725 17th Street, NW.,
Washington, DC 20503.
Hand Delivery: U.S. Environmental Protection Agency, EPA
West (Air Docket), 1301 Constitution Avenue, Northwest, Room 3334,
Washington, DC 20004, Attention Docket ID No. EPA-HQ-OAR-2009-0517.
Such deliveries are only accepted during the Docket's normal hours of
operation, and special arrangements should be made for deliveries of
boxed information.
Instructions. Direct your comments to Docket ID No. EPA-HQ-OAR-
2009-0517. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or e-mail. The https://www.regulations.gov Web site
is an ``anonymous access'' system, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an e-mail comment directly to EPA without
going through https://www.regulations.gov, your e-mail address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, EPA recommends that you include your name
and other contact information in the body of your comment and with any
disk or CD-ROM you submit. If EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, avoid any form of encryption, and be
free of any defects or viruses. For additional information about EPA's
public docket, visit the EPA Docket Center homepage at https://www.epa.gov/epahome/dockets.htm.
Docket. 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., 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
in https://www.regulations.gov or in hard copy at the Air and Radiation
Docket and Information Center, EPA/DC, EPA West Building, Room 3334,
1301 Constitution Ave., NW., Washington, DC. The Public Reading Room is
open from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding
legal 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: Mr. Joseph Mangino, Air Quality Policy
Division, Office of Air Quality Planning and Standards (C504-03),
Environmental Protection Agency, Research Triangle Park, NC 27711;
telephone number: (919) 541-9778; fax number: (919) 541-5509; e-mail
address: mangino.joseph@epa.gov.
To request a public hearing, please contact Pam Long, Air Quality
Planning Division, Office of Air Quality Planning and Standards (C504-
03), Environmental Protection Agency, Research Triangle Park, NC 27711;
telephone number: (919) 541-0641; fax number: (919) 541-5509 no later
than November 16, 2009 to request a hearing.
SUPPLEMENTARY INFORMATION:
[[Page 55293]]
I. Preamble Glossary of Terms and Abbreviations
The following are abbreviations of terms used in the preamble.
APA Administrative Procedure Act
ANPR Advance Notice of Proposed Rulemaking
APA Administrative Procedure Act
AQRV Air Quality Related Value
BACT Best Available Control Technology
CAA Clean Air Act
CAM Compliance Assurance Monitoring
CBI Confidential Business Information
CFR Code of Federal Regulations
CH4 Methane
CO2 Carbon Dioxide
CO2e Carbon Dioxide Equivalent
CO Carbon Monoxide
EG Emission Guidelines
EPA U.S. Environmental Protection Agency
FERC Federal Energy Regulatory Commission
FIP Federal Implementation Plan
FLM Federal Land Manager
FTC Federal Trade Commission
FTE Full-Time Equivalent
GHG Greenhouse Gas
GWP Global Warming Potential
HAP Hazardous Air Pollutant
HFC Hydrofluorocarbon
HFE Hydrofluorinated Ether
ICR Information Collection Request
IPCC Intergovernmental Panel on Climate Change
MWCs Municipal Waste Combustion Facilities
NAAQS National Ambient Air Quality Standard
NESHAP National Emission Standards for Hazardous Air Pollutants
NOD Notice of Deficiency
NOX Nitrogen Oxides
NSPS New Source Performance Standard
NSR New Source Review
OMB Office of Management and Budget
OTAQ Office of Transportation and Air Quality
PFC Perfluorocarbon
ppm Parts Per Million
PSD Prevention of Significant Deterioration
PTE Potential to Emit
RIA Regulatory Impact Analysis
SBA Small Business Administration
SO2 Sulfur Dioxide
SF6 Sulfur Hexafluoride
SIP State Implementation Plan
Tg Teragrams
TIP Tribal Implementation Plan
tpy Tons Per Year
UNFCCC United Nations Framework Convention on Climate Change
II. General Information
A. Does this action apply to me?
Entities affected by this proposed action include sources in all
sectors of the economy, including commercial and residential sources.
Entities potentially affected by this proposed action also include
States, local permitting authorities, and tribal authorities. The
majority of categories and entities potentially affected by this action
are expected to be in the following groups:
------------------------------------------------------------------------
Industry Group NAICS\a\
------------------------------------------------------------------------
Agriculture, fishing, and hunting...... 11.
Mining................................. 21.
Utilities (electric, natural gas, other 2211, 2212, 2213.
systems).
Manufacturing (food, beverages, 311, 312, 313, 314, 315, 316.
tobacco, textiles, leather).
Wood product, paper manufacturing...... 321, 322.
Petroleum and coal products 32411, 32412, 32419.
manufacturing.
Chemical manufacturing................. 3251, 3252, 3253, 3254, 3255,
3256, 3259.
Rubber product manufacturing........... 3261, 3262.
Miscellaneous chemical products........ 32552, 32592, 32591, 325182,
32551.
Nonmetallic mineral product 3271, 3272, 3273, 3274, 3279.
manufacturing.
Primary and fabricated metal 3311, 3312, 3313, 3314, 3315,
manufacturing. 3321, 3322, 3323, 3324, 3325,
3326, 3327, 3328, 3329.
Machinery manufacturing................ 3331, 3332, 3333, 3334, 3335,
3336, 3339.
Computer and electronic products 3341, 3342, 3343, 3344, 3345,
manufacturing. 4446.
Electrical equipment, appliance, and 3351, 3352, 3353, 3359.
component manufacturing.
Transportation equipment manufacturing. 3361, 3362, 3363, 3364, 3365,
3366, 3369.
Furniture and related product 3371, 3372, 3379.
manufacturing.
Miscellaneous manufacturing............ 3391, 3399.
Waste management and remediation....... 5622, 5629.
Hospitals/Nursing and residential care 6221, 6231, 6232, 6233, 6239.
facilities.
Personal and laundry services.......... 8122, 8123.
Residential/private households......... 8141.
Non-Residential (Commercial)........... Not available. Codes only exist
for private households,
construction and leasing/sales
industries.
------------------------------------------------------------------------
\a\ North American Industry Classification System.
B. Where can I get a copy of this document and other related
information?
In addition to being available in the docket, an electronic copy of
this proposal will also be available on the World Wide Web. Following
signature by the EPA Administrator, a copy of this action will be
posted on the EPA's New Source Review (NSR) Web site, under Regulations
& Standards, at https://www.epa.gov/nsr.
C. What should I consider as I prepare my comments for EPA?
1. Submitting CBI. Do not submit this information to EPA through
https://www.regulations.gov or e-mail. Clearly mark the part or all of
the information that you claim to be CBI. For CBI information in a disk
or CD ROM that you mail to EPA, mark the outside of the disk or CD ROM
as CBI and then identify electronically within the disk or CD ROM the
specific information that is claimed as CBI. In addition to one
complete version of the comment that includes information claimed as
CBI, a copy of the comment that does not contain the information
claimed as CBI must be submitted for inclusion in the public docket.
Information so marked will not be disclosed except in accordance with
procedures set forth in 40 CFR part 2. Send or deliver information
identified as CBI only to the following address: Roberto Morales, OAQPS
Document Control Officer (C404-02), U.S. EPA, Research Triangle Park,
NC 27711, Attention Docket ID No. EPA-HQ-OAR-2009-0517.
2. Tips for preparing your comments. When submitting comments,
remember to:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date and
page number).
Follow directions--The agency may ask you to respond to
specific questions or organize comments by referencing a
[[Page 55294]]
Code of Federal Regulations (CFR) part or section number.
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow for it to be
reproduced.
Provide specific examples to illustrate your concerns, and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline identified.
D. How can I find information about a possible public hearing?
People interested in presenting oral testimony or inquiring if a
hearing is to be held should contact Ms. Pamela S. Long, New Source
Review Group, Air Quality Policy Division (C504-03), U.S. EPA, Research
Triangle Park, NC 27711, telephone number (919) 541-0641. If a hearing
is to be held, persons interested in presenting oral testimony should
notify Ms. Long at least 2 days in advance of the public hearing.
Persons interested in attending the public hearing should also contact
Ms. Long to verify the time, date, and location of the hearing. The
public hearing will provide interested parties the opportunity to
present data, views, or arguments concerning these proposed rules.
E. How is the preamble organized?
The information presented in this preamble is organized as follows:
I. Preamble Glossary of Terms and Abbreviations
II. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document and other related
information?
C. What should I consider as I prepare my comments for EPA?
D. How can I find information about a possible public hearing?
E. How Is the preamble organized?
III. Overview of Proposed Rule
IV. Background
A. What are greenhouse gases and their sources?
B. What are the general requirements of the PSD program?
C. What are the general requirements of the title V operating
permits program?
D. What is the current treatment of GHG emissions under the
title V and PSD programs and what future actions may change that
treatment?
V. What would be the administrative burdens of implementing PSD and
title V at the current permitting thresholds?
A. PSD Implications
B. Title V Implications
C. ANPR Comments
VI. What is the legal rationale for this proposed Action?
A. ``Absurd Results'' Doctrine
B. ``Administrative Necessity'' Doctrine
C. Step-by-Step Process
D. What were the ANPR comments received on GHG tailoring options
for regulating GHG emissions under PSD and title V?
VII. Streamlining options and tools To address the administrative
burdens of PSD and title V for GHGs
A. Permit Streamlining Techniques for PSD and Title V
B. Implementation of Streamlining Techniques and Overall
Approach To Administering PSD and Title V Programs
C. Strategies for Obtaining GHG Reductions From Sources Under
the Proposed GHG Permit Thresholds
VIII. Description and Rationale of Proposed Action
A. Proposed Permitting Thresholds for GHGs
B. What is the definition of the GHG pollutant for the proposed
permitting thresholds?
C. What is the rationale for selecting the proposed GHG
permitting thresholds for PSD?
D. What is the rationale for selecting the proposed first-phase
GHG permitting threshold for title V?
E. how will EPA assess the GHG permitting thresholds in the
first phase of the tailoring program, and how will epa develop the
second phase?
IX. What would be the economic impacts of the proposed rule?
A. What entities are affected by this rule?
B. What are the estimated benefits to small sources due to
regulatory relief?
C. What are the economic impacts of this rulemaking?
D. What are the costs of the proposed rule for society?
X. What implementation issues are related to this proposal?
A. CAA Provisions Concerning SIP Requirements for PSD Programs,
State Submittal Requirements, and EPA Action
B. What PSD-Specific implementation considerations are there?
C. What title V-Specific implementation issues are there?
D. GHGs and title V permit fees
E. Implementation assistance and support
XI. Statutory and Executive Order Reviews
A. Executive Order 12866--Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
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 Concerning Regulations 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. Determination Under Section 307(d)
XII. Statutory Authority
III. Overview of Proposed Rule
EPA is proposing to tailor the major source applicability
thresholds for GHG emissions under the PSD and title V programs of the
CAA by setting first-phase levels under both programs, setting a first-
phase PSD significance level \1\ for GHG emissions, undertaking efforts
to streamline administrability of the programs, and committing to an
assessment of administrability within 5 years and a second-phase
rulemaking within 6 years.
---------------------------------------------------------------------------
\1\ ``Significant levels'' for regulated NSR pollutants are
commonly called ``significance levels'' or ``significance
thresholds,'' and these terms are used interchangeably for purposes
of this proposed action.
---------------------------------------------------------------------------
This proposal is necessary because EPA expects soon to promulgate
regulations under the CAA to control GHG emissions from light-duty
motor vehicles and, as a result, trigger PSD and title V applicability
requirements for GHG emissions. When the light-duty vehicle rule is
finalized, the GHGs subject to regulation under that rule would become
immediately subject to regulation under the PSD program, meaning that
from that point forward, prior to constructing any new major source or
major modifications that would increase GHGs, a source owner would need
to apply for, and a permitting authority would need to issue, a permit
under the PSD program that addresses these increases. Similarly, for
title V it would mean that any new or existing source exceeding the
major source applicability level for those regulated GHGs, if it did
not have a title V permit already, would have 1 year to submit a title
V permit application.
If PSD and title V requirements apply at the applicability levels
provided under the CAA, many small sources would be burdened by the
costs of individualized PSD control technology requirements and permit
applications. In addition, State permitting authorities would be
paralyzed by enormous numbers of these permit applications; the numbers
are orders of magnitude greater than the current inventory of permits
and would vastly exceed the current administrative resources of the
permitting authorities. Based on the long-established judicial
doctrines of
[[Page 55295]]
``absurd results'' and ``administrative necessity,'' this proposed rule
would phase in PSD and title V applicability. As the first phase, this
rule would establish applicability thresholds for both the PSD and
title V programs at the level of 25,000 tpy CO2e, and would
establish a PSD significance level of between 10,000 and 25,000 tpy
CO2e. This rule also marks the beginning of a concerted
effort by EPA to streamline administration of the PSD and title V
programs as much as possible and as quickly as possible. In addition,
EPA commits that, within 5 years of promulgating the first phase, EPA
will conduct a study of the permitting authorities' ability to
administer the programs going forward, and then, within a year, conduct
rulemaking for the second phase of the program. This second phase will
either confirm the first-phase permitting levels or establish revised
ones or other streamlining techniques. EPA also proposes to identify as
the pollutant subject to PSD and title V for applicability purposes the
group of up to six GHG emissions, each one weighted for its global
warming potential, that are included in regulations for their control
under the CAA. EPA also proposes to conform its action on PSD State
implementation plans (SIPs) and title V programs to match the proposed
Federal applicability requirements.
More specifically, following this overview, section IV of this
preamble provides background information as to the nature of GHG
emissions and the general requirements of the PSD and title V programs.
Currently, PSD applies to sources that emit at least 100 or 250
(depending on the source category) tpy of pollutants subject to
regulation under the CAA, and title V generally applies to sources that
emit at least 100 tpy of pollutants subject to regulation under the
CAA. Currently, PSD and title V requirements apply on the basis of
emissions applicability thresholds that are pollutant-specific mass
emissions rates expressed in tpy. Under PSD, construction of a
stationary source that has the potential to emit (PTE) a regulated NSR
pollutant in an amount exceeding 100 or 250 tpy (depending on the
source category) (the ``major stationary source'' threshold, in the
terminology of EPA regulations) triggers PSD permitting requirements.
PSD permitting requirements are also triggered if a major stationary
source undertakes a modification that is projected to increase
emissions of a regulated NSR pollutant above an emissions threshold
(the ``significance level''). For any particular pollutant, this level
is zero unless and until EPA establishes one on the basis of de minimis
emissions or administrative necessity. Under title V, a source with
emissions exceeding a ``major source'' emissions threshold--generally
100 tpy on a PTE basis--triggers title V permitting requirements.
It should be noted that, as further explained in the background
section, there are no geographic areas currently designated
``nonattainment'' for GHG pollutants; as a result, this action affects
only the PSD program, and we are not proposing to amend the
``nonattainment NSR'' provisions of our major NSR program at this time,
nor are we proposing to amend any provisions that affect minor NSR
permitting.
Section IV of this preamble further describes the current and
expected future treatment of GHG emissions for applicability purposes
under those PSD and title V programs. In particular, section IV
describes the light-duty motor vehicle rule, which EPA recently
proposed and expects to promulgate by the end of March 2010, and which
will control GHG emissions from certain mobile sources. Under EPA's
current interpretation of PSD and title V applicability requirements,
promulgation of this motor vehicle rule will trigger the applicability
of PSD and title V requirements for stationary sources that emit GHGs.
In section V of this preamble, EPA describes the administrative
burdens on permitting authorities if the requirements of PSD and title
V programs are triggered without having this tailoring rule in place.
In short, without this tailoring rule, the administrative burdens would
be immense, and they would immediately and completely overwhelm the
permitting authorities. Without this tailoring rule, permitting
authorities would receive approximately 40,000 PSD permit applications
each year--currently, they receive approximately 300--and they would be
required to issue title V permits for approximately some six million
sources--currently, their title V inventory is some 15,000 sources.
These increases are measured in orders of magnitude. We estimate the
additional resource burdens in full-time equivalents (FTEs) and time
delays in processing permits, but the sheer numbers of additional
permits by themselves paint the picture of the overwhelming
administrative burdens.
In section VI of this preamble, we describe the legal rationale for
this tailoring rule. The judicial doctrine of ``absurd results''
authorizes departure from a literal application of statutory provisions
if it would produce a result that is inconsistent with other statutory
provisions or congressional intent, and particularly one that would
undermine congressional purposes. The judicial doctrine of
``administrative necessity'' authorizes an agency to depart from
statutory requirements if the agency can demonstrate that the statutory
requirements, as written, are impossible to administer. However, the
agency must first attempt to mitigate administrative problems through
techniques consistent with the statutory requirements, and, if variance
from the statutory requirements nevertheless is necessary to allow
administrability, the variance must be limited as much as possible.
As discussed in section VI of this preamble, to apply the statutory
PSD and title V applicability thresholds to sources of GHG emissions
would bring tens of thousands of small sources and modifications into
the PSD program each year, and millions of small sources into the title
V program. This extraordinary increase in the scope of the permitting
programs, coupled with the resulting burdens on the small sources and
on the permitting authorities, were not contemplated by Congress in
enacting the PSD and title V programs. Moreover, the administrative
strains would lead to multi-year backlogs in the issuance of PSD and
title V permits, which would undermine the purposes of those programs.
Sources of all types--whether they emit GHGs or not--would face long
delays in receiving PSD permits, which Congress intended to allow
construction or expansion. Similarly, sources would face long delays in
receiving title V permits, which Congress intended to promote
enforceability. For these reasons, the absurd results doctrine applies
to avoid a literal application of the thresholds.
By the same token, the impossibility of administering the permit
programs brings into play the administrative necessity doctrine. This
doctrine also justifies EPA to avoid a literal application of the
threshold provisions.
Instead, these doctrines authorize EPA to apply the PSD and title V
applicability provisions through a phased program. The first phase
would establish the applicability thresholds at the 25,000-tpy levels
and vigorously develop streamlining measures that would facilitate
applying PSD and title V on a broader scale with overburdening sources
and administrators. In this manner, the phased approach reconciles the
language of the statutory provisions with the results of their
application and with congressional intent.
[[Page 55296]]
In section VII of this preamble, we describe the streamlining
techniques--short of limiting the applicability of PSD and title V to
higher-emitting sources--that may be available to improve
administrability. These techniques range from defining ``potential to
emit''--which is the basis for calculating the statutory thresholds--to
be closer to actual emissions, to general permits and presumptive best
available control technology (BACT), which is the principal control
requirement under the PSD program. Although these techniques offer
promise over the long term to improve administrability, they cannot be
in place by March 2010, when we expect PSD and title V requirements to
be triggered for GHG emitters, or within a several-year period
thereafter. Accordingly, this tailoring rule is necessary at this time.
In section VIII of this preamble, we describe in detail our
proposed tailoring rule. For the PSD program, we are proposing to
establish, as the first phase, the GHG ``major stationary source''
emissions applicability threshold level at 25,000 tpy on a
CO2e basis. That is, sources that emit at this level or
higher would be considered ``major stationary sources'' and therefore
would become subject to PSD requirements when they construct or modify.
We are also proposing to establish in this first phase a PSD
``significance level'' emissions rate for GHGs and are proposing a
range for that value of 10,000 to 25,000 tpy CO2e for
comment. The ``significance'' level is important for determining
whether existing sources that make physical or operational changes
become subject to PSD and for determining whether sources that are
subject to PSD for other pollutants are also subject to PSD for their
GHG emissions.
As further described in section VIII of this preamble, for the
title V operating permits program, we are also proposing to establish
the GHG emissions applicability threshold level at 25,000 tpy
CO2e for this first phase. That is, sources that emit at
this level or higher would be considered ``major sources'' and
therefore would become subject to title V requirements.
As further described in section VIII of this preamble, as an
integral part of the tailoring rule, EPA proposes to commit to
complete, within 5 years of a final rule, a study to evaluate the
actual administrative burden resulting from the proposed GHG permitting
thresholds and possible other thresholds, and the progress of
developing streamlining techniques and augmentation of permitting
authorities' resources. In addition, EPA commits to propose and
promulgate a rulemaking--informed by the study--within 6 years from the
effective date of a final version of this rulemaking (i.e., 1 year from
the completion of the study) that would establish the second phase,
which would either reaffirm the GHG permitting thresholds, promulgate
alternative thresholds, adopt other streamlining techniques, and/or
take other action consistent with the goal of expeditiously meeting CAA
requirements in light of the administrative burden that remains at that
time.
During this first phase of the tailoring program, EPA proposes to
make a concerted effort to assess and implement streamlining options,
tools, and guidance--some of which we describe in section VII of this
preamble--to reduce the administrative burden on permitting authorities
when implementing PSD and title V for GHGs. EPA proposes to undertake
as many of these streamlining actions as possible and to do so as
quickly as possible. In addition, for larger sources that would be
subject to PSD and title V requirements during the first phase, EPA
intends to work closely with the stakeholders to develop efficient
methods for implementing those requirements. For smaller sources for
which PSD and title V requirements would not apply during the first
phase due to the increase in the major source applicability threshold,
EPA intends to identify cost-effective opportunities available as soon
as possible to achieve GHG reductions through means other than PSD and
title V (e.g., energy efficiency and other appropriate measures).
Section VIII of this preamble further describes our proposal to
define the relevant pollutants as the group of up to six GHG emissions
that have been regulated for control, calculated on the basis of global
warming potential (GWP).\2\
---------------------------------------------------------------------------
\2\ The Intergovernmental Panel on Climate Change (IPCC)
describes GWP as an index, based upon radiative properties of well-
mixed GHGs, measuring the radiative forcing of a unit mass of a
given well-mixed greenhouse gas in the present-day atmosphere
integrated over a chosen time horizon, relative to that of
CO2. The GWP represents the combined effect of the
differing times these gases remain in the atmosphere and their
relative effectiveness in absorbing outgoing thermal infrared
radiation. (Intergovernmental Panel on Climate Change (IPCC),
Glossary of Terms used in the IPCC Fourth Assessment Report, WG1).
https://www.ipcc.ch/
---------------------------------------------------------------------------
Section IX of this preamble describes the burden and economic
impacts of the proposed rule.
Section X of this preamble discusses implementation issues related
to this proposal. These include conforming EPA approval of the PSD
programs in SIPs and EPA approval of the State title V programs to be
consistent with the proposed applicability threshold levels. By way of
background, as soon as EPA promulgates a rule regulating for control of
GHG emissions--which we expect to occur with the proposed light-duty
motor vehicle rule, scheduled for promulgation at the end of March
2010--stationary sources will become subject to PSD and title V
requirements. The major source thresholds for PSD and title V,
significance level for PSD, and identification of GHGs subject to PSD
and title V as proposed in this tailoring rule would each take effect
immediately in the Federal PSD program (codified at 40 CFR 52.21) and
in the Federal operating permits program (codified at 40 CFR 71), as
applicable. To conform EPA action on PSD SIPs and State title V
programs, EPA intends to limit its previous approval of those SIPs and
title V programs to cover only the permitting of sources of GHG
emissions at or above the proposed threshold levels. EPA will take no
action on--that is, EPA will not disapprove--the PSD SIPs and title V
programs to the extent they require permitting of GHG emitters at
levels below the proposed thresholds. EPA proposes to take this action
by virtue of its authority to reconsider its previous regulatory
actions. Section X of this preamble also explains how we propose to
address the treatment of GHGs in the fee programs under title V.
IV. Background
A. What are greenhouse gases and their sources?
Gases that trap heat in the atmosphere are often called GHGs. Some
GHGs such as carbon dioxide (CO2) are emitted to the
atmosphere through natural processes as well as human activities. Other
gases, such as fluorinated gases, are created and emitted solely
through human activities. The primary GHGs of concern directly emitted
by human activities include CO2, methane (CH4),
nitrous oxide (N2O), hydrofluorocarbons (HFCs),
perfluorocarbons (PFCs), and sulfur hexafluoride (SF6).
These six primary GHGs will, for the purposes of this proposal, be
referred to collectively as ``the six primary GHGs.'' These six gases,
once emitted, remain in the atmosphere for decades to centuries. Thus,
they become well-mixed globally in the atmosphere and their
concentrations accumulate when emissions exceed the rate at which
natural processes remove them from the atmosphere. The heating effect
caused by the human-induced buildup of GHGs
[[Page 55297]]
in the atmosphere is very likely the cause of most of the observed
global warming over the last 50 years. A detailed explanation of
climate change and its impact on health, society, and the environment
is included in EPA's technical support document for the endangerment
finding proposal (Docket ID No. EPA-HQ-OAR-2009-0171-0137).\3\
---------------------------------------------------------------------------
\3\ ``Document for Endangerment and Cause or Contribute Findings
for Greenhouse Gases under Section 202(a) of the Clean Air Act,''
Climate Change Division, Office of Atmospheric Programs, U.S.
Environmental Protection Agency, Washington, DC. April 17, 2009.
---------------------------------------------------------------------------
In the U.S., the combustion of fossil fuels (e.g., coal, oil, gas)
is the largest source of CO2 emissions and accounts for 80
percent of total GHG emissions. More than half the energy-related
emissions come from large stationary sources such as power plants,
while about a third come from transportation. Of the six primary GHGs,
four (CO2, CH4, N2O, and HFCs) are
emitted by motor vehicles. Industrial processes (such as the production
of cement, steel, and aluminum), agriculture, forestry, other land use,
and waste management are also important sources of GHG emissions in the
U.S. These emissions are inventoried at a national level by EPA in the
Inventory of U.S. Greenhouse Gas Emissions and Sinks.\4\
---------------------------------------------------------------------------
\4\ For additional information about the Inventory of U.S.
Greenhouse Gas Emissions and Sinks, and for more information about
GHGs, climate change, climate science, etc., see EPA's climate
change Web site at https://www.epa.gov/climatechange/.
---------------------------------------------------------------------------
Different GHGs have different heat-trapping capacities. It is
useful to compare them to each other through the use of the
CO2e metric. This metric incorporates both the heat-trapping
ability and atmospheric lifetime of each GHG and can be used to adjust
the quantities, in tpy, of all GHGs relative to the GWP of
CO2. When quantities of the different GHGs are multiplied by
their GWPs, the different GHGs can be summed and compared on a
CO2e basis. Depending on which GWP values are used, the
calculated GHG emissions on a CO2e basis will vary.
Throughout this preamble, we are applying the GWP values established by
the Intergovernmental Panel on Climate Change (IPCC) in its Second
Assessment Report (SAR) (IPCC 1996).\5\ For example, CH4 has
a GWP of 21, meaning each ton of CH4 emissions would have 21
times as much impact on global warming over a 100-year time horizon as
1 ton of CO2 emissions. Thus, on the basis of heat-trapping
capability, 1 ton of CH4 would equal 21 tons of
CO2e. The GWPs of the six primary GHGs range from 21 (for
CH4) up to 23,900 (for SF6). Aggregating all GHGs
on a CO2e basis at the source level allows a facility to
evaluate its total GHG emissions contribution based on a single metric.
For a complete list of the applicable GWP values for each GHG, please
refer to EPA's Inventory of U.S. Greenhouse Gas Emissions and Sinks.
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\5\ ``Inventory of U.S. Greenhouse Gas Emissions and Sinks:
1990-2007,'' U.S. Environmental Protection Agency, EPA 430-R-09-004,
April 15, 2009. Table 1-2, p. 1-6. https://www.epa.gov/climatechange/emissions/usinventoryreport.html.
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B. What are the general requirements of the PSD program?
1. Overview of the PSD Program
The PSD program is a preconstruction review and permitting program
applicable to ``new major stationary sources'' and ``major
modifications'' at existing major stationary sources, in the
terminology of EPA's implementing regulations. The PSD program applies
in areas meeting the health-based National Ambient Air Quality
Standards (NAAQS) or for which there is insufficient information to
determine whether they meet the NAAQS (``unclassifiable'' areas). The
PSD program is contained in part C of title I of the CAA. The
``nonattainment NSR'' program applies in areas not meeting the NAAQS
and in the Ozone Transport Region, and is implemented under the
requirements of part D of title I of the CAA. Collectively, we also
commonly refer to these two programs as the major NSR program. The
governing EPA rules are contained in 40 CFR 51.165, 51.166, 52.21,
52.24, and part 51, appendices S and W. There is no NAAQS for
CO2 or any of the other primary GHGs, nor does EPA plan to
promulgate one; therefore, we do not anticipate that the
``nonattainment'' major NSR program will apply to GHGs.
The applicability of the PSD program to a particular source must be
determined in advance of construction or modification and is pollutant-
specific. The primary criterion in determining PSD applicability is
whether the proposed project is sufficiently large (in terms of its
emissions) to be a major stationary source or major modification, both
of which are described below.
a. Major Stationary Sources
Under PSD, a ``major stationary source'' is any source type
belonging to a specified list of 28 source categories which emits or
has a PTE of 100 tpy or more of any pollutant subject to regulation
under the CAA, or any other source type which emits or has the
potential to emit such pollutants in amounts equal to or greater than
250 tpy. See, e.g., 40 CFR 52.21(b)(1). We may refer to these levels as
the 100/250-tpy thresholds. A new source with a PTE at or above the
applicable ``major stationary source threshold'' amount is subject to
major NSR. These limits originate from section 169 of the CAA, which
applies PSD to any ``major emitting facility'' \6\ and defines the term
to include any source with a PTE of 100 or 250 tpy, depending on source
category.
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\6\ EPA's regulations employ the term ``major stationary
source'' in lieu of ``major emitting facility.'' e.g., 40 CFR
52.21(a)(2)(i), (b)(1)(i).
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b. Major Modifications
PSD applies to not only new construction but also to existing
sources that undertake a ``major modification,'' which is defined in
terms of the following three criteria:
(1) A physical change in, or change in the method of operation of,
a ``major stationary source'' must occur;
(2) The change must result in an increase in emissions that is
``significant,'' that is, equal to or above the significance level
defined for the pollutant in question, e.g., in 40 CFR 52.21(b)(23));
and
(3) The increase in emissions resulting from the change must be a
significant net emissions increase. In other words, when the increase
from the project is added to other contemporaneous increases or
decreases in actual emissions at the source, the net emissions increase
must be significant (equal to or above the significance level defined,
e.g., in 40 CFR 52.21(b)(23)).
Generally, significance levels for PSD are pollutant-specific
emissions rates. For example, the significance level for emissions of
nitrogen oxides (NOX) is 40 tpy. See, e.g., 40 CFR
52.21(b)(23)(i). However, for a regulated NSR pollutant for which no
specific significance level is listed, PSD applies to ``any increase.''
See, e.g., 40 CFR 52.21(b)(23)(ii). Thus, if GHGs were to become
subject to regulation and PSD review, and no significance levels for
GHGs had been established, the default value would be ``zero.''
EPA has promulgated significance levels for criteria pollutants and
certain other pollutants, which EPA generally based on levels that
represent a de minimis contribution to air quality problems. For
example, for certain pollutants regulated under the new source
performance standards (NSPS), EPA generally based significance levels
at 20 percent of the NSPS. These concentrations were compared to
available health and welfare data to assure that significant adverse
effects
[[Page 55298]]
were avoided.\7\ To this point, EPA has not established a significance
level for GHGs, and we currently do not have an adequate supporting
record to establish a similar health and welfare-based de minimis level
for significance for GHGs.
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\7\ EPA established significance levels for hazardous air
pollutants on a similar basis, but subsequently, in the 1990 Clean
Air Act Amendments, Congress mooted them by exempting hazardous air
pollutants from PSD, under CAA section 112(b)(6).
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2. General Requirements for PSD
Under the PSD program, one of the principal requirements is that a
new major source or major modification must apply BACT, which is
determined on a case-by-case basis taking into account, among other
factors, the cost and effectiveness of the control. EPA has developed a
``top-down'' approach for BACT review which involves a decision process
that includes identification of all available control technologies,
elimination of technically infeasible options, ranking of remaining
options by control and cost effectiveness, and then selection of BACT.
Under PSD, once a source is determined to be major for any regulated
pollutant, a BACT review is performed for each attainment pollutant
whose emissions exceed its PSD significance level as part of new
construction or modification projects at the source.
In addition to performing a BACT review, the source must analyze
the impact of the project on ambient air quality to assure that no
violation of any NAAQS or PSD increments will result, and must analyze
impacts on soil, vegetation, and visibility. Sources or modifications
that would impact Class I areas (e.g., national parks) may be subject
to additional requirements to protect air quality related values
(AQRVs) that have been identified for such areas. Under PSD, if a
source proposes to locate within 100 kilometers of a Class I area, the
Federal Land Manager (FLM) is notified and is responsible for
evaluating a source's projected impact on the AQRVs and recommending
either approval or disapproval of the source's permit application based
on anticipated impacts. There are currently no NAAQS or PSD increments
established for GHGs, and therefore these PSD requirements would not
apply to GHG emissions sources, even when PSD is triggered for GHG
emissions sources. However, as noted previously, if PSD is triggered
for a GHG emissions source, all regulated NSR pollutants which the new
source emits in significant amounts would be subject to PSD
requirements. Therefore, if a facility triggers review for regulated
NSR pollutants that are non-GHG pollutants for which there are
established NAAQS or increments, the air quality, additional impacts,
and Class I requirements would apply to those pollutants.
When the reviewing authority reaches a preliminary decision to
authorize construction of a proposed new major source or major
modification, it must provide notice of the preliminary decision and an
opportunity for comment by the general public, industry, and other
interested persons. After considering and responding to the comments,
the reviewing authority may issue a final determination on the
construction permit in accordance with the PSD regulations.
Usually NSR permits are issued by State or local air pollution
control agencies. In these cases, State and local air pollution control
agencies may have their own permit programs that are approved by EPA in
the SIP or they may be delegated the authority to issue permits on
behalf of EPA. In some areas, the EPA issues the permits.
3. Minor NSR Program
The permitting program for minor stationary sources is addressed by
section 110(a)(2)(C) of the CAA. We commonly refer to this program as
the minor NSR program. A minor stationary source means a source whose
PTE is lower than the major source applicability threshold for a
particular pollutant as defined in the applicable nonattainment major
NSR program or PSD program. As with nonattainment NSR requirements, the
CAA does not require that minor source programs apply to GHGs because
there are no NAAQS for GHGs.
C. What are the general requirements of the title V operating permits
program?
1. Overview of Title V
The title V operating permits program was added to the CAA by
Congress in 1990. The operating permits program requirements under
title V are intended to improve sources' compliance with the
requirements of the CAA. In summary, the title V program requires major
sources (generally defined as sources that actually emit or have the
potential to emit 100 tpy) and certain other sources to obtain
operating permits that: Consolidate all CAA requirements into a single
document; provide for review of these documents by EPA, States, and the
public; and require permit holders to track, report, and annually
certify their compliance status with respect to their permit
requirements.
Title V will be triggered for GHG emissions when EPA regulates them
for control under another provision of the CAA. Section 502(a) of the
Act sets forth the sources required to obtain operating permits under
title V. These sources include: (1) Any affected source subject to acid
rain rules under title IV of the Act; (2) any major source; (3) any
source required to have a permit under part C or D (PSD/NSR) of title I
of the Act; (4) ``any source subject to section 111 [NSPS] or section
112 [NESHAP];'' and (5) any other source designated by rule. See also
40 CFR 70.3(a) and 71.3(a). The requirements of section 502(a) are
primarily implemented through the operating permit program rules at 40
CFR part 70, which sets out the minimum requirements for title V
operating permit programs administered by State, local, and tribal
permitting authorities (57 FR 32261; July 21, 1992); and part 71, the
Federal operating permit program requirements that apply where EPA or a
delegate agency authorized by EPA to carry out a Federal permit program
is the title V permitting authority (61 FR 34228, July 1, 1996).
Title V generally does not add new substantive requirements for
pollution control, but it does require that each permit contain all of
a facility's ``applicable requirements'' under the CAA, and that
certain procedural requirements be followed, especially with respect to
compliance with these requirements. ``Applicable requirements'' for
title V purposes include all stationary source requirements, but do not
include mobile source requirements.
2. Title V Permit Requirements
When a source becomes subject to title V, it must apply for a
permit within 1 year of the date it became subject. The application
must include identifying information, a description of emissions and
other information necessary to determine applicability of CAA
requirements, identification and certification of the source's
compliance status with these requirements (including a schedule to come
into compliance for any requirements for which the source is currently
out of compliance), a statement of the methods for determining
compliance, and other information. The permitting authority then uses
this information to issue the source a permit to operate, as
appropriate. A title V source may not operate without a permit, except
that if it has submitted a complete application, the submission acts as
a ``shield'' that
[[Page 55299]]
authorizes it to operate while awaiting issuance of its permit.
Title V permits must contain the following main elements: (1)
Emissions standards to assure compliance with all applicable
requirements; (2) a duration of no more than 5 years, after which the
permit must be renewed; (3) monitoring, recordkeeping, and reporting
requirements necessary to assure compliance, including a semiannual
report of all required monitoring and a prompt report of each deviation
from a permit term; (4) provisions for payment of permit fees as
established by the permitting authority such that total fees collected
are adequate to cover the costs of developing and implementing the
program; and (5) a requirement for an annual compliance certification
by a responsible official at the source. An additional specific
monitoring requirement, compliance assurance monitoring (CAM), also
applies to some emissions units operating at major sources with title V
permits. The CAM rule requires source owners to design and conduct
monitoring of the operation of add-on control devices used to control
emissions from moderately large emissions units. Source owners use the
monitoring data to evaluate, verify, and certify the compliance status
for applicable emissions limits. The CAM rule is implemented in
conjunction with the schedule of the operating permits program. While
these are the main elements relevant to a discussion of GHGs, there are
numerous other permit content requirements and optional elements, as
set forth in the title V regulations at 40 CFR 70.6.
In addition to the permit content requirements, there are
procedural requirements that permitting authorities (typically States)
must follow in issuing title V permits, including (1) determining and
notifying the applicant that its application is complete; (2) providing
public notice and a 30-day public comment period on the draft permit,
as well as the opportunity for a public hearing; (3) giving notice to
EPA and affected States; and (4) preparing and providing to any
requester a statement of the legal and factual basis of the draft
permit. The permitting authority must take final action on permit
applications within 18 months of receipt. EPA also has 45 days from
receipt of a proposed permit to object to its issuance, and citizens
have 60 days to petition EPA to object. Permits may also need to be
revised or reopened if new requirements come into effect or if the
source makes changes that conflict with, or necessitate changes to, the
current permit. Permit revisions and reopenings follow procedural
requirements which vary depending on the nature of the necessary
changes to the permits.
D. What is the current treatment of GHG emissions under the title V and
PSD programs and what future actions may change that treatment?
This section of the preamble describes the current treatment of GHG
emissions under the PSD and title V programs--under which GHG emissions
are not included for purposes of determining applicability--including
recent regulatory and legal developments related to this action, and
then describes what future action may change that treatment.
1. Regulation of GHGs Under the CAA
a. The Massachusetts U.S. Supreme Court Decision
On April 2, 2007, in Massachusetts v. EPA, 549 U.S. 497 (2007), the
U.S. Supreme Court held that GHGs are air pollutants covered by the
CAA. Therefore, the Court further held that GHG emissions are subject
to CAA section 202(a) under which the Administrator must determine
whether or not emissions of GHGs from new motor vehicles or motor
vehicle engines cause or contribute to air pollution which may
reasonably be anticipated to endanger public health or welfare, or
whether the science is too uncertain to make a reasoned decision. This
decision resulted from a petition for rulemaking under section 202(a)
filed by more than a dozen environmental, renewable energy, and other
advocacy organizations. As a result of this decision, EPA decided to
issue an advance notice of proposed rulemaking (ANPR), discussed later
in this preamble, soliciting comment on how GHG emissions should be
regulated under the CAA.
b. The EPA ANPR
On July 30, 2008, EPA published an ANPR in the Federal Register
entitled, ``Regulating Greenhouse Gas Emissions under the CAA.'' 73 FR
44354, July 30, 2008. This ANPR presented information relevant to, and
solicited public comment on how to respond to, the U.S. Supreme Court's
decision in Massachusetts v. EPA, holding that GHGs are air pollutants
subject to the CAA. The notice reviewed the various CAA provisions
(including the PSD and title V requirements) that may be applicable to
sources of GHGs, examined the issues that regulating GHGs under those
provisions may raise, provided information regarding potential
regulatory approaches and technologies for reducing GHG emissions, and
raised issues relevant to possible legislation and the potential for
overlap between legislation and CAA regulation.
In addition, the notice described and solicited comment on
petitions the EPA had received to regulate GHG emissions from ships,
aircraft, and nonroad vehicles such as farm and construction equipment.
Finally, the notice discussed several other actions concerning
stationary sources for which EPA has received comment regarding the
regulation of GHG emissions, including promulgation of performance
standards or guidelines under CAA section 111 for new and existing
sources in various source categories. The EPA included options for
phasing in the PSD program and title V programs to mitigate burdens
that would occur if GHGs were to be regulated under the CAA and
solicited comments on those actions. Section V.C of this preamble
summarizes some of the substantive comments received on the ANPR. In
issuing the ANPR, EPA made clear that it believed that the best way to
address the problems posed by GHG emissions would be through
legislation directly addressing GHG emissions, rather than through use
of the tools in the CAA.
2. Current Applicability of the PSD Program to Sources of GHG Emissions
As explained earlier in this preamble, EPA treats sources as
subject to PSD requirements only if they emit ``regulated NSR
pollutants'' at specified threshold levels. Currently, EPA does not
consider GHG emissions to be ``regulated NSR pollutants'' under the PSD
program because GHG emissions have not, thus far, been subject to
regulation requiring control under the CAA. As discussed later in this
preamble, EPA is in the process of reviewing its approach to PSD
applicability and is in the process of developing a rulemaking--the
light-duty motor vehicle rule--that will trigger PSD applicability for
GHG emissions.
a. PSD Interpretive Memorandum
EPA is currently reconsidering the PSD Interpretive Memorandum
(previously referred to as the ``Johnson Memorandum''), which describes
the circumstances under which EPA considers a pollutant subject to PSD
requirements. See memorandum (in docket for this rulemaking) from
Administrator Stephen L. Johnson to Regional Administrators, ``EPA's
Interpretation of Regulations that Determine Pollutants Covered by
Federal Prevention of Significant Deterioration (PSD) Permit Program,''
December 18, 2008. The PSD
[[Page 55300]]
Interpretive Memorandum followed a decision by the Environmental
Appeals Board (EAB) in In re Deseret Power Electric Cooperative, on
November 13, 2008. PSD Appeal No. 07-03 (EAB 2008) (In re Deseret).
There, the Board remanded a PSD permit that EPA Region VIII issued on
August 30, 2007, to Deseret Power Electric Cooperative, authorizing the
latter to construct a new waste-coal-fired electric generating unit
near its existing Bonanza Power Plant, in Bonanza, Utah. The primary
issue before the Board was whether the permit had to include BACT
limits for CO2, which depended on whether CO2
meets the definition of a ``regulated NSR pollutant'' under 40 CFR
52.21(b)(50), which in turn interprets the provisions in CAA sections
165 and 169 that apply the BACT requirement to ``each pollutant subject
to regulation'' under the CAA. The Board rejected arguments by the
petitioner, the Sierra Club, that the CAA compelled a broad
interpretation of the phrase ``subject to regulation,'' which,
according to the petitioner, required EPA to apply BACT to pollutants
as long as they are subject to monitoring and reporting requirements.
Currently, and since 1993, sources covered by the Acid Rain program
have been required to monitor and report CO2 emissions
pursuant to the CAA. The Board also rejected the view advanced by the
EPA offices involved in the case--Region VIII and the Office of Air and
Radiation--that EPA had already established an interpretation of
``subject to regulation,'' which was that this term authorized BACT
only for pollutants subject to actual regulatory controls. Thus, the
Board remanded the permit to the Region to ``reconsider whether or not
to impose a CO2 BACT limit in light of the `subject to
regulation' definition under the CAA.'' In re Deseret, slip op. at 63.
On December 18, 2008, EPA's then-Administrator Stephen Johnson
issued a memorandum establishing an interpretation clarifying the scope
of the PSD program under the CAA (the PSD Interpretive Memorandum).
This memorandum interprets the definition of ``regulated NSR
pollutant'' to include each pollutant subject to either a provision in
the CAA or regulation adopted by EPA under the CAA that requires actual
control of emissions of that pollutant, and to exclude pollutants for
which EPA regulations only require monitoring or reporting.
On February 17, 2009, EPA Administrator Lisa Jackson responded to
an amended petition for reconsideration dated January 6, 2009, filed on
behalf of the Sierra Club and other parties (petitioners), seeking
reconsideration of the PSD Interpretive Memorandum. In Administrator
Jackson's response, she granted the petition for reconsideration in
order to allow for public comment on issues raised in the memorandum
and stated that EPA will also seek public comment on any issues raised
by the opinion of the EAB with regard to the In re Deseret decision (as
discussed in the PSD Interpretive Memorandum), to the extent they are
not coextensive with the issues raised in the memorandum. However,
Administrator Jackson made clear that the current interpretations in
the PSD Interpretive Memorandum remain in effect during the
reconsideration process.
Because the PSD Interpretive Memorandum concerns PSD applicability,
its reconsideration will identify the circumstances under which GHG
emissions are treated as ``subject to regulation under the CAA'' and,
therefore, are ``regulated NSR pollutants.'' Once GHG emissions are
considered ``regulated NSR pollutants,'' PSD program requirements for
existing thresholds (100/250 tpy) are triggered. The PSD Interpretive
Memorandum reconsideration is being addressed in a proposed rule
published in the Federal Register on