Final Rule To Implement the 8-Hour Ozone National Ambient Air Quality Standard-Phase 2; Final Rule To Implement Certain Aspects of the 1990 Amendments Relating to New Source Review and Prevention of Significant Deterioration as They Apply in Carbon Monoxide, Particulate Matter and Ozone NAAQS; Final Rule for Reformulated Gasoline, 71612-71705 [05-22698]
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Federal Register / Vol. 70, No. 228 / Tuesday, November 29, 2005 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 51, 52, and 80
[OAR 2003–0079; FRL–7996–8]
RIN 2060–AJ99
Final Rule To Implement the 8-Hour
Ozone National Ambient Air Quality
Standard—Phase 2; Final Rule To
Implement Certain Aspects of the 1990
Amendments Relating to New Source
Review and Prevention of Significant
Deterioration as They Apply in Carbon
Monoxide, Particulate Matter and
Ozone NAAQS; Final Rule for
Reformulated Gasoline
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: In this document, we are
taking final action on most remaining
elements of the program to implement
the 8-hour ozone national ambient air
quality standard (NAAQS or standard).
This final rule addresses, among other
things, the following control and
planning obligations as they apply to
areas designated nonattainment for the
8-hour ozone NAAQS: reasonably
available control technology and
measures (RACT and RACM),
reasonable further progress (RFP),
modeling and attainment
demonstrations, and new source review
(NSR). We are issuing this rule so that
States and Tribes will know how these
statutory control and planning
obligations apply and when State
implementation plan (SIP) revisions are
due for these obligations so that the
States may develop timely submissions
consistent with the statutory obligations
and attain the NAAQS as expeditiously
as practicable but no later than their
maximum attainment dates. The
intended effect of the rule is to provide
certainty to States and Tribes regarding
development of those plans.
In this rule, we are also finalizing
several revisions to the regulations
governing the nonattainment NSR
programs mandated by section
110(a)(2)(C) and part D of title I of the
Clean Air Act (CAA).
Finally, this rule addresses what
effect the transition to the 8-hour
standard will have on certain aspects of
the Reformulated Gasoline (RFG)
program. The nine original mandatory
RFG areas, as well as most other areas
that have become mandatory RFG areas
by being reclassified as severe areas
under section 181(b) of the CAA, will
continue to be required to use RFG at
least until they are redesignated to
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attainment for the 8-hour NAAQS. The
EPA reserves for future consideration
what effect the transition to the 8-hour
standard will have on areas reclassified
as severe areas for the 1-hour NAAQS
under section 181(b) of the CAA that
were redesignated to attainment for the
1-hour standard before revocation of
that standard.
EFFECTIVE DATE: This rule is effective on
January 30, 2006.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. OAR–2003–0079. All documents in
the docket are listed in the EDOCKET
index at https://www.epa.gov/edocket.
Although listed in the index, some
information is not publicly available,
i.e., Confidential Business Information
or other information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the Internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either
electronically in EDOCKET or in hard
copy at the EPA Docket Center (Air
Docket), EPA/DC, EPA West, Room
B102, 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 Office of Air and Radiation Docket
and Information Center is (202) 566–
1742.
In addition, we have placed a variety
of earlier materials regarding
implementation of the 8-hour ozone
NAAQS on the Web site: https://
www.epa.gov/ttn/naaqs/ozone/
o3imp8hr.
For
general information: Mr. John Silvasi,
Office of Air Quality Planning and
Standards, U.S. Environmental
Protection Agency, Mail Code C539–02,
Research Triangle Park, NC 27711,
phone number (919) 541-5666, fax
number (919) 541-0824 or by e-mail at
silvasi.john@epa.gov or Ms. Denise
Gerth, Office of Air Quality Planning
and Standards, U.S. Environmental
Protection Agency, Mail Code C539–02,
Research Triangle Park, NC 27711,
phone number (919) 541–5550, fax
number (919) 541–0824 or by e-mail at
gerth.denise@epa.gov. For information
concerning new source review: Ms.
Janet McDonald, Office of Air Quality
Planning and Standards, U.S.
Environmental Protection Agency, Mail
Code C539–03, Research Triangle Park,
NC 27711, phone number (919) 541–
FOR FURTHER INFORMATION CONTACT:
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1450, fax number (919) 541–5509 or by
e-mail at mcdonald.janet@epa.gov.
SUPPLEMENTARY INFORMATION:
Outline
I. What is the Background for this Rule?
II. What is Included in this Rule?
III. In Short, What Does this Final Rule
Contain?
IV. Final Rule for Phase 2 Elements Other
than NSR and RFG
A. Should prescribed requirements of
subpart 2 apply in all 8-hour
nonattainment areas classified under
subpart 2, or is there flexibility in
application in certain narrowly-defined
circumstances?
B. How will we address long-range
transport of ground-level ozone and its
precursors when implementing the 8hour ozone standard?
C. How will we address transport of
ground-level ozone and its precursors for
rural nonattainment areas, areas affected
by intrastate transport, and areas affected
by international transport?
D. How will EPA address requirements for
modeling and attainment demonstration
SIPs for areas implementing the 8-hour
ozone standard?
E. What requirements for RFP should apply
under the 8-hour ozone standard?
F. Are contingency measures required in
the event of failure to meet a milestone
or attain the 8-hour ozone NAAQS?
G. What requirements should apply for
RACM and RACT for 8-hour ozone
nonattainment areas?
H. How will the section 182(f) NOX
provisions be handled under the 8-hour
ozone standard?
I. Should EPA promulgate a NSR provision
to encourage development patterns that
reduce overall emissions?
J. How will EPA ensure that the 8-hour
ozone standard will be implemented in
a way which allows an optimal mix of
controls for ozone, PM2.5, and regional
haze?
K. What emissions inventory requirements
should apply under the 8-hour ozone
NAAQS?
L. What guidance should be provided that
is specific to Tribes?
M. What are the requirements for Ozone
Transport Regions (OTRs) under the 8hour ozone standard?
N. Are there any additional requirements
related to enforcement and compliance?
O. What requirements should apply to
emergency episodes?
P. What ambient monitoring requirements
will apply under the 8-hour ozone
NAAQS?
Q. When will EPA require 8-hour
attainment demonstration SIP
submissions?
R. How will the statutory time periods in
the CAA be addressed when we
redesignate areas to nonattainment
following initial designations for the 8hour NAAQS?
V. EPA’s Final Rule for New Source Review
A. Background
B. Summary of Final Rule and Legal Basis
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C. Comments and Responses
D. NSR Implementation Under the 8-hour
ozone NAAQS
VI. Final Rule for RFG
A. Introduction
B. Background
C. What Action is EPA Taking?
D. Why is EPA Taking This Action?
E. Future Proceedings
F. Miscellaneous Administrative Changes
to RFG Regulations
G. Comments and Responses
VII. Other Considerations
A. How will EPA’s implementation of the
8-hour ozone NAAQS affect funding
under the Congestion Mitigation and Air
Quality Improvement (CMAQ) Program?
B. What is the relationship between
implementation of the 8-hour standard
and the CAA’s title V permits program?
C. What action is EPA taking on the
Overwhelming Transport Classification
for Subpart 1 Areas?
VIII. 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 and
Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
L. Petitions for Judicial Review
M. Determination Under Section 307(d)
Appendix A to Preamble—Methods to
Account for Non-Creditable Reductions
when Calculating ROP Targets for the
2008 and Later ROP Milestone Years
Appendix B to Preamble—Glossary Of
Terms and Acronyms
I. What Is the Background for This
Rule?
On June 2, 2003 (68 FR 32805), we
published a proposed rule to implement
the 8-hour ozone NAAQS. The proposal
addressed a number of implementation
issues. We proposed one or more
options for each issue addressed in the
proposal. Please refer to the proposed
rule (68 FR 32802) for a detailed
discussion and background information
on the 8-hour ozone NAAQS; the
associated litigation; our proposed
strategy for areas to achieve the NAAQS;
and the stakeholder process for
gathering input into this effort, among
other topics.
On August 6, 2003 (68 FR 46536), we
published a notice of availability of the
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draft regulatory text for the proposed
rule to implement the 8-hour ozone
NAAQS. This notice started a 30-day
public comment period on the draft
regulatory text.
On April 30, 2004 (69 FR 23951), we
published a final rule that addressed the
following key elements related to
implementation of the 8-hour ozone
NAAQS: classifications for the 8-hour
NAAQS; revocation of the 1-hour
NAAQS (i.e., when the 1-hour NAAQS
will no longer apply); how antibacksliding principles will ensure
continued progress toward attainment of
the 8-hour ozone NAAQS; attainment
dates; and the timing of emissions
reductions needed for attainment.
Following publication of the April 30,
2004 final rule, the Administrator
received three petitions, pursuant to
section 307(b)(7)(B) of the CAA
requesting reconsideration of a number
of aspects of the final rule.1 On
September 23, 2004, we granted
reconsideration of three issues raised in
the Earthjustice Petition. On February 3,
2005 (70 FR 5593), we published a
proposed rule to take comment on two
of these issues: (1) The provision that
section 185 fees would no longer be
applicable once the 1-hour NAAQS is
revoked and (2) the timing for
determination of what is an ‘‘applicable
requirement.’’ On May 20, 2005, the
final rule on these two issues was
signed by the Administrator of EPA. On
April 4, 2005 (70 FR 17018), we
published a proposed rule to take
comment on the issue of whether we
should interpret the Act to require areas
to retain major NSR requirements that
apply to certain 1-hour ozone
nonattainment areas in implementing
the 8-hour standard. We took final
action on the NSR issues on June 30,
2005 (70 FR 39413; July 8, 2005).
On January 10, 2005, we granted
reconsideration of the overwhelming
transport classification issue raised by
Earthjustice in their Petition. At the
same time, we denied reconsideration of
the issues they raised in their Petition
dealing with the applicability of RFG
when the 1-hour NAAQS is revoked and
future 8-hour ozone redesignations to
nonattainment. We intend to publish a
proposed rule on the overwhelming
1 Three petitions for reconsideration of the Phase
1 Rule were filed by: (1) Earthjustice on behalf of
the American Lung Association, Environmental
Defense, Natural Resources Defense Council, Sierra
Club, Clean Air Task Force, Conservation Law
Foundation, and Southern Alliance for Clean
Energy; (2) the National Petrochemical and Refiners
Association and the National Association of
Manufacturers; and (3) the American Petroleum
Institute, American Chemistry Council, American
Iron and Steel Institute, National Association of
Manufacturers and the U.S. Chamber of Commerce.
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transport classification shortly. We are
continuing to review the issues raised in
the National Petrochemical and Refiners
Association and American Petroleum
Institute Petitions. Copies of the
Petitions for Reconsideration and
actions EPA has taken regarding the
Petitions may be found at:
www.epa.gov/ttn/naaqs/ozone/
o3imp8hr.
In addition, in the April 30, 2004 rule,
we established a subpart E in 40 CFR
part 81 ‘‘Identification of Area
Designations and Classifications for the
1-Hour Ozone NAAQS as of June 15,
2004 [Reserved].’’ We intend to publish
that list shortly.
Concerning the major NSR provisions,
today’s final regulations were proposed
as part of two different regulatory
packages. On July 23, 1996 (61 FR
38250), we proposed changes to the
major NSR program, including
codification of the requirements of part
D of title I of the 1990 CAA
Amendments for major stationary
sources of volatile organic compounds
(VOC), NOX, particulate matter having a
nominal aerodynamic diameter less
than or equal to 10 microns (PM10), and
CO. On June 2, 2003 (68 FR 32802), we
proposed a rule to implement the 8-hour
ozone NAAQS. In the 2003 action, we
proposed a rule to identify the statutory
requirements that apply for purposes of
developing SIPs under the CAA to
implement the 8-hour ozone NAAQS
(68 FR 32802). We did not propose
specific regulatory language for
implementation of NSR under the 8hour NAAQS. However, we indicated
that we intended to revise the
nonattainment NSR regulations to be
consistent with the rule for
implementing the 8-hour ozone NAAQS
(68 FR 32844). On April 30, 2004 (69 FR
23951), we published a final rule that
addressed classifications for the 8-hour
NAAQS. The April 2004 rule also
included the NSR permitting
requirements for the 8-hour ozone
standard, which necessarily follow from
the classification scheme chosen under
the terms of subpart 1 and subpart 2.
Also, in our 1996 action, and then
again in our June 2, 2003 action, we
proposed to amend our nonattainment
NSR provisions to expressly include
NOX as an ozone precursor in
nonattainment major NSR programs (61
FR 38297 and 68 FR 32847). We also
proposed that, as provided under CAA
section 182(f), a waiver from
nonattainment NSR for NOX as an ozone
precursor would be available for both
subpart 1 and subpart 2 areas (68 FR
32846). Moreover, we proposed to
require States to modify their existing
programs to include NOX as an ozone
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precursor in attainment areas (68 FR
32846).
In 1996, we proposed to revise the
regulations limiting offsets from
emissions reductions due to shutting
down an existing source or curtailing
production or operating hours below
baseline levels (‘‘shutdowns/
curtailments’’). We proposed
substantive revisions in two alternatives
that would ease, under certain
circumstances, the existing restrictions
on the use of emission reduction credits
from source shutdowns and
curtailments as offsets.
On July 23, 1996, we proposed to
revise § 52.24 to incorporate changes
made by the 1990 CAA Amendments
related to the applicability of
construction bans (61 FR 38305). To
clarify our intent, our proposed 8-hour
ozone NAAQS implementation rule in
June 2003 explained that § 52.24(k)
remained in effect and would be
retained. In that action, we also
proposed that we would revise
§ 52.24(k) to reflect the changes in the
1990 CAA Amendments (68 FR 32846).
On June 2, 2003 (68 FR 32802), we
explained implementation of the major
NSR program under the 8-hour ozone
NAAQS during the SIP development
period, and proposed flexible NSR
requirements for areas that expected to
attain the 8-hour NAAQS within 3 years
after designation.
In this rule, we are also finalizing
several revisions to the regulations
governing the nonattainment NSR
programs mandated by section
110(a)(2)(C) and part D of title I of the
Clean Air Act (CAA). First, we are
codifying requirements added to part D
of title I of the CAA in the 1990
Amendments related to permitting of
major stationary sources in areas that
are nonattainment for the ozone,
particulate matter (PM), and carbon
monoxide (CO) NAAQS. Second, we are
revising the criteria for crediting
emissions reductions credits from
shutdowns and curtailments as offsets.
Third, we are revising the regulations
for permitting of major stationary
sources in nonattainment areas in
interim periods between designation of
new nonattainment areas and EPA’s
approval of a revised SIP. Fourth, we are
changing the regulations that impose a
moratorium (ban) prohibiting
construction of new or modified major
stationary sources in nonattainment
areas where the State fails to have an
implementation plan meeting all of the
requirements of part D. In addition to
the changes to the nonattainment NSR
regulations, we also are making one
change to the Prevention of Significant
Deterioration (PSD) regulations under
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part C of title I of the CAA. We are
codifying nitrogen oxides (NOX) as an
ozone precursor in attainment and
unclassifiable areas.
Today’s changes regarding NSR are
based on the proposed rule published
on June 2, 2003 to Implement the 8-hour
Ozone National Ambient Air Quality
Standard (NAAQS), as well as the
proposed rule published on July 23,
1996 for ‘‘Prevention of Significant
Deterioration (PSD) and Non-attainment
New Source Review (NSR).’’ These
changes provide a consistent national
program for permitting major stationary
sources under section 110(a)(2)(C) and
parts C and D of title I, including major
stationary sources of ozone precursors
in ozone nonattainment areas.
For the reader’s convenience, a
glossary and list of acronyms appears in
Appendix B of this preamble.
II. What Is Included in This Rule?
Today’s action, Phase 2 of the
implementation rule, addresses
numerous topics, but primarily focuses
on the following key implementation
obligations for areas designated
nonattainment for the 8-hour NAAQS:
RACT and RACM; RFP; modeling and
attainment demonstrations; and NSR. It
also addresses what effect the transition
to the 8-hour standard will have on
certain aspects of the RFG program.
III. In Short, What Does This Final Rule
Contain?
This summary is intended to give
only a convenient overview of our final
rule. It should not be relied on for the
details of the actual rule. The final rule
(regulatory text) and the discussion of it
in the sections below should be
consulted directly.
Summary of Section IV (Below): Final
Rule for Phase 2 Elements Other Than
NSR and RFG
A. Should prescribed requirements of
subpart 2 apply in all 8-hour
nonattainment areas classified under
subpart 2, or is there flexibility in
application in certain narrowly defined
circumstances?
There may be a basis for waiving a
prescribed requirement on a case-bycase basis where imposition of the
requirement would create an absurd
result. If a State submits a
demonstration that application of a
specific requirement in a specific
nonattainment area would create an
absurd result, we will consider
application of the absurd results
doctrine at that time. We believe that
absurd results that might occur from
application of mandatory control
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measures would happen only in rare
instances, if at all.
B. How will we address long-range
transport of ground-level ozone and its
precursors when implementing the 8hour ozone standard?
The EPA has issued two major rules
to address interstate transport of ozone
pollution. The 1998 NOX SIP Call Rule
already is achieving significant
reductions in NOX emissions that
contribute to interstate ozone pollution
in the eastern United States. Nineteen
States were required to achieve
reductions by May 2004, and additional
reductions are required by May 2007.
On May 12, 2005, EPA published the
Clean Air Interstate Rule (CAIR) in the
Federal Register (70 FR 25162). It
establishes statewide sulfur dioxide
(SO2) and NOX emissions budgets for
upwind States that significantly
contribute to nonattainment or interfere
with maintenance of the fine particle or
8-hour ozone air quality standards in
downwind States. For ozone, this action
established summertime NOX budgets
for the District of Columbia and 25
States in the eastern half of the country,
with reductions to be achieved by 2009
and 2015. The CAIR goes beyond the
SIP call by requiring reductions from
additional States and by requiring
further emissions reductions in SIP call
States.
C. How will we address transport of
ground-level ozone and its precursors
for rural nonattainment areas, areas
affected by intrastate transport, and
areas affected by international
transport?
1. Rural Transport Nonattainment Areas
The final rule does not contain any
revisions to current policy on rural
transport areas under section 182(h). We
do not believe there are any 8-hour
nonattainment areas covered under
subpart 2 that are ‘‘rural’’ and therefore
eligible for consideration for coverage
under section 182(h).
2. Intrastate Transport
The final rule does not contain any
additional provisions for addressing
intrastate transport for the reasons
stated in the proposal.
3. How will EPA address transport of
ground-level ozone and its precursors
for areas affected by international
transport?
We are not setting forth any regulatory
provisions related to international
transport in this rule. Section 179B of
the CAA applies for these purposes. We
continue to recommend that States
confer with the appropriate EPA
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Regional Office to establish on a caseby-case basis the technical requirements
for these analyses. These analyses will
be subject to public comment during the
State and Federal SIP processes.
D. How will EPA address requirements
for modeling and attainment
demonstration SIPs for areas
implementing the 8-hour ozone
standard?
The final rule retains the following
three elements that each attainment
demonstration SIP must include: (1)
Technical analyses to locate and
identify sources of emissions that are
causing violations of the 8-hour NAAQS
within nonattainment areas (i.e.,
analyses related to the emissions
inventory required for the
nonattainment area), (2) adopted
measures with schedules for
implementation and other means and
techniques necessary and appropriate
for attainment, and (3) contingency
measures required under section
172(c)(9) of the CAA that can be
implemented without further action by
the State or the Administrator to cover
failures to meet RFP milestones and/or
attainment.
1. Attainment Demonstration Due Date
Areas required to submit an
attainment demonstration must do so no
later than 3 years after the effective date
of designation for the 8-hour ozone
NAAQS.
2. Multi-State Nonattainment Areas
State partners involved in a multiState ozone nonattainment area must
work together to perform the
appropriate modeling analyses to
identify control measures that will
enable the area to achieve attainment as
expeditiously as practicable. Each State
will be responsible for its portion of the
control program and will be held
accountable for controls identified for
implementation within its State
boundaries.
3. Role of Modeling Guidance in
Attainment Demonstrations
Attainment demonstrations must be
consistent with 40 CFR 51.112. We will
generally review the demonstrations for
technical merit using EPA’s most recent
modeling guidance at the time the
modeled attainment demonstration is
performed.
4. Multi-pollutant Assessments (OneAtmosphere Modeling)
There is no regulatory text on this
issue, but the preamble makes several
recommendations concerning multipollutant assessments.
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E. What requirements for RFP should
apply under the 8-hour ozone standard?
1. General Discussion
We are adopting nearly all the
approaches set forth in our proposed
rule for the various 1-hour rate-ofprogress (ROP) and 8-hour RFP issues.
2. What is the content and timing of the
plan for addressing the RFP
requirements under section 182(b)(1) for
areas covered under subpart 2?
Areas that are classified as moderate
under the 8-hour standard that have
already implemented their 15 percent
plans under their 1-hour ozone SIPs
would be considered to have met the
statutory 15 percent requirement.
Reasonable further progress for the first
6 years from the baseline year would be
covered under the more generic RFP
requirements of subpart 1. Serious and
above areas would have to meet 3
percent reductions per year starting in
the baseline year averaged over each 3year period out to the attainment year.
An 8-hour nonattainment area that is
identical, geographically, to its
predecessor 1-hour nonattainment area
(which has already done the 15 percent
reduction) will not be required to do
another 15 percent VOC-only reduction
plan. For an 8-hour moderate or higher
nonattainment area that contains a 1hour nonattainment area that has an
approved 15 percent VOC ROP plan but
also contains areas that do not have an
approved 15 percent VOC ROP plan, the
final rule allows States the choice
between two options:
Option 1. Develop a new baseline and
new 15 percent VOC ROP emission
reduction target for the entire newly
expanded area. Determine that
emissions reductions that occur after the
2002 baseline emissions inventory year
are creditable in the combined new area.
The reductions must be of VOC only.
Option 2. Treat the 8-hour
nonattainment area as divided between
the old 1-hour area(s) and the newly
added 8-hour area. For the newly added
portion (which had not previously
implemented a 15 percent plan), States
must establish a separate 15 percent
VOC target under subpart 2. The
previous nonattainment area that fell
under the 1-hour standard will now be
subject to the subpart 1 provisions of the
CAA and will be able to credit both
VOC and NOX toward meeting the RFP
target for this portion of the
nonattainment area. VOC reductions to
meet the 15 percent requirement for the
portion of the new 8-hour
nonattainment area that has not yet met
this requirement may come from across
the entire 8-hour area.
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The subpart 1 RFP provisions
addressed by the rule below that are
applicable in the former 1-hour portion
of the area depend on the subpart 2
area’s attainment date as follows:
• In moderate areas that have an
attainment date within 5 years after
their 8-hour designation, for which
portions of the area have previously met
their 15 percent requirements under the
1-hour standard, the former 1-hour
portion will only be subject to subpart
1 RFP requirements, which will be
satisfied with the measures that
demonstrate attainment as expeditiously
as practicable. These areas will not be
developing RFP plans separate from
their attainment plans. Thus, for these
areas, the only motor vehicle emissions
budgets that will be developed will be
for the attainment year.
• In moderate areas that have an
attainment date beyond 5 years after
their 8-hour designation, for which
portions of the area have previously met
their 15 percent requirements under the
1-hour standard, the former 1-hour
portion will only be subject to subpart
1 RFP requirements, which will be
satisfied with a plan to demonstrate 15
percent emissions reductions (which
may be either VOC or NOX or a
combination of both) from 2002 to 2008,
and any additional emissions reductions
needed for attainment beyond 2008.
Thus, these areas (the entire 8-hour
nonattainment area) would establish a
motor vehicle emission budget for 2008
and for their attainment year.
Serious and above areas will be
developing both a 15 percent VOC plan
for the new portion of the 8-hour
nonattainment area and an 18 percent
VOC/NOX plan for the portion of the
area that previously met its 15 percent
requirement. Thus, the RFP plan as a
whole will establish total allowable
emissions for 2008 for the entire 8-hour
nonattainment area. Therefore, the plans
for these areas, as well as moderate
areas that choose option one, will
establish motor vehicle emissions
budgets for both 2008 and the
attainment year.
3. What baseline year should be
required for the emissions inventory for
the RFP requirement?
We are using the 2002 inventory as
the baseline inventory for the RFP
requirement for areas designated
nonattainment in 2004 primarily
because of timing concerns related to
attainment dates and when data is
collected and compiled. However, in
response to several comments, we are
allowing States the option of justifying
the use of an alternative baseline year
inventory year for RFP.
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4. Should moderate and higher
classified areas be subject to prescribed
additional RFP requirements prior to
their attainment date?
Moderate areas would have to provide
additional emissions reductions (VOC/
NOX) needed to provide for attainment
by the beginning of the ozone season
prior to the area’s attainment date.
Serious and higher classified areas
would need to provide in their SIPs an
additional average of three percent per
year emission reduction over each
subsequent 3-year period beyond the
initial 6-year period through the
attainment year.
5. What is the timing of the submission
of the RFP plan?
For moderate and higher classified
areas, the first RFP SIP must be
submitted within 3 years after the area’s
nonattainment designation. For areas
with a June 15, 2004 effective date, for
the 8-hour designations, the SIP would
be due by June 15, 2007. This would
provide up to 3 years for States to
develop and submit RFP plans, and 1
additional year (until the end of 2008)
for control measures to be implemented.
The RFP SIP for any remaining 3-year
periods out to the attainment date
beyond the first 6 years would be
required to be submitted with the
attainment demonstration, i.e., within 3
years after designation. We recommend
that States complete their RFP plans as
soon as possible after designation to
provide more time for sources to
implement the emissions reductions.
6. How should CAA restrictions on
creditable measures be interpreted?
Which national measures should count
as generating emissions reductions
credit toward RFP requirements?
All emissions reductions that occur
after the baseline emissions inventory
year are creditable for purposes of the
RFP requirements in this section except
as specifically provided in section
182(b)(1)(C) and (D) and section
182(c)(2)(B) of the CAA which exclude
four categories of emissions reductions
requirements required to be adopted
prior to 1990.
7. For areas covered only by subpart 1,
how should the RFP requirement be
structured?
We are finalizing rules for two rather
than three categories of areas based on
the CAA’s division of attainment dates
for subpart 1 areas under section
172(a)(2). The following are the two
scenarios and the RFP requirements for
each:
Scenario A: Areas with attainment
dates 5 years or less after designation
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(i.e., for most areas on or before June 15,
2009). Reasonable further progress for
these areas would be met by ensuring
emissions reductions needed for
attainment are implemented, as noted
above, by the beginning of the ozone
season prior to the attainment date. This
would be similar to subpart 2 RFP for
areas classified as marginal.
Scenario B: Areas with attainment
dates beyond 5 years after designation
(i.e., beyond 2009).
• The RFP plan must show
increments of progress from the baseline
emissions inventory year out to the
attainment date.
• The RFP SIP would first have to
provide for a 15 percent emission
reduction from the baseline year within
6 years after the baseline year (i.e., out
to 2008).
• The 15 percent RFP SIP would have
to be submitted within 3 years after
designation (i.e., in 2007).
• Either NOX or VOC emissions
reductions (or both) could be used to
achieve the 15 percent emission
reduction requirement.
• For each subsequent 3-year period
(after 2008) out to the attainment date,
the RFP SIP would have to provide for
an additional increment of progress no
less than the amount of emissions
reductions that would be roughly
proportional to the time between the
end of the first increment (in 2008) and
the attainment date. This second RFP
SIP would also have to be submitted
within 3 years after the effective date of
designation (i.e., in 2007).
8. Where part of an 8-hour
nonattainment area was a 1-hour
nonattainment area with a ROP
obligation extending past 2002, can
emissions reductions from the area’s 1hour ROP plan be used as credit toward
meeting the area’s 8-hour RFP plan?
Where an area has both 1-hour and 8hour RFP obligations for the post-2002
period, the State may rely on emissions
reductions from the 1-hour plan in
achieving RFP for the 8-hour standard.
The State could develop a new baseline
and new RFP emission reduction targets
for the entire 8-hour standard
nonattainment area (i.e., the old 1-hour
standard nonattainment area and any
newly added portion of the 8-hour
standard nonattainment area).
Emissions reductions from measures in
the 1-hour ozone SIP that are achieved
after the 8-hour ozone NAAQS baseline
year could count (subject to creditability
restrictions as discussed above) toward
meeting the RFP requirement for the
entire 8-hour area.
This approach would set an RFP
target for the entire 8-hour ozone
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nonattainment area. Under this
approach, the new RFP target for the 8hour standard would replace the
previous 1-hour ROP target (while
ensuring that, at a minimum, the
emissions reductions required to meet
the old target are met; see 40 CFR
51.905(a)(1)(iii)).
9. Will EPA’s ‘‘Clean Data Policy’’ apply
for purposes of 8-hour RFP, attainment
demonstrations and other related
requirements?
We intend to apply the Clean Data
Policy, which we had applied under the
1-hour standard, for purposes of the 8hour standard. In this action EPA is
finalizing the statutory interpretation
that is embodied in the policy. The text
of the final rule encapsulates the
statutory interpretation set forth in the
policy.
10. How will RFP be addressed in Tribal
areas?
We intend to follow the Tribal
Authority Rule (TAR), which provides
Tribes with the ability to develop Tribal
implementation plans (TIPs) to address
and implement the NAAQS in Indian
country. It further provides the Tribes
with flexibility to develop these plans in
a modular way, as long as the elements
of their TIPs are reasonably ‘‘severable.’’
11. How will RFP targets be calculated?
Appendix A to the preamble to this
final rule provides calculation
procedures for determining the RFP
targets. These have been revised from
those in the proposal to account for NOX
and for emissions models in addition to
the MOBILE model.
12. Should EPA continue the policy of
allowing substitution of controls from
outside the nonattainment area within
100 kilometers for VOC and 200
kilometers for NOX?
We intend to continue to rely on this
policy at the current time. The use of
emissions reductions outside the
nonattainment area must be shown to be
beneficial toward reducing ozone in the
nonattainment area and must ensure
that the reductions meet the standard
tests of creditability (permanent,
enforceable, surplus, and quantifiable).
13. When must RFP emissions
reductions be achieved?
The target level of emissions must be
met by the attainment date of the
attainment year. Section 182(c)(2)(B)
requires that RFP be continued out to
the attainment date.
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14. Banked emission reduction credits
(including shutdown credits): Can prebaseline emission reduction credits be
used to satisfy the RFP requirement?
• The baseline emissions should not
include pre-enactment banked emission
credits since they were not actual
emissions during the calendar year of
enactment of the CAA Amendments of
1990.
• Banked emissions reductions
credits created prior to enactment of the
CAA Amendments of 1990 are not
creditable toward the 15 percent
progress requirement. However, for
purposes of equity, EPA encourages
States to allow sources to use such
banked emissions credits for offsets and
netting as authorized.
• When States use such banked
credits for offsets and netting to the
extent otherwise creditable under the
part D NSR regulations, these preenactment emissions credits must be
treated as growth. Prior guidance on this
issue is still relevant for banked
emission reduction credits in relation to
the RFP requirement for the 8-hour
ozone standard. However, because the
rule for implementing the 8-hour ozone
standard uses a 2002 baseline year, the
prior guidance should be interpreted
with that baseline in mind instead of
enactment of the CAA Amendments of
1990.
areas within an Ozone Transport Region
(OTR), a RACT SIP is required covering
CTG sources and major non-CTG
sources. The RACT submittal date is 27
months after designation, except a
subpart 1 area shall submit the RACT
SIP with its attainment date extension
request.2 States must require sources to
implement RACT no later than the first
ozone season or portion thereof which
occurs 30 months after the required
submittal date.
Where a RACT SIP is required, State
SIPs implementing the 8-hour standard
generally must assure that RACT is met,
either through a certification that
previously required RACT controls
represent RACT for 8-hour
implementation purposes or through a
new RACT determination. States may
use existing EPA guidance in making
RACT determinations. The State need
not perform a NOX RACT analysis for
sources subject to the State’s emission
cap-and-trade program where the capand-trade program has been adopted by
the State and approved by EPA as
meeting the NOX SIP Call requirements
or, in States achieving CAIR reductions
solely from electric generating units
(EGUs), the CAIR NOX requirements.3
States are free to conduct case-by-case
RACT determinations, or RACT
determinations or certifications for
groups of sources, at their discretion.
F. Are contingency measures required in
the event of failure to meet a milestone
or attain the 8-hour ozone NAAQS?
Contingency measures are required to
be implemented in the event of failure
to meet a milestone or attain the 8-hour
ozone NAAQS and must accompany the
attainment demonstration SIP. All
subpart 1 and subpart 2 areas other than
marginal areas need contingency
measures.
2. Reasonably Available Control
Measures (RACM)
For each nonattainment area required
to submit an attainment demonstration,
the State must submit with the
attainment demonstration a SIP revision
demonstrating that it has adopted all
control measures necessary to
demonstrate attainment as expeditiously
as practicable and to meet any RFP
requirements.
G. What requirements should apply for
RACM and RACT for 8-hour ozone
nonattainment areas?
H. How will the section 182(f) NOX
provisions be handled under the 8-hour
ozone standard?
The final rule allows a person to
petition the Administrator for an
exemption from nonattainment major
NSR and/or RACT requirements for
major stationary sources of NOX in 8hour ozone nonattainment areas and for
any area in a section 184 ozone
transport region. The final rule includes
an extension of the NOX waiver
provisions to 8-hour ozone
nonattainment areas covered under
1. Reasonably Available Control
Technology (RACT)
For subpart 1 areas that submit a
demonstration of attainment for 5 or less
years after designation (i.e., do not
request an attainment date extension
beyond 5 years after designation), the
CAA’s RACT requirement is met with
the control requirements associated
with a demonstration that the NAAQS
is attained as expeditiously as
practicable.
For subpart 1 areas that submit an
attainment demonstration that requests
an attainment date extension (i.e.,
beyond 5 years after designation),
subpart 2 moderate and above areas, and
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2 This is generally expected with the submission
of the attainment demonstration.
3 Alternatively, a State need not perform a NO
X
RACT analysis for sources subject to Federal
implementation plan that implements the emission
reductions required by the NOX SIP call or the
CAIR.
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subpart 1 (as proposed) as well as
subpart 2 nonattainment areas. In
addition, the final rule states that a
section 182(f) NOX exemption granted
under the 1-hour ozone standard does
not relieve the area from any
requirements under the 8-hour ozone
standard. A petition must contain
adequate documentation that the
exemption provisions in section 182(f)
are met. We recently issued updated
guidance on appropriate documentation
regarding section 182(f) for application
to the 8-hour ozone program.4
I. Should EPA promulgate a NSR
provision to encourage development
patterns that reduce overall emissions?
Section V of this preamble below
addresses rules for NSR for the 8-hour
ozone standard. We are not at this time
issuing any rule related to Clean Air
Development Communities (CADCs).
J. How will EPA ensure that the 8-hour
ozone standard will be implemented in
a way which allows an optimal mix of
controls for ozone, fine particulate
matter PM2.5), and regional haze?
We are continuing our policy of
encouraging each State with an ozone
nonattainment area which overlaps or is
nearby a PM2.5 nonattainment area to
take all reasonable steps to coordinate
the required revisions for these
nonattainment areas and meet
reasonable progress goals for regional
haze.
K. What emissions inventory
requirements should apply under the 8hour ozone NAAQS?
Existing ozone-relevant emissions
data element requirements under 40
CFR 51 subpart A are sufficient to
satisfy the emissions inventory data
requirements under the 8-hour ozone
NAAQS.
L. What guidance should be provided
that is specific to Tribes?
Section 301(d) of the CAA recognizes
that American Indian Tribal
governments are generally the
appropriate authority to implement the
CAA in Indian country. As discussed in
the TAR, it is appropriate to treat Tribes
in the same manner as States for
purposes of implementing all of the
provisions of the CAA, except those
provisions for which EPA has
specifically determined that it is not
appropriate to treat Tribes in the same
4 Memorandum dated January 14, 2005,
‘‘Guidance on Limiting Nitrogen Oxides (NOX)
Requirements Related to 8-Hour Ozone
Implementation’’ from Stephen D. Page, Director,
Office of Air Quality Planning and Standards, to Air
Directors, Regions I–X.
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manner as States. (The CAA provisions
for which EPA has determined it is not
appropriate to treat Tribes in the same
manner as States are listed in section
IV.L. of this preamble.) Examples of
CAA provisions for which EPA has
determined it is not appropriate to treat
Tribes in the same manner as States
include specific plan submittal and
implementation deadlines.
In implementing this rule, it is
important for both States and Tribes to
work together to coordinate planning
efforts. Other than in very limited
circumstances, State regulations do not
apply to Indian Country, but SIP control
measures could impact downwind
areas, including Indian communities. In
addition, nonattainment area
boundaries may include a portion of
Indian Country. Coordinated planning
will help ensure that the planning
decisions made by the States and Tribes
complement each other and achieve
progress toward meeting the NAAQS.
Q. When will EPA require 8-hour
attainment demonstration SIP
submissions?
M. What are the requirements for Ozone
Transport Regions (OTRs) under the 8hour ozone standard?
In today’s action, we are finalizing
previously proposed changes to three
regulations that govern major NSR
permitting of major stationary sources in
nonattainment areas—40 CFR 51.165,
appendix S of 40 CFR part 51, and 40
CFR 52.24.
The regulations at 40 CFR 51.165
contain the minimum elements that a
State’s preconstruction permitting
program for major stationary sources in
nonattainment areas must contain in
order for EPA to approve the State’s
program into the SIP. In § 51.165, we are
making revisions to incorporate the
major stationary source thresholds,
significant emission rates, and offset
ratios pursuant to part D of title I of the
CAA, as amended in 1990, for the 8hour ozone NAAQS, the CO NAAQS,
and the PM10 NAAQS. We are also
promulgating final changes to the
requirements for emissions reductions
achieved from shutdowns or
curtailments at § 51.165(a)(3)(ii)(C). We
are not currently acting on any other
proposed changes to 40 CFR 51.165.
Appendix S of 40 CFR part 51
contains the preconstruction permitting
program that applies to major stationary
sources in nonattainment areas lacking
an approved part D NSR program. It
applies during the interim period after
EPA designates an area as
nonattainment, but before EPA approves
a SIP to implement the nonattainment
NSR requirements for that pollutant (SIP
development period). We are making
the same changes to appendix S that we
are making to § 51.165 to implement the
CAA as revised by the 1990
Section 184 continues to apply for
purposes of the 8-hour standard;
therefore, the current OTR remains in
place and the section 184 control
requirements continue to apply for
purposes of the 8-hour standard. If a
new OTR is established for purposes of
the 8-hour standard pursuant to section
176A, that area would also be subject to
the provisions and additional control
requirements of section 184.
N. Are there any additional
requirements related to enforcement
and compliance?
We are not setting forth any
additional rule related to compliance
and enforcement.
O. What requirements should apply to
emergency episodes?
We have not yet proposed any rule
revision related to emergency episodes
(at 40 CFR part 51, subpart H), and the
final rule below does not contain any
such rule revision.
P. What ambient monitoring
requirements will apply under the 8hour ozone NAAQS?
No monitoring requirements are being
promulgated as part of this rulemaking.
The preamble discusses current relevant
requirements (40 CFR part 58) and
anticipated activities.
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Modeled attainment demonstrations—
where required—must be submitted
within 3 years after the effective date of
the area’s nonattainment designation.
R. How will the statutory time periods
in the CAA be addressed when we
redesignate areas to nonattainment
following initial designations for the 8hour NAAQS?
For any area that is initially
designated attainment or unclassifiable
for the 8-hour NAAQS and subsequently
redesignated to nonattainment for the 8hour ozone NAAQS, the attainment date
and dates for submittal of any
applicable requirements under subpart 1
or subpart 2 and these regulations
would run from the date of
redesignation to nonattainment for the
8-hour NAAQS.
Summary of Section V (Below): EPA’s
Final Rule for New Source Review
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Amendments. In addition, we are
finalizing revisions to section VI of
appendix S to qualify applicability of
this section. This revision is an
outgrowth of the proposed revisions to
section VI in the 8-hour NAAQS
implementation proposal (68 FR 32802).
We also are removing an outdated
exemption for sources increasing
emissions less than 50 tons per year
(tpy).
The regulations at 40 CFR 52.24
contain restrictions on the construction
or modification of major stationary
sources, including a construction ban
applicable in circumstances enumerated
by the 1977 CAA. These regulations also
apply if the Administrator determines
pursuant to CAA section 173(a)(4) that
the State is not adequately
implementing the SIP for meeting the
part D requirements. today’s final rules
codify requirements of the 1990 CAA
Amendments related to the applicability
of construction bans. The final rules at
§ 52.24 also codify that § 51.165 applies
in interpreting the terms in § 52.24. The
regulations at 40 CFR 52.24(k) retain the
requirement that appendix S governs
permits to construct and operate applied
for during the period between the date
of designation as nonattainment and the
date the part D plan for NSR is
approved, but is updated to remove the
reference to the construction ban.
In addition to the changes to the
nonattainment NSR regulations, we also
are making one change to the PSD
regulations under part C of title I of the
CAA. We are codifying NOX as an ozone
precursor in attainment and
unclassifiable areas.
Summary of Section VI (Below): Final
Rule for RFG
Today’s rule specifies that the nine
original RFG mandatory areas must
continue to use RFG at least until they
are redesignated to attainment for the 8hour standard. Similarly, areas that have
been reclassified as severe areas under
section 181(b) of the CAA for the 1-hour
NAAQS, and which were not
redesignated to attainment for the 1hour NAAQS prior to its revocation,
must continue to use RFG at least until
they are redesignated to attainment for
the 8-hour standard. The EPA is
reserving for future consideration what
RFG requirements apply to areas that
were reclassified as severe under the 1hour standard, but were redesignated to
attainment for that standard before its
revocation. The only such area that was
redesignated to attainment prior to
revocation of the 1-hour standard is
Atlanta, Georgia. The EPA is also
reserving for future consideration
whether areas must continue using RFG
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after they are redesignated to attainment
for the 8-hour standard, for the original
nine mandatory areas as well as the
areas reclassified to severe. Finally, EPA
clarifies that the current opt-in rules
will remain in place after the 1-hour
standard is revoked. Areas classified
under subpart 2 as marginal or above are
eligible to opt-in to the RFG program.
Summary of Section VII (Below): Other
Considerations
A. How will EPA’s implementation of
the 8-hour ozone NAAQS affect funding
under the Congestion Mitigation and Air
Quality Improvement (CMAQ) Program?
This section describes the
relationship between the CMAQ
program and the 8-hour ozone NAAQS
implementation program.
B. What is the relationship between
implementation of the 8-hour standard
and the CAA’s title V permits program?
The interrelationship between
implementation of the 8-hour ozone
standard and the title V permits
program was not discussed in the
proposed rule. However, various
questions have been raised about the
interface between the implementation of
the 8-hour ozone standard and the title
V operating permits program. The
preamble presents several questions and
answers, mainly dealing with how title
V applicability is affected by the new 8hr ozone standard and the revocation of
the 1-hour ozone standard.
C. What action is EPA taking on the
Overwhelming Transport Classification
for subpart 1 areas?
We are not completing rulemaking on
the overwhelming transport
classification in this rulemaking. This
section discusses the status of the
rulemaking.
IV. Final Rule for Phase 2 Elements
Other Than New Source Review and
Reformulated Gasoline
The discussion of many of the
regulatory elements below address
timing of required actions, such as
submission dates for SIP revisions. The
discussion is primarily directed toward
8-hour ozone nonattainment areas for
which the effective date of the
designation was June 15, 2004.
However, a number of areas may have
later effective dates for their
designations, such as early action
compact areas and areas subsequently
redesignated from attainment to
nonattainment for the 8-hour ozone
standard. For these situations, the
timing will run from the effective date
of those designations. In cases in this
preamble where we have used June 15,
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2004 as a substitute for the ‘‘effective
date,’’ we are using it only for purposes
of those areas with an effective date of
June 15, 2004.
A. Should prescribed requirements of
subpart 2 apply in all 8-hour
nonattainment areas classified under
subpart 2, or is there flexibility in
application in certain narrowly-defined
circumstances?
[Section VI.D. of June 2, 2003
proposed rule (68 FR 32825); no draft or
final regulatory text.]
1. Background
The 1990 CAA Amendments
overhauled the CAA’s requirements for
ozone nonattainment areas and, in
doing so, specified new mandatory
measures for many areas. The approach
embodied in subpart 2 was to classify
areas according to the severity of their
pollution. Areas with more serious
ozone pollution were given a higher
classification that did two things. First,
the successively higher classifications
provided a successively longer
maximum timeframe for attaining the
ozone NAAQS. Second, each higher
classification mandated specific
additional and/or more stringent
obligations than the classification
immediately below. Specifying
mandatory measures in the statute was
necessary because States and EPA, prior
to 1990, had failed to ensure that SIPs
achieved steady reasonable progress in
reducing emissions or to require readily
available measures that were cost
effective and necessary to meet the
standard. See generally H.R. Rep. No.
101–490 at 144–48 (1990).
For this rule, we examined the issue
of mandatory measures from both a legal
and policy standpoint. Our legal view is
guided by the statutory language in part
D of title I of the CAA. In addition, we
were guided by the Supreme Court’s
view of this language. Our policy view
is guided by past precedents and also
the principles we set forth in our
proposed rule (June 3, 2003; 68 FR
32802).
We have consistently interpreted the
CAA to mean that once an area is
classified under subpart 2, the subpart
2 requirements apply. While certain
requirements allow for some flexibility
in how they apply, the requirements do
not allow for broad waivers. For
example, all areas classified as serious
or above must meet the requirement for
an enhanced inspection and
maintenance (I/M) program, however,
there is some flexibility in determining
what type of I/M program meets the
requirement for an enhanced I/M
program. The Supreme Court, in
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addressing whether the classification
provisions in subpart 2 applied for
purposes of the 8-hour ozone NAAQS
found that they did and stated that
EPA’s implementation scheme, which
would have avoided classifications
under subpart 2, was unreasonable
because it would effectively nullify the
subpart 2 provisions that Congress
created with the intent to limit State and
EPA discretion. Whitman v. American
Trucking Assoc., 531 U.S. 484–85.
In the proposed rule, we recognized
that there is case law doctrine that
might allow a case-by-case waiver from
mandatory requirements when
sufficient evidence is presented that
application of a specific requirement in
a particular area would cause absurd
results.
2. Final Rule
We continue to interpret the CAA to
mean that the prescribed requirements
for each classification under subpart 2
apply to areas with such classification
for the 8-hour NAAQS. As we noted in
the preamble to the proposed rule, there
may be a basis for waiving a prescribed
requirement on a case-by-case basis
where imposition of the requirement
would create an absurd result. However,
as stated in the proposed rule, we
believe that absurd results that might
occur from application of mandatory
control measures would happen only in
rare instances. If a State submits a
demonstration that application of a
specific requirement in a specific
nonattainment area would create an
absurd result, we will consider
application of the absurd results
doctrine at that time.
3. Comment and Responses
Comment: A number of commenters
supported the approach that we
discussed in the proposed rule. Other
commenters agreed with the overall
concept that we proposed but felt that
we should take additional factors into
consideration if we make case-by-case
waivers from subpart 2 requirements.
Several commenters suggested that we
take the cost of controls into
consideration when determining if there
were an absurd result while others
suggested that we look at relative
control strategy effectiveness, e.g.,
allowing a demonstration that NOX
reductions are more effective and
therefore may be substituted for
mandatory VOC emissions reductions.
Several other commenters stated that
we should more broadly allow
substitution of subpart 2 mandatory
measures. One commenter felt that
substitution of subpart 2 measures
should be allowed as long as the
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substituted measures are at least
equivalent to the mandatory measures.
Another commenter stated that we
should allow areas to adopt substitute
measures in lieu of subpart 2 measures
where the subpart 2 measures would not
be as effective as the substitute
measures in reaching attainment. The
commenter stated that we have been
overly limited in our characterization of
when subpart 2 measures might be
waived to avoid an absurd result. The
commenter believed that we should
create a categorical exemption as an
exercise of agency power to allow areas
to substitute NOX for VOC measures or
more effective control measures for less
effective control measures when doing
so would expedite attainment. Another
commenter urged us to limit the strict
application of subpart 2 measures
because the imposition of such
measures creates economic
disincentives for companies to locate
and expand in nonattainment areas. A
number of commenters stated that they
do not support the vehicle I/M or Stage
II vapor recovery programs and
recommended that we provide States
with flexibility in meeting these
requirements.
Response: Many of the commenters’
suggestions go beyond the application of
an absurd results doctrine and instead
suggest broad waiver of subpart 2
requirements based on a determination
that an alternative or substitute is more
effective. We do not believe that we
have the authority to broadly waive
measures mandated by Congress. As
noted by the Supreme Court, Congress
intended to cabin States’ discretion
when it mandated the specific controls
under subpart 2. See e.g., Whitman, 531
U.S. 484–85. (‘‘Whereas subpart 1 gives
EPA considerable discretion to shape
nonattainment programs, subpart 2
prescribes large parts of them by law’’
and ‘‘EPA may not construe the statute
in a way that completely nullifies
textually applicable provisions meant to
limit discretion’’).
However, as stated in our proposed
rule, we believe that case law may
provide EPA with limited flexibility to
waive federally mandated requirements
on a case-by-case basis where
application of those requirements would
produce an absurd result. We do not
need to conclude here what precise
circumstances would create an absurd
result. Rather, that decision would need
to be made on a case-by-case basis in the
context of a specific request. In general,
we note that to demonstrate an absurd
result, a State would need to
demonstrate that application of the
requirement would result in more harm
than benefit. For example, the programs
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mandated under subpart 2 are generally
effective in reducing emissions of the
two ozone precursors—NOX and VOC—
and because reductions of those
precursors generally lead to improved
air quality, we believe that such a
demonstration could be made, if at all,
only in rare instances.
With regard to the comment relating
to Stage II vapor recovery, section
202(a)(6) of the CAA does provide for
revision or waiver of the Stage II vapor
recovery requirement under certain
conditions: ‘‘The requirements of
section 182(b)(3) (relating to stage II
gasoline vapor recovery) for areas
classified under section 181 as moderate
for ozone shall not apply after
promulgation of such standards and the
Administrator may, by rule, revise or
waive the application of the
requirements of such section 182(b)(3)
for areas classified under section 181 as
Serious, Severe, or Extreme for ozone, as
appropriate, after such time as the
Administrator determines that onboard
emissions control systems required
under this paragraph are in widespread
use throughout the motor vehicle fleet.’’
Currently, EPA is formulating policy
concerning how widespread use will be
determined and has been seeking
participation from affected parties.
Further information is available at:
https://www.epa.gov/ttn/naaqs/ozone/
ozonetech/stage2/.
Comment: A few commenters
disagreed with the approach in our
proposed rule. One commenter stated
that we do not have the statutory
authority to create new waivers to
subpart 2 requirements. Another
commenter stated that the CAA does not
allow case-by-case waivers to avoid
‘‘absurd’’ results. The commenter
further stated that doing so would in
effect require us to rewrite the statute by
regulation.
Response: As stated above, we agree
that we do not have broad authority to
waive subpart 2 requirements and that
the CAA itself does not expressly create
authority to waive such requirements.
However, the ‘‘absurd results’’ line of
cases provides that where application of
a statute as written would create a result
counter to what Congress intended, an
Agency has limited authority to
construe that provision in a manner
than would effectuate Congress’ intent.5
5 See Holy Trinity Church v. United States, 143
U.S. 457 (1892) (‘‘If literal construction of the words
of a statute be absurd, the act must be so construed
to avoid the absurdity.’’); Griffin v. Oceanic
Contractors, Inc. 458 U.S. 564 (1982) (recognizing
the absurdity exemption, but concluding that a
harsh penalty provision did not produce results
counter to Congress’ intent); Mova Pharm. Corp. v.
Shalala, 140 F. 3d 1060 (D.C. Cir. 1998) (recognizing
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B. How will we address long-range
transport of ground-level ozone and its
precursors when implementing the 8hour ozone standard?
[Section VI.F. of June 2, 2003
proposed rule (68 FR 32827); no draft or
final regulatory text.]
1. Background
Interstate transport can make it
difficult or impossible for some States to
meet attainment deadlines for areas
within their boundaries solely by
regulating sources within their own
boundaries. Section 110(a)(2)(D) of the
CAA provides an important tool for
addressing the problem of interstate
transport. It provides that a State must
include adequate provisions in its SIP to
prohibit sources within the State from
emitting air pollutants in amounts that
contribute significantly to
nonattainment, or interfere with
maintenance, in one or more downwind
States. Section 110(k)(5) of the CAA
authorizes EPA to find that a SIP is
substantially inadequate to meet any
CAA requirement, including the
requirements of section 110(a)(2)(D) of
the CAA. If we make such a finding, we
must require the State to submit, within
a specified period, a SIP revision to
correct the inadequacy. The CAA
further addresses interstate transport of
pollution in section 126, which
authorizes any State to petition EPA to
regulate emissions from significant
upwind sources of air pollutants in
other States.
In addition to requiring States to
control interstate air pollution under
section 110(a)(2)(D), the CAA requires
States with nonattainment areas to
develop State plans under part D that
provide for meeting the NAAQS as
expeditiously as practicable, and for
maintaining healthy air quality in those
areas over time. Together, the section
110(a)(2)(D) and part D provisions
provide for upwind State and in-State
controls to ensure that national healthbased air quality standards are met and
maintained.
2. Current Approach
In the NOX SIP Call Rule, EPA found
the SIPs for certain States in the eastern
U.S. to be substantially inadequate to
address emissions transported to
downwind States and required those
States to select and adopt control
measures to meet statewide ozoneseason NOX emissions budgets based on
highly cost-effective NOX emissions
the absurdity exemption, but finding that a
‘‘successful defense’’ regulation went beyond the
statute was not necessary to meet Congressional
intent.)
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reductions (63 FR 57356, October 27,
1998.) In that rule, we determined that
the same level of emissions reductions
was needed to address transport for both
the 1-hour and 8-hour standards.6
The NOX SIP Call Rule is achieving
substantial emissions reductions and air
quality improvement well in advance of
the attainment dates of 8-hour
nonattainment areas. In the eastern
United States, monitoring data shows a
10 percent improvement between 2002
and 2004 in the seasonal (May–
September) average of daily maximum
8-hour ozone concentrations, after
adjustment for meteorological
differences. The EPA believes that the
NOX reductions achieved as a result of
the NOX SIP Call are an important factor
in this improvement. The compliance
date for achieving the required NOX
reductions under phase I of the NOX SIP
Call was May 31, 2004. All of the 19
affected States and the District of
Columbia submitted complete Phase I
SIPs, which EPA approved, in response
to the NOX SIP Call and are
implementing their NOX control
programs. State programs to implement
the rule have focused on reducing
emissions from electric power
generators and large industrial emitters.
The phase II NOX SIP Call Rule, which
responds to court decisions on issues
from the original SIP call rule involving
certain types of sources and geographic
coverage, requires additional emissions
reductions by May 1, 2007.
The EPA’s modeling for the CAIR
indicates that ozone levels across the
eastern half of the country will improve
substantially by 2010 because of
existing requirements—including the
NOX SIP call, federal motor vehicle and
nonroad engine regulations, and other
existing State and federal rules. Last
year, EPA designated more than 100
areas in that region as having ozone
levels not meeting the 8-hour ozone
standard, based on 2001–2003 data. Air
quality improvements due to existing
requirements (i.e., without State
measures required for areas designated
nonattainment for the 8-hour standard)
are projected to leave only 16 of these
areas in nonattainment in 2010. This
estimate is derived from base case CAIR
modeling results shown in the final
notice for the CAIR (70 FR 25254, Table
VI–12).
On May 12, 2005, EPA published the
Clean Air Interstate Rule in the Federal
Register (70 FR 25162). The EPA
determined that 28 States and the
District of Columbia contribute
6 In light of various challenges to the 8-hour
NAAQS, we stayed the 8-hour basis for the NOX SIP
Call Rule (65 FR 56245; September 18, 2000).
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significantly to downwind
nonattainment, or interfere with
maintenance, of the PM2.5 and 8-hour
ozone NAAQS in other States. The rule
requires these States to submit SIP
revisions to reduce SO2 and/or NOX
emissions.
To reduce interstate ozone transport,
the rule established statewide ozoneseason NOX budgets for 25 States and
the District of Columbia. The budgets
are based on the level of emissions that
can be achieved through highly costeffective controls that EPA determined
are available from EGUs; however,
States have flexibility to choose the
measures they will use to achieve the
necessary emissions reductions. Due to
feasibility constraints, EPA is requiring
the CAIR budgets to be achieved in two
phases. For summertime NOX, the first
phase starts in 2009 (covering 2009–
2014); 7 the second phase of NOX
reductions begins in 2015 (covering
2015 and thereafter).
The 25 States that are required to
meet a summertime NOX cap for ozone
purposes, along with the District of
Columbia, are Alabama, Arkansas,
Connecticut, Delaware, Florida, Illinois,
Indiana, Iowa, Kentucky, Louisiana,
Maryland, Massachusetts, Michigan,
Mississippi, Missouri, New Jersey, New
York, North Carolina, Ohio,
Pennsylvania, South Carolina,
Tennessee, Virginia, West Virginia, and
Wisconsin.
The CAIR is geographically broader
and more stringent than EPA’s previous
ozone interstate transport rule, the NOX
SIP Call, adopted in 1998.8 The CAIR’s
ozone requirements are based on
updated analyses of the impacts of
pollution transported across State
borders, and of highly cost-effective
control opportunities for NOX.
As detailed in the final CAIR action,
the CAIR rule will further reduce ozone
transport to assist States in their efforts
to bring ozone nonattainment areas into
attainment or—in the case of downwind
receptor areas that attain prior to some
or all CAIR reductions—maintain air
quality meeting the 8-hour ozone
NAAQS. In the CAIR rulemaking, EPA
projected that 39 counties (in the 16
nonattainment areas referenced above)
would have ozone levels exceeding the
7 The CAIR first phase also provides an annual
NOX budget, which also starts in 2009.
8 The CAIR requires summertime NO reductions
X
in the following States not covered by the NOX SIP
Call: Arkansas, Florida, Iowa, Louisiana,
Mississippi, and Wisconsin. The NOX SIP Call has
requirements for two States not covered by CAIR
ozone requirements: Rhode Island and Georgia. The
EPA has proposed a stay of applicability of the SIP
Call to Georgia as an initial response to a petition
for reconsideration on whether Georgia should be
covered.
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71621
standard in 2010 in the absence of
further control requirements (i.e., the
base case without CAIR). Most of these
counties were projected to be within a
few parts per billion (ppb) of the
standard. For the 39 counties, the
average reduction in ozone levels
estimated from 2009 CAIR NOX controls
is 0.4 ppb, and the maximum
improvement is 1.4 ppb (70 FR 25254,
Table VI–12.) The 2009 CAIR NOX
requirements will achieve reductions
prior to the maximum attainment date
for downwind 8-hour ozone areas
classified as moderate.
We believe that States will be able to
demonstrate timely attainment for most
8-hour ozone nonattainment areas with
the help of emissions reductions from
Federal rules. However, we also believe
that a limited number of downwind
areas, while showing improvement, are
likely to remain in nonattainment after
2009. This is due to the severity of
projected ozone levels in certain areas,
uncertainties about the levels of
emissions reductions that will actually
occur, and persistence of historical
difficulties with attaining the 1-hour
ozone standard. The EPA determined in
the CAIR that even if all downwind
receptor areas attained on time, many
areas will remain close enough to the
standard to be at risk of falling back into
nonattainment. The EPA concluded that
the 2015 summertime NOX reductions
will assist attainment and maintenance
of the 8-hour standard.9
In addition to controlling interstate air
pollution under section 110(a)(2)(D),
EPA national rules and State rules for
controlling local sources of emissions
are significantly reducing, and in the
future will further reduce, the amount of
pollution transported to 8-hour ozone
nonattainment areas in downwind
States. Downwind States, in devising
their attainment and maintenance plans,
will be able to take required upwind
reductions into account. Depending on
the particular area, the upwind
reductions will help to hasten
attainment of the NAAQS, make
attainment and maintenance of the
NAAQS less difficult and costly, or
both.
The EPA notes that interstate
pollution transport will be further
reduced through cost-effective measures
that individual States adopt for
purposes of bringing their ozone
9 For the 22 counties projected to be in
nonattainment in 2015 in the absence of further
control requirements (i.e., the CAIR base case), the
average ozone reduction in 2015 from CAIR is 1.1
ppb, and the maximum improvement is 1.6 ppb. (70
FR 25254, 25455, Table VI–13.)
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nonattainment areas into attainment.10
Given the potential for measures
adopted by one State to improve air
quality downwind, EPA is supportive of
multi-State cooperation on strategies for
attaining the 8-hour standard.
3. Comments and Responses
This section addresses the more
significant comments received; the
response to comment document
addresses other comments also.
Comment: Several commenters
thought the June 2, 2003, 8-hour
implementation proposal failed to
adequately address transport and
disagreed with our statement that 8hour transport has been addressed up
front by the NOX SIP Call. Some added
that this puts northeastern States
located in the OTR in a situation where
their citizens and businesses are bearing
a disproportionate burden of health and
economic impacts compared to upwind
States that have fewer control
requirements than OTR States. Some
OTR State commenters said that the rule
should address this inequity. One said
we cannot assume that transport has
been addressed until after the NOX SIP
Call is implemented and has been
evaluated.
Response: The 8-hour ozone
implementation rule is not intended as
a rule to address interstate transport of
pollution and to achieve emissions
reductions from upwind sources as
provided under CAA section
110(a)(2)(D). Rather, its purpose is to
interpret nonattainment requirements
(in subparts 1 and 2 of part D of title I)
for State plans to implement the 8-hour
NAAQS. We have addressed the section
110(a)(2)(D) obligation through the NOX
SIP Call and CAIR, which provide
substantial air quality benefit for
downwind areas significantly affected
by transport of pollution from other
States.
Comment: Two commenters
recommended a regional approach
among States to address transport. One
commenter thought that Clear Skies is
the best way to address transport, but
absent that, would support a regional
approach. Some commenters thought
the 8-hour ozone implementation
proposal ignored the issue that ozone is
a regional problem that can only be
solved through regional planning. These
commenters added that instead of
incentives for regional planning there
were disincentives. Another commenter
thought that EPA unrealistically expects
10 Many types of sources contribute to ozone
transport. The CAIR reduction requirements are
based solely upon potential reductions from EGUs;
EPA did not find other source types highly cost
effective to control.
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States to be able to resolve all potential
conflicts between the States by working
together in a collaborative process to
identify and adopt appropriate controls
that provide for attainment. The
commenter suggested that EPA
oversight may be necessary in these
situations. One commenter thought the
development of multiple OTRs for
regional planning and coordination may
be highly desirable to bring States with
a common problem together to
coordinate efforts with the strength of
several States rather than to go-it alone.
Another suggested some criteria for EPA
to use if we were to choose to establish
OTRs.
Response: We believe that addressing
interstate transport requires regional
approaches and regional cooperation.
The EPA has ensured regional action to
reduce interstate ozone transport
through the NOX SIP Call Rule and
CAIR. In addition, we note that groups
of States have worked effectively
together in the past to address regional
ozone problems. For example, the Lake
Michigan Air Directors Consortium
(LADCO) was established in 1990 by the
States of Illinois, Indiana, Michigan, and
Wisconsin. The main purpose of
LADCO is to provide technical
assessments for and assistance to its
member States on problems of ozone air
quality and to provide a forum for its
member States to discuss air quality
issues. We will continue to encourage
these multi-State efforts to assess and
address ozone nonattainment and will
work with these States as needed to
provide support and ensure progress.
We agree with other commenters that
States should work together in the SIP
development process to ensure localized
transport is addressed. States that share
an interstate nonattainment area are
expected to work together in developing
the nonattainment SIP for that area and
in reducing emissions that contribute to
local-scale interstate transport problems.
We would also encourage collaborative
efforts even in cases where there is not
a multi-State nonattainment area but
where significant emissions sources in
one State might affect air quality in a
nonattainment area in an adjacent State.
In response to comments suggesting
that EPA establish additional transport
regions, at this time we do not
anticipate formalizing any additional
transport regions. We believe that the
NOX SIP Call and CAIR rules go far to
effectively address the kind of transport
that establishment of a transport region
would be intended to address, without
the costs of setting up a commission to
oversee the transport region.
Comment: Some commenters stated
that we should not rely on the proposed
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Clear Skies legislation to reduce
emissions transport because there is no
guarantee that the legislation will be
enacted. Several State commenters
added that Clear Skies would not
provide adequate or timely emissions
reductions. Another commenter
suggested that we work with Congress to
enact legislation to allow for the
development and use of a transport
argument in attainment demonstrations.
Response: While we still hope that
Congress will adopt the
Administration’s Clear Skies multipollutant legislation, we acknowledge
that the outcome of that process is
uncertain. To ensure that regional
transport is addressed in a timely
manner, EPA finalized the CAIR in May
2005 based on our existing regulatory
authority.
Comment: One commenter proposed
that rather than addressing transport
through national measures, we could
include transport as one of the criteria
for determining the adequacy of a SIP.
This commenter supported the multiState collaborative effort mentioned in
the proposed rule, so that areas work
together to address transport as their
SIPs are being developed. The
commenter asserted that our proposed
early, top-down approach could
significantly hinder SIP planning for
local areas considering the complex
chemistry of ozone and PM2.5 formation.
Response: We believe that the NOX
SIP Call and CAIR help, rather than
hinder, SIP planning for nonattainment
areas. We agree that the CAA does allow
the States to work together in a
collaborative fashion to assess regional
or sub-national transport. The EPA
worked with a State-led effort in the
mid-to late-1990’s [the Ozone Transport
Assessment Group (OTAG) process] to
perform such an assessment, which
documented the magnitude and extent
of long-range transport of ozone and its
precursors. At that time, EPA concluded
that without some certainty of what
levels of emission controls would be
required in the larger region, States
faced great uncertainty regarding the
amounts of ozone and precursor
concentrations being transported into
the modeling domain of the
nonattainment area for which they were
required to develop their attainment
demonstrations. Therefore, EPA issued
the NOX SIP Call—and more recently,
CAIR—to establish the emission
reduction responsibilities of upwind
States under section 110(a)(2)(D). In this
way, eastern States could then have a
fair degree of certainty regarding
required upwind reductions and the
amount of transported emissions to be
assumed in their 1-hour ozone
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attainment demonstrations for
individual nonattainment areas. Based
on the OTAG experience, we believed
that there was high risk that States
working together in a collaborative
fashion would not agree on a regional
control strategy within the time the
CAA provides for States to develop 8hour attainment demonstrations.
Therefore, we believe the commenter is
incorrect that the ‘‘top-down’’ approach
will significantly hinder SIP planning
for the individual areas, and on the
contrary, will provide the certainty
needed to complete the attainment
demonstrations in a timely manner.
The commenter also proposed that
rather than addressing transport through
national measures, we could include
transport as one of the criteria for
determining the adequacy of a SIP. It is
true that section 110(a)(2)(D)(i)(I)
requires a SIP to ‘‘contain adequate
provisions * * * prohibiting, consistent
with the provisions of this title, any
source or other type of emissions
activity within the State from emitting
any air pollutant in amounts which
will—(I) contribute significantly to
nonattainment in, or interfere with
maintenance by, any other State with
respect to any such national primary or
secondary ambient air quality standard
* * *’’ Furthermore, sections 110(a)(1)
and (2) of the CAA require States to
submit SIPs that implement, maintain,
and enforce a new or revised NAAQS
within 3 years of promulgation of the
standard. Among other things, these SIP
revisions must address a State’s
significant contribution of pollution to
nonattainment and maintenance
problems in other States under section
110(a)(2)(D). On March 10, 2005, EPA
officially notified States that they have
failed to submit SIPs to satisfy this
requirement of the CAA with respect to
the 8-hour ozone and PM2.5 NAAQS (70
FR 21147; April 25, 2005). The finding
starts a 2-year clock for EPA to issue a
final Federal Implementation Plan (FIP)
that will address the requirements of
section 110(a)(2)(D) unless a SIP
revision correcting the deficiency is
approved by EPA before the FIP is
promulgated. The EPA plans to issue
guidance regarding how States could
satisfy the section 110(a)(2)(D)
requirement. For States affected by
CAIR, an approved SIP responding to
the CAIR would satisfy the requirement
and turn off the FIP clock.
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C. How will we address transport of
ground-level ozone and its precursors
for rural nonattainment areas, areas
affected by intrastate transport, and
areas affected by international
transport?
[Section VI.G. of June 2, 2003
proposed rule (68 FR 32828); no draft or
final regulatory text.] 11
1. Rural Transport Nonattainment Areas
a. Background
In the June 2, 2003 proposal, we noted
that section 182(h) of the CAA (under
subpart 2) recognizes that the ozone
problem in a rural transport area is
almost entirely attributable to emissions
from upwind areas. This section
provides that the only requirements
applicable to an area classified under
subpart 2 that we determine is a rural
transport area are the minimal
requirements specified for marginal
areas, i.e., those areas expected to attain
within 3 years after designation. The
timing for attainment for these areas
will depend on the schedule for
adoption and implementation of control
measures in the upwind areas. We did
not propose any revision to current
policy and practices related to the rural
transport area provisions under section
182(h).
b. Summary of Final Rule
The final rule does not contain any
revisions to current policy on rural
transport areas under section 182(h).12
c. Comments and Responses
Comment: Several commenters
favored the proposed approach of not
revising our current policies with regard
to subpart 2 areas that meet the criteria
for being a rural transport area under
section 182(h).
Response: We agree with these
comments.
Comment: Several commenters urged
us to provide more flexibility such as
extending the provision to other areas
whose problems are caused by transport
but that do not qualify as rural under
section 182(h).
Response: These commenters did not
suggest any legal mechanism for
11 This section of the proposal also addressed
multi-State nonattainment areas. The discussion of
multi-State nonattainment areas is now covered
under the discussion below on attainment
demonstrations and modeling.
12 Based on current information, we do not
believe there are any 8-hour nonattainment areas
covered under subpart 2 that are ‘‘rural’’ and
therefore eligible for consideration for coverage
under section 182(h). Existing policy on rural
transport areas includes the ‘‘General Preamble for
the Implementation of Title I of the Clean Air Act
Amendments of 1990; Proposed Rule,’’ April 16,
1992 (57 FR 13505).
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71623
granting the flexibility provided under
section 182(h) to areas that do not
qualify as rural under section 182(h).
We have not found any such legal
mechanism and, therefore, the final rule
does not extend the flexibility provided
under section 182(h) to additional areas.
2. Intrastate Transport
a. Background
In the proposed rule, we noted that a
number of State air agency
representatives had voiced concern
about intrastate transport of ozone and
precursor emissions and asked EPA to
address this concern. We indicated that
the CAA requires individual States, as
an initial matter, to deal with intrastate
transport. We also pointed out that a
State could recommend designation of
nonattainment areas that are large
enough to encompass upwind and
downwind areas of the State and require
that the individual jurisdictions work
together on an attainment plan that
accounts for transport and results in
attainment by the attainment date for
the entire nonattainment area. We also
solicited comments on other ways of
addressing intrastate transport within
the context of the CAA provisions.
b. Summary of Final Rule
The final rule does not contain any
additional provisions for addressing
intrastate transport for the reasons
stated in the proposal. However, as
indicated in the Phase 1 Rule published
on April 30, 2004, for subpart 1 areas,
States and EPA could consider intrastate
transport in determining the attainment
date for an area.13 In identifying the
appropriate attainment date for an area,
the State should consider measures to
address intrastate transport of pollution
from sources within its jurisdiction.
c. Comments and Responses
Comment: Two commenters
recommended that States have
regulatory authority to require controls
as necessary regarding the problem of
intrastate transport. They asserted that
nonattainment areas should work with
upwind contributing areas within the
State to address regional transport
within the State.
Response: As provided in the
proposed rule (68 FR 32829), we agree
with the commenters that States have
the obligation and authority to address
the transport of pollution from one area
13 Intrastate transport also could be considered in
determining the attainment date that is as
expeditious as practicable for subpart 2 areas, but
if the date were later than allowed for the area’s
classification, the State would need to request
bump-up of the area to a higher classification for
that date to be approved.
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of the State to a different area of the
State.
Comment: Several comments
recommended an intrastate transport
classification.
Response: Our response to those
comments is in the response to
comment document for the Phase 1 Rule
of April 30, 2004. (Docket document
OAR–2003–0079–0717; p. 68.)
3. How will EPA address transport of
ground-level ozone and its precursors
for areas affected by international
transport?
a. Background
As discussed in the proposal,
international transboundary transport of
ozone and ozone precursors can
contribute to exceedances of the
NAAQS. It is possible that the
international transport of air pollutants
may affect the ability of some areas to
attain and maintain the 8-hour ozone
NAAQS. Section 179B of the CAA
(International Border Areas), applies to
nonattainment areas that are affected by
emissions emanating from outside the
United States. This provision requires
EPA to approve a SIP for an ozone
nonattainment area if it meets all of the
requirements applicable under the CAA,
other than a requirement that the area
demonstrate attainment and
maintenance of the ozone NAAQS by
the applicable attainment date, and the
State establishes to EPA’s satisfaction
that the SIP would be adequate to attain
and maintain the ozone NAAQS by the
applicable attainment date but for
emissions emanating from outside the
United States. The preamble to the
proposed rule recommended that States
should confer with the appropriate EPA
Regional Office to establish on a caseby-case basis the technical requirements
for these analyses.
b. Final Rule
As in the proposal, we are not setting
forth any regulatory provisions related
to international transport. Section 179B
of the CAA applies for these purposes.
We continue to recommend that States
confer with the appropriate EPA
Regional Office to establish on a caseby-case basis the technical requirements
for analyses to support showings under
section 179B. These analyses will be
subject to public comment during the
State and Federal SIP processes.
c. Comments and Responses
Comment: Several commenters
addressed the discussion of
international transport in the proposed
rule. Two commenters suggested that
EPA is placing too high a burden on
States to make a demonstration that a
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nonattainment area would attain but for
international transport (e.g., assessing
emissions from foreign countries). These
commenters stated that EPA has the
appropriate resources and technical
expertise to evaluate international
transport and highlighted certain data
EPA has gathered and modeling EPA
has performed. The commenters
suggested that EPA should re-evaluate
relevant policies regarding section 179B
of the CAA to ensure they are
streamlined and not unnecessarily
burdensome on States in making an
international transport demonstration.
Another commenter thought that the
proposed rule does not adequately
address ozone from international
sources, especially in a situation where
a State does not have jurisdiction over
most of the significant sources of ozone
or access to available data for modeling
in that region. Another commenter
encouraged EPA to expand its view of
the applicability of section 179B and
allow consideration of the impact on
attainment of smoke from crop burning
activities in Southern Mexico and
Central America.
Response: The CAA, not EPA’s
proposed rule, places the burden on
States to demonstrate that an area would
be able to attain but for emissions from
sources located outside the United
States. However, EPA agrees with the
commenters that EPA has been
performing numerous activities that will
provide data that States may be able to
rely on as they develop these
demonstrations. We recognize that
adequate data for foreign sources may
not be available to States. Therefore,
modeling, according to the modeling
guidance for attainment demonstrations,
may not be possible in all cases.
Because the availability of information
and the causes of international pollution
vary significantly from one area to
another, EPA continues to believe that
the best approach for addressing
international transport is for States to
work with EPA on an area-by-area basis
to determine what is the best available
information and the best method for
analysis that fits the unique situation for
each area.
Regarding consideration under
section 179B of the impact on
attainment of smoke from crop burning
activities in Southern Mexico and
Central America, in many cases it may
not be possible to confidently quantify
the impacts to the total ozone loadings
from individual foreign sources that are
hundreds or even thousands of miles
from the U.S. border. Particularly since
1998, when spring fires in Mexico and
Central America were very severe, EPA
has received much information about
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the potential impacts from such
occurrences on ozone and PM levels in
the United States. A prime lesson
learned from those experiences is that a
well-designed, detailed analysis is
required before one can estimate the
degree of influence from such fires. In
many cases, sufficient data will not exist
to draw such a conclusion. Case-by-case
consultation between EPA and the State
will help determine how best to
consider this information in attainment
planning.
With respect to the applicability of
section 179B to areas affected by
emissions from very distant, foreign
sources, EPA currently has not taken a
position. If and when there are any SIP
submittals that request a section 179B
dispensation on such a basis, EPA will
examine those submittals on a case-bycase basis, including focusing on the
sufficiency of the technical
demonstration, in order to make a
determination of section 179B
applicability.
The EPA considers international
transport of pollution an important
issue. The EPA is engaged in several
international efforts that will allow us to
better understand the linkages between
air pollution sources in other countries
and their impacts on public health and
air quality in the United States. The
EPA has cooperative agreements with
both Canada and Mexico to investigate
international border transport. The
information generated by these
partnerships will assist States in
evaluating international transport
affecting 8-hour nonattainment areas.
D. How will EPA address
requirements for modeling and
attainment demonstration SIPs for areas
implementing the 8-hour ozone
standard?
[Section VI.H. of June 2, 2003
proposed rule (68 FR 32830); § 51.908 in
draft and final regulatory text.]
As noted in the proposal, an
attainment demonstration SIP consists
of (1) technical analyses to locate and
identify sources of emissions that are
causing violations of the 8-hour NAAQS
within nonattainment areas (i.e.,
analyses related to the emissions
inventory required for the
nonattainment area), (2) adopted
measures with schedules for
implementation and other means and
techniques necessary and appropriate
for attainment, (3) commitments, in
some cases, to perform a mid-course
review (MCR), and (4) contingency
measures required under section
172(c)(9) of the CAA that can be
implemented without further action by
the State or the Administrator to cover
failures to meet RFP milestones and/or
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attainment. The final rule retains three
of these four elements, the exception
being the requirement for a commitment
to perform a MCR. As noted below, EPA
will assess whether a MCR is needed on
a case-by-case basis in reviewing
individual attainment demonstrations.
In the Phase 1 Rule, § 51.908
contained only the requirement related
to the timing of implementation of the
emissions reductions needed for
attainment. In today’s final rule, that
provision is retained as paragraph (d) of
§ 51.908, and other requirements related
to modeling and attainment
demonstrations appear in the remaining
paragraphs of § 51.908.
In the proposal, we also solicited
public comment on the guidance related
to multi-pollutant assessments (as
discussed below), areas with earlier and
later attainment dates, MCR, modeling
guidance, and multi-State
nonattainment areas. These topics are
discussed below. Associated with the
attainment demonstration also are the
RFP/ROP plans and the SIP submission
concerning RACM, both of which we
discussed elsewhere in the preamble to
the proposed rule and which are
discussed in later sections of this
preamble.
1. Areas With Early Attainment Dates
a. Background
The proposal noted that under section
182(a), marginal areas, which have a
maximum attainment date of 3 years
after designation, are not required to
perform a complex modeling analysis
using photochemical grid modeling. We
noted that areas covered under either
subpart 1 or 2 with ozone
concentrations close to the level of the
NAAQS [e.g., within 0.005 parts per
million (ppm)] 14 will most likely come
into attainment within 3 years after
designation as nonattainment without
any additional local planning as a result
of national and/or regional emission
control measures that are scheduled to
occur. We noted that regional scale
modeling for national rules, such as the
NOX SIP Call and Tier II motor vehicle
tailpipe standards, projects major ozone
benefits for the 3-year period of 2004–
2006. Attainment for many areas
classified as marginal is further
indicated by subsequent modeling used
to support the CAIR. This 3-year period
coincides with the period that would be
used to determine whether an area
attains the 8-hour standard within 3
14 Even though the June 2, 2003 proposal
contained the reference to the 0.005 ppm criterion,
the draft regulatory text issued for public comment
did not contain a reference to this criterion.
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years after designation for areas
classified as marginal.
If existing modeling for a marginal
area does not indicate the area will
attain with the current planned control
measures, EPA encouraged the areas to
request reclassification to moderate and
encouraged the State or Tribe to develop
an attainment demonstration using
photochemical grid modeling. (See 68
FR 32831; June 2, 2003.) Even though
modeling is not required, it may be
prudent.
In the proposal, we noted that many
subpart 1 areas are projected through
regional modeling to come into
attainment within 3 years after
designation with current control
programs. Therefore, we proposed that
no additional modeled attainment
demonstration would be required for
areas with air quality observations close
to the level of the standard and where
regional or national modeling exists that
is appropriate for use to demonstrate the
area will attain the 8-hour standard
within 3 years after designation (i.e.,
based on data from 2004–2006).
We proposed that areas subject only
to subpart 1 may request an attainment
date no later than 3 years following
designation for the 8-hour NAAQS by
submitting within 1 year of the
designation a SIP that demonstrates the
area will attain within 3 years following
designation. The demonstration must
include modeling results and analyses
that the State is relying on to support its
claim. Such modeling must be
consistent with EPA guidance and must
be appropriate for the area.
b. Summary of Final Rule
Although we proposed that subpart 1
areas requesting an attainment date
within 3 years after designation should
submit their attainment demonstration
within 12 months, we have removed
that provision from the final rule. A
subpart 1 area is free to choose to
submit its attainment demonstration at
any time prior to the 3-year due date.15
As is the case with all required
attainment demonstrations, the
demonstration must be submitted no
later than 3 years following designation
and must be appropriate for use in the
area. We anticipate that most subpart 1
areas will be included in the modeling
analyses conducted by areas with later
15 The EPA notes that 8-hour ozone
nonattainment areas are also free to develop early
SIPs with motor vehicle emissions budgets for
transportation conformity purposes in advance of a
complete SIP attainment demonstration. For more
information on establishing an early 8-hour ozone
SIP and how it could be used for conformity, please
refer to EPA’s July 1, 2004, conformity final rule (69
FR 40019).
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71625
attainment dates. States are encouraged
to use these available analyses, as well
as future EPA national or regional
modeling. The demonstration must
include modeling results and analyses
that the State or Tribe is relying on to
support its claim. Such modeling
should be consistent with EPA guidance
and should be applicable and
appropriate for the area.16 If acceptable
available modeling does not
demonstrate attainment, the area would
need to submit a local modeled
attainment demonstration.
c. Comments and Responses
Comment: Several commenters
recommended that the requirement for
attainment demonstrations from all
subpart 1 areas be eliminated.
Response: Section 172(c)(1) clearly
requires that nonattainment areas
‘‘* * * shall provide for attainment of
the national primary ambient air quality
standards.’’ To meet this requirement, a
State must demonstrate that the area
will attain by a specified date and
identify and adopt the control measures
that will bring the area into attainment.
We see no authority for waiving this
requirement for areas.
Comment: What are the requirements
for subpart 1 areas requesting
attainment dates within 3 years of
designation?
Response: Subpart 1 areas must
submit their attainment demonstrations
within 3 years after designation.
2. Areas With Later Attainment Dates
a. Background
For areas with attainment dates of
more than 3 years after designation,
regardless of whether they are covered
under subpart 1 or subpart 2 (except
marginal areas), we proposed to require
them to submit an attainment
demonstration SIP. This proposal was
reflected in § 51.908(b) and (c) of the
draft regulatory text. We stated that
local, regional and national modeling
developed to support Federal or local
controls could be used provided the
modeling is consistent with EPA’s
modeling guidance. Several States have
invested considerable time and
resources in regional 8-hour ozone
modeling projects following this
guidance. Where exceedances of the 8hour ozone standard are more pervasive
and widespread than they were for the
1-hour ozone standard, we
recommended that States work together
in multi-State modeling efforts and
16 If an assessment indicates that a regional
modeling analysis is not applicable to a particular
nonattainment area, additional local modeling
would be required.
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leverage off work under development
and resources spent on these projects.
b. Summary of Final Rule
Subpart 1 areas with attainment dates
later than 3 years after designation and
areas classified as moderate or higher
under § 51.903, are required to submit
an attainment demonstration no later
than 3 years after the effective date of
designation for the 8-hour ozone
NAAQS. Areas with an effective date of
designation of June 15, 2004 are
required to submit an attainment
demonstration no later than June 15,
2007. These demonstrations must be
consistent with section 51.112,
including appendix W. In addition, for
the review of technical adequacy, we
will generally rely on our most recent
modeling guidance at the time the
modeled attainment demonstration is
performed. We will be making available
a final version of the modeling guidance
related to developing attainment
demonstrations for the 8-hour ozone
standard.17
Areas required to submit an
attainment demonstration are
encouraged to follow the procedures
described in this guidance. Local,
regional and national modeling
developed to support Federal or local
controls generally may be used provided
the modeling is consistent with EPA’s
modeling guidance at the time the
modeled attainment demonstration is
performed.18
c. Comments and Responses
We received no comments on this
topic per se; comments on the timing of
submission of attainment
demonstrations is discussed elsewhere.
We noted in the proposal that comments
on the modeling guidance were
welcome at any time and that we would
consider those comments in any future
revision of that document. We noted
that comments submitted on the
modeling guidance document would not
be docketed as part of this rulemaking,
17 U.S. EPA, (November 4, 2005), Guidance on the
Use of Models and Other Related Analyses in
Attainment Demonstrations for the 8-Hour Ozone
NAAQS, EPA–454/R–05–002, https://www.epa.gov/
ttn/scram, (Modeling Guidance, File name: ozonefinal.pdf).
18 The guidance may not apply to a particular
situation, depending upon the circumstances. The
EPA and State decision makers retain the discretion
to adopt approaches on a case-by-case basis that
differ from this guidance where appropriate. Any
decisions by EPA regarding a particular SIP
demonstration will only be made based on the
statute and regulations, and will only be made
following notice and opportunity for public review
and comment. Therefore, interested parties will be
able to raise questions and objections about the
contents of this guidance and the appropriateness
of its application for any particular situation.
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nor would a comment/response
summary of these comments be a part of
the final 8-hour ozone implementation
rule since they will not affect the rule
itself. We will address those comments
at the time we issue the final modeling
guidance.
3. Multi-State Nonattainment Areas
a. Background
As discussed in the June 2003
proposal, section 182(j) of the CAA
defines a multi-State ozone
nonattainment area as an ozone
nonattainment area, portions of which
lie in two or more States. Section
182(j)(1)(A) and (B) set forth certain
requirements for such areas. First, each
State in which a multi-State ozone
nonattainment area lies must take all
reasonable steps to coordinate the
implementation of the required
revisions to SIPs for the given
nonattainment area [section
182(j)(1)(A)]. Next, section 182(j)(1)(B)
requires the States to use photochemical
grid modeling or any other equally
effective analytical method approved by
us for demonstrating attainment. We are
prevented by section 182(j) from
approving any SIP revision submitted
under that section if a State has failed
to meet the above requirements.
To address the provisions of section
182(j)(1)(A), States that include portions
of a multi-State ozone nonattainment
area should develop a joint work plan
as evidence of early cooperation and
integration. The work plan should
include a schedule for developing the
emissions inventories, and the
attainment demonstration for the entire
multi-State area. Each State within a
multi-State ozone nonattainment area is
responsible for meeting all the
requirements relevant to the given area.
Care should be taken to coordinate
strategies and assumptions in a modeled
area with those in other, nearby
modeled areas in order to ensure that
consistent, plausible strategies are
developed.
Section 182(j)(2) for multi-State
nonattainment areas recognizes that one
State may not be able to demonstrate
attainment for the nonattainment area if
other States in which portions of the
nonattainment area are located do not
adopt and submit the necessary
attainment plan for the area. In such
cases, even though the area as a whole
would not have an approvable
attainment demonstration, the sanction
provisions of section 179 will not apply
in the portion of the nonattainment area
located in a State that submitted an
attainment plan.
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b. Summary of Final Rule
As discussed in the proposal, State
partners involved in a multi-State ozone
nonattainment area must work together
to perform the appropriate modeling
analyses to identify control measures
that will enable the area to achieve
attainment as expeditiously as
practicable. Each State will be
responsible for its portion of the control
program and therefore will be held
accountable for controls identified for
implementation within its State
boundaries. The modeling analyses
should encompass the entire multi-State
nonattainment area as well as adjacent
counties which may contribute to the
nonattainment problem. State plans
should address local transport within
the region and its contribution to
nonattainment in the multi-State area.
Consideration of long-range transport
and its contributions to nonattainment
is discussed in section IV.B. of this
preamble. Multi-State nonattainment
areas are subject to the same modeling
and attainment demonstration
requirements of the final rule that apply
to all other areas. Marginal multi-State
nonattainment areas do not have to
submit a modeled attainment
demonstration because section 182(a)
exempts marginal areas from the
requirement to submit an attainment
demonstration.
c. Comments and Responses
Comment: Several commenters
encouraged us to clearly define in the
rule how multi-State nonattainment
areas will be treated if all or a portion
of an area is subject only to subpart 1.
One of these commenters requested a
clarification that photochemical grid
modeling will not be required for multiState areas classified under subpart 1 or
areas that are classified as marginal. The
commenter’s reasoning was that such
modeling is unnecessary since they are
close to achieving the 8-hour NAAQS
and will be in attainment before the
modeling can be completed.
Response: We agree with these
commenters that since section 182(a)
exempts marginal areas from the
requirement to submit an attainment
demonstration, such areas need not
develop an attainment demonstration.
Section 182(j) of the CAA requires that
multi-State areas use photochemical
grid modeling as part of their attainment
demonstrations while Section 172
(Subpart 1 areas) of the CAA does not
explicitly require photochemical grid
modeling. For subpart 1 areas that do
not seek an attainment date of 3 years
or less after designation, we make no
distinction between multi-State and
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single-State subpart 1 nonattainment
areas. All subpart 1 nonattainment areas
are required to submit an attainment
demonstration that relies on
photochemical grid modeling, either
one that has already been performed
that is appropriate for use in the area,
or a new one. We do not believe that
techniques other than those based on
photochemical grid modeling will
provide credible assurance that an area
will achieve the 8-hour ozone standard
by the area’s attainment date.
Comment: One commenter requested
that we perform the modeling for multiState areas. Two commenters stated that
if any additional photochemical
modeling is required for such areas
pursuant to CAA 182(j)(1)( B), then EPA
should refine previous modeling;
perform new modeling; or approve a
less resource-intensive, alternate
method that fulfills the requirement.
The commenters asserted that we
should assist the States in coordinating
the development of the attainment/
maintenance plans and ensure that areas
involving multiple EPA Regions are not
hampered by jurisdictional conflicts and
inconsistencies.
Response: The EPA has conducted,
and will continue to conduct, regional
and national scale modeling that covers
most of the ozone nonattainment areas.
Both single State and multi-State
nonattainment areas will be able to
make use of EPA modeling, where
appropriate. The EPA will work with
States to determine the steps necessary
for the proper use of EPA modeling in
a local attainment demonstration. States
that plan to use EPA modeling in lieu
of local modeling should be prepared to
justify the local use of the regional
projections as well as conduct
additional analyses to monitor progress
towards attainment. The EPA will
continue to work with States to
coordinate the development of
consistent attainment/maintenance
plans.
State to develop and submit a modeled
attainment demonstration.19
We noted that section 182(c)(2)(A)
provides that for serious and higherclassified areas the ‘‘attainment
demonstration must be based on
photochemical grid modeling or any
other analytical method determined by
the Administrator, in the
Administrator’s discretion, to be at least
as effective.’’ A photochemical grid
model should meet several general
criteria for it to be a candidate for
consideration in an attainment
demonstration. We noted that, unlike in
previous guidance,20 we did not
propose recommending a specific
photochemical grid model for use in the
attainment demonstration for the 8-hour
NAAQS for ozone. At present, there is
no single model which has been
extensively tested and shown to be
clearly superior or easier to use than
other available models. Criteria for
attainment demonstrations are
contained in 40 CFR 51.112, including
appendix W (i.e., ‘‘EPA’s Guideline on
Air Quality Models,’’ 68 FR 18440,
April 15, 2003). Appendix W refers to
EPA’s ‘‘Use of Models and Other
Analyses in Attainment Demonstrations
for the 8-Hour Ozone NAAQS’’ and lists
a set of general requirements that an air
quality model should meet to qualify for
use in an attainment demonstration for
the 8-hour ozone NAAQS.21 The
proposal described alternatives
available to the States and the scope and
coverage of the draft guideline. The
draft regulatory text of 2003 addressed
this requirement in § 51.908(d).
We noted that we were planning to
make substantial changes to the draft
version of this document before
finalizing the attainment demonstration
aspects of the implementation rule. We
said we welcomed public comments on
the guidance at any time and would
consider those comments in any future
revision of the document. However, we
said we would not consider comments
4. Role of Modeling Guidance in
Attainment Demonstrations
19 As noted above in the discussion of subpart 1
areas with early attainment dates, although the draft
regulatory text in § 51.908(a) was structured such
that no attainment demonstration was needed for
subpart 1 areas that received an attainment date
within 3 years after the effective date of the
nonattainment designation, this was misleading,
since the draft § 51.904(b)(2) provision that affected
these areas required submission of a demonstration
of attainment within 3 years after designation. The
final regulatory text in § 51.908(b) clarifies this
point.
20 U.S. EPA, (1991), Guideline for Regulatory
Application of the Urban Airshed Model, EPA–450/
4–91–013. Available at: https://www.epa.gov/
scram001/tt25.htm; see document DRAFT8HR.
21 U.S. EPA, (May 1998), Draft Guidance on the
Use of Models and Other Analyses in Attainment
Demonstrations for the 8-Hour Ozone NAAQS,
EPA–454/R–99–004, https://www.epa.gov/ttn/scram,
(Modeling Guidance, File name: DRAFT8HR).
a. Background
The proposal noted that section
182(b)(1)(A) requires ozone
nonattainment areas to develop an
attainment demonstration which
provides for reductions in VOC and
NOX emissions ‘‘as necessary to attain
the national primary ambient air quality
standard for ozone.’’ Section 172(c),
requires areas covered under subpart 1
to demonstrate attainment. For a subpart
1 area that does not qualify for an
attainment date within 3 years after
designation, we proposed to require the
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71627
on the technical merits of the modeling
guidance in this present rulemaking.
b. Summary of Final Rule
The final rule [§ 51.908(c)] requires
each attainment demonstration to be
consistent with the provisions of
§ 51.112, including appendix W to 40
CFR part 51. In addition, we will
generally review the demonstrations for
technical merit using EPA’s most recent
modeling guidance at the time the
modeling relied on in the attainment
demonstration is performed. This
guidance will generally have the State
provide (1) technical analyses to locate
and identify sources of emissions that
are causing violations of the 8-hour
NAAQS within nonattainment areas, (2)
adopted measures with schedules for
implementation and other means and
techniques necessary and appropriate
for attainment that are needed for
attainment, with implementation no
later than the beginning of the
attainment year ozone season 22 (e.g.,
prior to 2009 ozone season for areas
with June 15, 2010 attainment dates),
and (3) contingency measures required
under section 172(c)(9) of the CAA that
can be implemented without further
action by the State or the Administrator
to cover emissions shortfalls in RFP
plans and failures to attain.
c. Comments and Responses
Comment: One commenter
recommended that EPA must ensure
that attainment demonstrations are
based on scientifically valid regional
airshed modeling rather than
scientifically invalid linear proportional
rollback and weight-of-evidence
methods.
Response: Criteria for attainment
demonstrations are contained in 40 CFR
51.112, including appendix W (i.e.,
‘‘EPA’s Guideline on Air Quality
Models,’’ 68 FR 18440, April 15, 2003).
Appendix W cites EPA’s ‘‘Use of Models
and Other Analyses in Attainment
Demonstrations for the 8-Hour Ozone
NAAQS’’ and describes a set of general
criteria that an air quality model and its
application should meet to qualify for
use in an attainment demonstration for
the 8-hour ozone NAAQS.23 The draft
guidance was developed through a
collaborative process, which included
review from the scientific community,
and it has been revised to reflect recent
review comments. The procedures
described are considered a scientifically
22 See
40 CFR 51.900(g) for definition.
EPA, (1998), Draft Guidance on the Use of
Models and Other Analyses in Attainment
Demonstrations for the 8-Hour Ozone NAAQS,
EPA–454/R–99–004, https://www.epa.gov/ttn/scram,
(Modeling Guidance, File name: DRAFT8HR).
23 U.S.
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valid use of regional and urban airshed
modeling. The modeled attainment test
makes use of the model derived
relationship between ozone and its
precursors. It does not, as is the case
with proportional rollback, assume
equal proportions of the precursors will
provide an equally proportional
reduction in ozone. For example, it does
not assume that 20 percent reduction in
precursors will provide 20 percent
improvement in ozone.
The guidance also identifies
additional data which, if available,
should enhance the credibility of model
results and results of other analyses
used in a weight of evidence
determination. The EPA believes use of
weight of evidence is appropriate as do
many in the scientific community.
Weight of evidence is a credible
approach for considering inherent
uncertainties in a modeling application.
As noted above, we will be making
available a final version of the modeling
and attainment demonstration guidance
for the 8-hour ozone standard.24
Comment: All attainment
demonstrations should be subject to the
same rigorous standards.
Response: The EPA envisions that the
final 8-hour ozone modeling guidance
will be available for use by the majority
of subpart 1 areas and subpart 2 areas
classified as moderate and above.
However, due to the unique nature of
the ozone problem in many areas, EPA
will accept various applications of the
guidance. Although EPA anticipates all
areas will follow the guidance closely,
there will be variation based on
availability of new and improved data
methods and field study data. The EPA
is always striving to make best use of
available data and improvements in
methodologies as the science and our
understanding of ozone formation and
transport in different parts of the
country increases. Unique to many areas
is the source receptor configuration,
level of precursor data collected and the
model’s ability to simulate unique
factors influencing the formation and
transport of ozone. As more information
becomes available in particular areas,
EPA expects more rigorous
demonstrations will be provided. Areas
close to attaining the standard for which
there is a better understanding of the
meteorology and the relationships
between precursor emissions and ozone
may not require as much rigor. These
decisions will be made on a case-bycase basis and the public will be able to
24 U.S. EPA, (2005), Guidance on the Use of
Models and Other Related Analyses in Attainment
Demonstrations for the 8-Hour Ozone NAAQS,
EPA–454/R–05–002, https://www.epa.gov/ttn/scram,
(Modeling Guidance, File name: ozone-final.pdf).
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express their views during the State SIP
development and EPA review process.
Comment: The EPA cannot adopt or
change the Draft Guidance, use it for
regulatory purposes, or require States to
use it for regulatory purposes, without
subjecting it to separate notice-andcomment rulemaking.
Response: The final rule [§ 51.908(c)]
requires each attainment demonstration
to be consistent with the provisions of
40 CFR 51.112, including appendix W.
However, we are not adopting the
Guidance as a rule. The EPA plans to
use the current (2005) guidance and
future updates as a benchmark for
reviewing the technical analysis
submitted in support of 8-hour ozone
attainment demonstrations. The
guidance document is not a regulation.
Therefore, it does not impose binding,
enforceable requirements on any party,
and may not apply to a particular
situation based upon the circumstances.
The EPA and State decision makers
have the discretion to adopt approaches
on a case-by-case basis that differ from
this guidance where appropriate. Any
decisions by EPA regarding adequacy of
a particular SIP to meet the 8-hour
ozone NAAQS will be based on the
CAA and our regulations. Therefore,
interested parties are free to raise
questions and objections about the
appropriateness of the application of
this guidance to a particular situation
during the State SIP development and
EPA review process.
Comment: One commenter requested
an opportunity to review and comment
on the revised guidance prior to the
‘‘final’’ release.
Response: States, Tribes and others
were given an opportunity to comment
on the revised draft guidance prior to
release. Also, EPA received additional
comments on the draft guidance during
the comment period on the
implementation rule. The EPA has
reviewed and considered the comments
and will be releasing the final guidance.
For more information and updates to the
modeling guidance for ozone, visit
EPA’s Technology Transfer Network
Support Center for Regulatory Air
Models (TTN/SCRAM) on the Internet,
https://www.epa.gov/ttn/scram/. Even
though the guidance will be issued in
final form shortly, EPA is always open
to suggestions for future improvements
to the guidance, including the
incorporation of methodologies and
procedures that increase accuracy and
credibility of results. Such suggestions
may be made to EPA regional or
headquarters modeling contacts listed at
the above TTN/SCRAM web site.
Comment: The EPA should carefully
consider the resources that will be
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needed to perform the requisite
modeling for multiple areas in many
States.
Response: States/Tribes are
encouraged to share and leverage
resources currently being used in
regional model applications that affect
multiple areas. There is much
opportunity for common use of data and
methodologies among the modeling
requirements for the regional haze
program, the PM2.5 attainment
demonstrations and the ozone
attainment demonstrations that should
make the overall exercise less onerous.
States and Tribes are encouraged to
model multiple precursor strategies for
multiple areas and review their efficacy
for all three programs.
Comment: Any photochemical grid
model utilized must either be in the
public domain or licensed for unlimited
use by any person for purposes of
modeling within the area.
Response: The EPA modeling
guidance supports this comment which
is addressed in section 10 of the
modeling guidance. ‘‘Applicable
models’’ may be used, if they are nonproprietary. A ‘‘non-proprietary’’ model
is one whose source code is available for
free or for a reasonable cost. Further, the
user must be free to revise the code to
perform diagnostic analyses and/or to
improve the model’s ability to describe
observations in a credible manner.
Comment: One commenter
recommended that EPA update its
guidance in 40 CFR 51, appendix W to
include a discussion of the role of
weight-of-evidence as part of a modeling
demonstration, and to make any updates
in appendix W subject to public review.
Response: In regard to the role of
weight of evidence, EPA does not plan
to revise appendix W. Use of weight of
evidence is dependent on local
information only available when the
technical analysis for a specific model
application is under development.
Therefore, use of weight of evidence is
considered on a case-by-case basis as
the appropriate Regional Office works
with the State as it develops its SIP and
during the State adoption process and
during EPA’s SIP approval process. Any
weight of evidence analysis is available
for public review.
5. Mid-Course Review (MCR)
a. Background
The proposal noted that a MCR
provides an opportunity to assess
whether a nonattainment area is or is
not making sufficient progress toward
attainment of the 8-hour ozone
standard, as predicted in its attainment
demonstration. We noted that a
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commitment to perform a MCR is a
critical element of an attainment
demonstration that employs a long-term
projection period and relies on weight
of evidence. Because of the uncertainty
in long-term projections, we said we
believed such attainment
demonstrations need to contain
provisions for periodic review of
monitoring, emissions, and modeling
data to assess the extent to which
refinements to emission control
measures are needed.
A number of States participated in a
consultative process with EPA, which
resulted in the development of the 1hour MCR guidance.25 We noted that we
would update the 1-hour MCR policy
and technical guidance to include 8hour metrics and that we were soliciting
comment on appropriate revisions. We
proposed that the final MCR guidance
incorporating 8-hour metrics would be
available at the time we issue our final
implementation rule.
The proposal briefly described the
procedure for performing a MCR. The
proposal noted that States would not
have to commit in advance to adopt new
control measures as a result of the MCR
process. Based on the MCR, if we
determine sufficient progress has not
been made, we would determine
whether additional emissions
reductions are necessary from the
State(s) in which the nonattainment area
is located or upwind States or both. We
would then require the appropriate
State(s) to adopt and submit new
measures to bring about the necessary
emissions reductions within a specified
period. We anticipated that these
findings would be made as calls for SIP
revisions under section 110(k)(5) and,
therefore, the period for submission of
the measures would be no longer than
18 months after the EPA finding. Thus,
we proposed that States complete the
MCR 3 or more years before the
applicable attainment date to ensure
that any additional controls that may be
needed can be adopted in sufficient
time to reduce emissions by the start of
the ozone season in the attainment year.
b. Summary of Final Rule
The final regulatory text does not
contain a requirement for the MCR. In
reviewing attainment demonstrations
from individual States, however EPA
will assess the need for a MCR for areas
with an attainment date beyond 6 years
25 Memorandum of March 28, 2002, from Lydia N.
Wegman and J. David Mobley, re: ‘‘Mid-Course
Review Guidance for the 1-Hour Ozone
Nonattainment Areas that Rely on Weight-ofEvidence for Attainment Demonstration.’’ Located
at URL: https://www.epa.gov/scram001/guidance/
guide/policymem33d.pdf.
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after the effective date of the area’s
designation in the context of whether
the attainment demonstration and any
weight of evidence analysis is
supportable without a commitment by
the State to perform a MCR.
The 8-hour ozone modeling
guidance 26 is expected to identify
measurements and activities to support
subsequent reviews of an attainment
demonstration SIP (i.e., MCR), such as
improvements in air quality monitoring,
meteorology and emission
measurements. Even though the
proposal noted that we expected to
revise the existing 1-hour MCR
guidance, EPA now believes the 1-hour
MCR guidance coupled with the 8-hour
modeling guidance provides sufficient
guidance. States should consult with
EPA prior to using a methodology other
than the one developed through the
public consultative process.
Guidance for performing a MCR for
the 1-hour ozone NAAQS identifies
several methods for reviewing whether
the existing SIP is sufficient for the area
to attain by its attainment date.27 These
guidance documents should provide
adequate information for developing
protocols for performing MCRs for the 8hour ozone NAAQS. States/Tribes
should prepare protocols which identify
analyses and data bases to be used to
support a MCR and discuss these with
the appropriate EPA Regional Office
prior to performing a MCR. If we
determine that additional guidance is
needed, we will issue updated guidance
in a timeframe suitable to support the
timely completion of MCRs.
71629
c. Comments and Responses
Comment: Requiring the MCR 3 or
more years prior to the attainment date
is not reasonable or feasible for some
areas. The EPA needs to recognize that
for moderate and lower classifications
the MCR would be due at the time of the
SIP submittal. Mid-course review
should be required only for areas with
nonattainment classifications of serious
or greater, as at least 3 years of
monitored data are required for a MCR,
after the implementation of controls.
One commenter recommended that EPA
make the MCR process part of the
requirements for RFP and ROP.
Response: The final regulatory text
does not require a MCR; as noted above,
EPA will assess on a case-by-case basis
whether a MCR would be needed in the
context of a particular attainment
demonstration.
Comment: The EPA should develop
proper analysis techniques so that
meteorological conditions do not affect
a nonattainment area’s perceived
progress towards attainment. A MCR
should also include an evaluation of
ozone transport into the nonattainment
area and control implementation in
upwind areas.
Response: Assessments of transport
are covered in the MCR guidance. The
EPA is improving methods for
determining the ozone trends and how
they are affected by meteorology. The
latest information will be made
available.
Comment: The EPA needs to release
the revised MCR guidance before the
final rule is issued in order for it to be
reviewed and commented on during the
public comment period.
Response: The final rule does not
incorporate any MCR guidance by
reference. The 8-hour ozone modeling
guidance 28 is expected to identify
measurements and activities to support
subsequent reviews of an attainment
demonstration SIP (i.e., MCR), such as
improvements in air quality monitoring,
meteorology and emission
measurements. Guidance for performing
a MCR for the 1-hour ozone NAAQS
identifies several methods for reviewing
whether a SIP is on track to attain
within prescribed time limits.29 These
guidance documents should provide
adequate information for developing
protocols for performing MCRs for the 8hour ozone NAAQS. States/Tribes
should prepare protocols which identify
analyses and data bases to be used to
support a MCR and discuss these with
the appropriate EPA Regional Office
prior to performing a MCR. If we
determine that additional guidance is
needed, we will issue updated guidance
in a timeframe suitable to support
completion of MCR’s within established
deadlines.
26 U.S. EPA, (2005), Guidance on the Use of
Models and Other Related Analyses in Attainment
Demonstrations for the 8-Hour Ozone NAAQS,
EPA–454/R–05–002, https://www.epa.gov/ttn/scram,
(Modeling Guidance, File name: ozone-final.pdf).
27 Memorandum of March 28, 2002, from Lydia N.
Wegman and J. David Mobley, re: ‘‘Mid-Course
Review Guidance for the 1-Hour Ozone
Nonattainment Areas that Rely on Weight-ofEvidence for Attainment Demonstration.’’ Located
at URL: https://www.epa.gov/scram001/guidance/
guide/policymem33d.pdf.
28 U.S. EPA, (2005), Guidance on the Use of
Models and Other Related Analyses in Attainment
Demonstrations for the 8-Hour Ozone NAAQS,
EPA–454/R–05–002, https://www.epa.gov/ttn/scram,
(Modeling Guidance, File name: ozone-final.pdf).
29 Memorandum of March 28, 2002, from Lydia N.
Wegman and J. David Mobley, re: ‘‘Mid-Course
Review Guidance for the 1-Hour Ozone
Nonattainment Areas that Rely on Weight-ofEvidence for Attainment Demonstration.’’ Located
at URL: https://www.epa.gov/scram001/guidance/
guide/policymem33d.pdf.
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Federal Register / Vol. 70, No. 228 / Tuesday, November 29, 2005 / Rules and Regulations
6. Multi-Pollutant Assessments (OneAtmosphere Modeling) 30
b. Summary of Final Rule
a. Background
The proposal noted that many factors
affecting formation and transport of
secondary fine particles (i.e., PM2.5
components) are the same as those
affecting formation and transport of
ozone. The proposal, therefore, noted
that models and data analysis intended
to address visibility impairment need to
be capable of simulating transport and
formation of both secondary fine
particles and ozone. At a minimum,
modeling should include previously
implemented or planned measures to
reduce ozone, secondary fine particles,
and visibility impairment. An integrated
assessment of the impact controls have
on ozone, secondary fine particles, and
regional haze provides safeguards to
ensure ozone controls will not preclude
optimal controls for secondary fine
particles and visibility impairment.
The concept of modeling control
impacts on all three programs is further
strengthened by the alignment of the
implementation process for ozone and
secondary fine particles. As the dates for
attainment demonstration and planning
SIPs for the three programs are
anticipated to be fairly close, the
practicality of using common data bases
and analysis tools for all three programs
is viable and encourages use of shared
resources.
The proposal noted that States that
undertake multi-pollutant assessments
as part of their attainment
demonstration would assess the impact
of their ozone attainment strategies on
secondary fine particles and visibility or
perform a consistent analysis for ozone,
secondary fine particles, and visibility.
To facilitate such an effort, we
encouraged States to work closely with
established regional haze Regional
Planning Organizations (RPOs) and the
jurisdictions responsible for developing
PM2.5 implementation plans. We
encouraged States to perform similar
multi-pollutant assessments as part of
their ozone attainment demonstrations,
considering the control programs that
are in place at the time of the
assessment. Multi-pollutant assessments
are discussed elsewhere in this
proposed rulemaking.
30 Use of models that are capable of simulating
transport and formation of multiple pollutants
simultaneously. For example, for ozone and fine
particles, it is critical that the model simulate
photochemistry, which includes interactions among
the pollutants and their precursors.
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There is no regulatory text on the
issue of multi-pollutant assessments,
but we recommend the following:
• Attainment demonstration
modeling should include previously
implemented or planned measures to
reduce ozone, secondary fine particles,
and visibility impairment.
• An integrated assessment of the
impact controls have on ozone,
secondary fine particles, and regional
haze is encouraged to promote
efficiencies in strategies for achieving
all three goals.
• States are also encouraged to use
common data bases and analysis tools
for all three programs and work closely
with established regional haze RPOs
and the jurisdictions responsible for
developing PM2.5 implementation plans.
• States are encouraged to follow
EPA’s lead and perform similar multipollutant assessments as part of their
ozone attainment demonstrations,
considering the control programs that
are in place at the time of the
assessment.
c. Comments and Responses
Comments: The EPA received several
comments on the recommendation that
States perform multi-pollutant
assessments as part of their ozone
attainment demonstrations. Almost all
of the comments agreed with the basic
rationale behind encouraging an
analysis of the expected ozone, PM2.5,
and visibility impacts of a given set of
air quality control measures associated
with an 8-hour ozone attainment
demonstration. The comments differed
on whether multi-pollutant assessments
should be required or only encouraged.
The commenters who urged EPA to
encourage rather than require a multipollutant assessment provided reasons
for why they believe a multi-pollutant
assessment is not possible at this time.
One commenter indicated that the
proposal was unclear as to whether the
multi-pollutant assessments were
required.
One commenter recommended that
EPA require, in certain unspecified
cases, nonattainment areas to perform
an integrated control strategy
assessment to ensure that ozone controls
will not preclude optimal controls for
secondary fine particles and visibility
impairment. Conversely, several other
commenters expressed the opinion that
the multi-pollutant assessment should
not be a requirement of an ozone
attainment demonstration. Several
reasons were offered for why the
assessment should remain optional: (1)
That the state of the science for
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assessing PM2.5 and visibility is not yet
sufficient for providing meaningful
input to the regulatory process, (2) that
the additional resources necessary to
model the atmosphere as a single system
would result in an undue burden on the
States, and (3) that requiring a PM2.5 and
visibility assessment would result in
delayed attainment due to the
additional time necessary to complete
such an analysis.
Response: The EPA continues to
believe that encouraging, but not
requiring, multi-pollutant assessments
is the most sound approach for total air
quality management given the schedule
by which ozone attainment
demonstrations are legally required.
Much progress has been made on
improving the available PM2.5 models
and inputs to these models over the past
3 years. As a result, EPA believes that
the available tools are able to support air
quality planning. Further improvements
are likely over the next several years;
much of which will be driven by the
RPO’s. By working closely with the
appropriate RPO’s, States can reduce the
burden associated with one-atmosphere
modeling analyses. However, EPA
recognizes that many States have
already invested resources in an ozoneonly modeling platform analysis which
is typically conducted over a finite
number of episode days and for
geographic regions that are typically less
than (in time) and smaller than (in
space) what might be required in a
multi-pollutant assessment. By
encouraging States to consider such
assessments, EPA hopes to speed the
process of the transition to more
integrated air quality planning tools
while yielding sound multi-pollutant
control strategies. It is prudent for areas
to perform these multi-pollutant
assessments earlier as it will lessen the
planning burden in the long-term since
later planning activities for PM2.5 and
regional haze will need to consider the
effects of emission control measures
adopted for the ozone attainment plan.
7. What baseline emission inventory
should be used for the attainment
demonstration?
[Not addressed in the June 2, 2003
proposal; § 51.909 of the draft regulatory
text.]
The June 2, 2003 proposal did not
discuss baselines for purposes of the
attainment demonstration. (It did,
however, discuss baselines for RFP
demonstrations.) Section 51.909 of the
draft regulatory text provided that 2002
should be used as the baseline emission
inventory year for purposes of both RFP
and the attainment demonstration for
areas with an effective date of
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designation of June 15, 2004. We
recognize, however, that some areas
have already begun to perform modeling
for their attainment demonstrations
using baseline year inventories earlier
than the 2002 inventory, and because
the 2002 inventory may not be in a
format to readily be used for
photochemical grid modeling.31
Therefore, the final rule does not specify
a baseline for purposes of the attainment
demonstration and modeling. As
discussed more fully in the section of
the preamble regarding RFP, the
specification of 2002 as a baseline year
for RFP purposes (for areas with an
effective date of designation of June 15,
2004) appears in the RFP provisions of
40 CFR 51.910. Section 51.909 remains
reserved.
areas’ 8-hour classification,32 and
because the Phase 1 final
implementation rule for the 8-hour O3
NAAQS contains anti-backsliding
provisions generally requiring areas to
continue implementing measures
required for the 1-hour classification.
Although there may not be additional
mandatory control measures required
because the areas may already have
such measures in place, an area that
needs more time to attain may need
additional emission reductions to reach
attainment.
8. Voluntary Reclassifications (‘‘BumpUps’’)
1. General Discussion
Although we believe most 8-hour
nonattainment areas will attain the
standard by their statutory attainment
date, we recognize that some areas
classified under subpart 2 may need
additional time beyond the statutory
attainment date for their area to attain
as expeditiously as practicable. As
discussed in the Phase 1 Rule (69 FR at
23959, col. 3), in the event an area
cannot practicably attain by the
maximum date for its classification, the
Clean Air Act provides the opportunity
for more time. An area regulated under
subpart 2 can receive a later maximum
attainment date through a State request
to bump-up to a higher classification
(e.g. from moderate to serious). The Act
requires EPA to grant a State request to
reclassify an area to a higher
classification; the State plan still must
provide for attainment as expeditiously
as practicable. Although bump-up
means that certain additional specified
requirements apply, an area may already
be meeting most or all of these specified
requirements due to controls previously
adopted to implement the 1-hour ozone
standard. This is because some areas
had 1-hour classifications that were
higher (and more restrictive) than the
31 The
EPA guidance on baseline years is found
in the memorandum of November 18, 2002, from
Lydia Wegman and Peter Tsirigotis, ‘‘2002 Base
Year Emission Inventory SIP Planning: 8-hr Ozone,
PM2.5 and Regional Haze Programs.’’ This document
is available at the following Web site: https://
www.epa.gov/ttn/oarpg/meta.442.1.202baseinv.pdf.
That document noted, ‘‘The EPA is aware that some
areas have already begun on a voluntary basis to
model for purposes of the 8-hour ozone standard.
These areas may continue to use modeling from
previous base years for each set of meteorological
episode conditions for use in their SIP submittals
if these studies are still applicable for an attainment
demonstration.’’
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E. What requirements for RFP should
apply under the 8-hour ozone standard?
[Section VI.I. of June 2, 2003 proposed
rule (68 FR 32832); § 51.909 and
§ 51.910 in draft; § 51.910(d) in final
regulatory text.]
a. Background
As noted in the June 2, 2003 proposal,
section 172(c)(2), which is located in
subpart 1, requires State plans for
nonattainment areas to require RFP.
Section 171(1) of the CAA defines RFP
to mean ‘‘such annual incremental
reductions in emissions of the relevant
air pollutant as are required by this part
[part D of title I] or may reasonably be
required by the Administrator for the
purpose of ensuring attainment of the
applicable [NAAQS] by the applicable
date.’’
Subpart 2 provides more specific RFP
requirements for ozone areas classified
under section 181.33 In particular,
subpart 2 specifies the base year
emissions inventory upon which RFP is
to be planned for and implemented, the
increments of emissions reductions
required over specified time periods,
and the process for determining whether
the RFP milestones were achieved.
Subpart 2 does not specify RFP
requirements for marginal areas. Section
182(b)(1)(A) mandates a 15 percent VOC
emission reduction, accounting for
growth, between 1990 and 1996 for
moderate and above ozone
nonattainment areas. Furthermore,
32 Although some 8-hour ozone nonattainment
areas have additional areas beyond the boundary of
the former 1-hour nonattainment area and thus
would be faced with new requirements for the
higher classification.
33 Note that § 51.900 provides the following
definitions:
(p) Reasonable further progress (RFP) means for
the purposes of the 8-hour NAAQS, the progress
reductions required under section 172(c)(2) and
section 182(b)(1) and (c)(2)(B) and (c)(2)(C) of the
CAA.
(q) Rate of progress (ROP) means for purposes of
the 1-hour NAAQS, the progress reductions
required under section 172(c)(2) and section
182(b)(1) and (c)(2)(B) and (c)(2)(C) of the CAA.
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71631
section 182(c)(2)(B) of the CAA requires
each serious and above ozone
nonattainment area to submit a SIP
revision providing for an actual VOC
emission reduction of at least 3 percent
per year averaged over each consecutive
3-year period beginning in 1996 until
the area’s attainment date (referred to as
the post-1996 ROP plan for the 1-hour
standard). Section 182(c)(2)(C) of the
CAA allows for substitution of NOX for
VOC emissions reductions for
reductions required under section
182(c)(2)(B). The EPA’s policy, NOX
Substitution Guidance (December 15,
1993; available at https://www.epa.gov/
ttn/oarpg/t1pgm.html), addresses the
substitution of NOX emissions
reductions for VOC emissions
reductions. The baseline emissions
inventory for determining the required
ROP reductions for the 1-hour standard
is specified in section 182 as 1990.
The requirements for RFP under
subparts 1 and 2, as described above, are
the minimum required for an area. More
reductions may be necessary for
attainment within the nonattainment
area. Moreover, an upwind area that
contributes to nonattainment in a
downwind area in the same State may
need reductions in order for the
downwind area to reach attainment by
its required attainment date. As we
noted above in section IV.D.8., we
recognize that some areas classified
under subpart 2 may need additional
time beyond the statutory attainment
date for their current classification to
attain the 8-hour standard as
expeditiously as practicable. In the
event an area cannot practicably attain
by the maximum date for its
classification, the CAA provides the
opportunity for more time. An area
regulated under subpart 2 can receive a
later maximum attainment date through
a State request to bump-up to a higher
classification (e.g. from moderate to
serious). Although a higher
classification would mandate additional
control measures, in fact there may not
be additional mandatory control
measures required because the area may
already have such measures because of
its classification for the 1-hour standard
and the anti-backsliding provisions.
However, an area that needs more time
to attain may also need additional
emissions reductions to reach
attainment. These reductions may be
achieved through implementation of
measures that are necessary to
demonstrate RFP requirements or
additional reductions beyond RFP may
be needed. Preliminary analyses
indicate that already required control
measures (e.g., motor vehicle and
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nonroad-engine rules, CAIR, etc.) may
largely or fully fulfill RFP requirements
for many areas and that they will
provide substantial progress toward
attainment for most areas.
Many areas may have significant
creditable reductions as a result of
Federal motor vehicle and nonroad
rules, the NOX SIP Call, and the CAIR.
With the statutory exceptions
enumerated above, assured emissions
reductions that will occur in an area
after the base year can be credited
toward meeting an RFP emission
reduction milestone.
To reduce interstate ozone transport,
the CAIR (described above in section
IV.B.) established statewide ozoneseason NOX budgets for 25 States and
the District of Columbia (i.e., the eastern
part of the U.S. where all 8-hour
nonattainment areas are classified as
moderate or below). As noted above, the
first phase of NOX reductions under
CAIR starts in 2009 (covering 2009–
2014); the second phase of NOX
reductions begins in 2015 (covering
2015 and thereafter).
With respect to timing of reductions,
the following table shows how
summertime NOX reductions from local
CAIR sources that will be achieved by
May 1, 2009, or earlier can assist in
demonstrating RFP.
Type of 8-hour nonattainment area
RFP requirement *
Relationship of CAIR and RFP
—Subpart 1 areas with attainment dates within
5 years of designation;
—Subpart 2 moderate areas for which of expeditious attainment is no later than 5 years
after designation.
Subpart 1 areas with attainment dates 6–10
years from designation.
Subpart 2 marginal areas ...................................
Meet RFP through showing of expeditious attainment.
CAIR reductions not required prior to ozone
season preceding latest attainment date.
Must demonstrate RFP through their attainment date.
No subpart 2 RFP requirement for marginal
areas.
Subject to RFP similar to subpart 1 areas;
must demonstrate RFP through their attainment date.
15% VOC reduction required between 2002
and 2008; continued progress required
through attainment date.
CAIR reductions in 2009 can help fulfill RFP
requirement.
Not applicable.
Subpart 2 moderate areas with an attainment
date later than 5 years after designation.
Subpart 2 moderate-and-above areas that did
not implement 15% VOC reductions for 1hour ozone standard.
CAIR NOX reductions in 2009 can help fulfill
RFP requirement.
CAIR 2009 NOX reductions can help demonstrate continued progress after 2008 attainment date.
* RFP requirement descriptions in table are abbreviated; RFP requirements are more precisely described elsewhere in preamble and rule text.
The CAIR provisions do not require
States to require emissions reductions
prior to January 1, 2009. However,
States may choose to require or some
sources may elect to apply CAIR-level
NOX controls earlier than that date. If
such controls are made enforceable in
the SIP (e.g., through a specific rule), the
State may take RFP credit for such
emissions reductions for the RFP period
(i.e., an RFP period ending earlier than
December 31, 2008) during which the
reductions occur.
The RFP provisions in the CAA for
both subpart 1 and subpart 2 areas
require that actual emissions be reduced
from the baseline by the milestone year.
Only emissions reductions required to
be achieved during an RFP period may
be credited toward the State’s RFP
obligation for that period. In developing
their RFP plans, States will have to
provide their best estimate of the CAIRaffected sources that are expected to
actually reduce emissions to meet the
CAIR requirements and those that are
expected to meet CAIR through holding
allowances and not actually reducing
emissions.
Local CAIR NOX reductions that
States must require by May 1, 2015,
could assist in meeting RFP for an area
that is bumped up to severe and
demonstrates attainment cannot be
achieved before the end of the 2015
ozone season.
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b. Summary of Final RFP Features
We are adopting nearly all the
approaches set forth in our proposed
rule for the various 8-hour RFP issues.
We are making exceptions where
convincing arguments were presented
by commenters for a suitable alternative
or where, through reassessment of the
issue, EPA was able to develop a better
option that still reflects the concepts in
the original proposal. The issues for
which we have adopted approaches that
vary from the proposal are: (a) The
timing of the submission of the RFP
plan; (b) the structuring of RFP
requirements in subpart 1 areas; (c) the
implementation of RFP in areas
designated for the 8-hour ozone
standard that entirely or in part
encompass an area that was designated
nonattainment for the 1-hour ozone
standard; and (d) the substitution of
controls from outside the nonattainment
area within 100 kilometers (km) for VOC
and 200 km for NOX. These changes are
discussed in the sections below.
In developing an approach for
addressing the RFP requirements for the
8-hour ozone standard, we are adopting
the following:
• The same baseline year would be
used both to address growth (in
emissions, vehicle miles traveled (VMT)
or otherwise) and to calculate the RFP
target level. The baseline year of 2002
applies for areas with an 8-hour ozone
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nonattainment designation effective in
June 2004.
• Emissions reductions from outside
the nonattainment area up to 100 km for
VOC and 200 km for NOX (and
statewide for areas that are part of a
regional strategy) would be allowed
consistent with (a) the concepts in
EPA’s existing December 1997 interim
implementation policy for 1-hour ozone
NAAQS 34, and (b) with the constraint
that in all cases the distances in the
policy provide only a general policy
presumption that, if used, would need
data in the record showing that
reductions from sources in the specific
locations outside the nonattainment
area benefit the nonattainment area.
This is discussed further below in
section IV.E.12. of this preamble.
• For all 8-hour nonattainment areas
classified under subpart 2 as moderate
34 Memorandum of December 29, 1997 from
Richard D. Wilson to Regional Administrators,
Regions I–X re ‘‘Guidance for Implementing the 1Hour Ozone and Pre-Existing PM10 NAAQS.’’
Located at URL: https://www.epa.gov/ttn/oarpg/t1/
memoranda/iig.pdf. This policy recognized that
VOC emissions up to 100 km and NOX emissions
up to 200 km from the nonattainment area could be
relied on for RFP. Those distances resulted from
Federal Advisory Committee Act discussions cited
earlier and generally represent transport of 1 to 2
days. We still believe it is appropriate to allow this
credit. However, as noted below, because we
received concerns about this policy outside the
rulemaking process, we are in the process of
subjecting this policy to a technical review and may
revise it in light of that review.
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and above that had not met the 15
percent VOC emission reduction
requirement for the 1-hour standard, the
RFP requirements specified in subpart 2
would apply, namely a 15 percent VOC
emission reduction, accounting for
growth, in the first 6 years after the
baseline year for moderate and above
ozone nonattainment areas. In addition,
for all 8-hour nonattainment areas
classified as serious and above, the RFP
provisions in subpart 2 require a VOC
or NOX emission reduction of at least
three percent per year averaged over
each consecutive 3-year period
beginning 6 years after the baseline year.
(See section 182(c)(2)(B)).
• Areas classified under subpart 2 as
moderate that had met the 15 percent
VOC emission reduction requirement
for the 1-hour standard are treated in the
final rule like areas covered under
subpart 1.
• Areas classified under subpart 2 as
serious and above that had met the 15
percent VOC emission reduction
requirement for the 1-hour standard
would be subject to the RFP
requirement in section 172(e) and the
final rule would require them to obtain
an average of 3 percent annual
reductions of VOC and/or NOX
emissions reductions for the first 6 years
after the baseline year and every
subsequent 3 years out to their
attainment date.
• The periods for RFP under subpart
2 for the 8-hour ozone NAAQS run from
the date of the baseline year, and would
be equivalent to the periods Congress
established in subpart 2, which applied
for the 1-hour NAAQS. Thus, the first
15 percent reduction would be required
for the 6-year period starting after the
end of the last day of the baseline year
(e.g., January 1, 2003–December 31,
2008). The first 3-year period for the
subsequent (average of) three percent
per year emission reduction
requirement in serious and higher areas
would begin 6 years after the end of the
last day of the baseline year (e.g.,
January 1, 2009–December 31, 2011).
However, the last period for any area
would end on the attainment date for
the area.
• Subpart 1 areas with attainment
dates 5 years or less after designation
can meet the RFP requirement by
achieving the emission reductions
necessary to attain as expeditiously as
practicable. These emissions reductions
must be implemented by the beginning
of the full ozone season prior to the
attainment date (See 40 CFR § 1.908).35
For subpart 1 areas with attainment
35 With today’s rulemaking, this provision is now
codified as 40 CFR 51.908(d).
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dates beyond 5 years after designation,
the RFP SIP must provide for a 15
percent emission reduction (either NOX
and/or VOC) from the baseline year
within 6 years after the baseline year.
For each subsequent 3-year period out
to the attainment date, the RFP SIP
would have to provide for an additional
increment of progress. The increment
for each 3-year period would be a
portion of the remaining emission
reductions needed for attainment
beyond those reductions achieved for
the first increment of progress (e.g.,
beyond 2008 for areas designated
nonattainment in June 2004).
Specifically, the amount of reductions
needed for attainment should be
divided by the number of years needed
for attainment after the first increment
of progress in order to establish an
‘‘annual increment.’’ For each 3-year
period out to the attainment date, the
area must achieve roughly the portion of
reductions equivalent to three annual
increments.36
• Subpart 2 moderate or higher areas
that had not met the 15 percent VOC
reduction requirement under the 1-hour
standard would be subject to section
182(b)(1) for the 8-hour standard and
would need to obtain the emissions
reductions within 6 years after the
baseline year (e.g., for areas designated
in June 2004, the reductions would need
to occur by the end of 2008, based on
a baseline year 2002).
• Reductions from any Federal and
regional measures promulgated after
1990 (except those measures that were
not creditable under the CAAs
creditability provisions (section
182(b)(1)(D)) and achieved after the
baseline year are creditable for the RFP
requirement.
• Allow use of the ‘‘Clean Data
Policy.’’
c. Comments and Responses
This set of comments and responses
on our proposal on RFP are of a general
nature. Comments and responses on
specific topics appear with the sections
below on those topics.
Comment: One commenter stated that
EPA’s proposed 8-hour ozone rule
36 For example, if the area’s attainment date is
2014, and a total of 30 percent reduction is needed
between the end of 2008 and the attainment date
(a 6-year period) to reach attainment, the ‘‘annual
increment’’ would be 5 percent (i.e., 1⁄6 of 30
percent). Thus, the area must achieve roughly the
portion of reductions equivalent to three annual
increments or 15 percent during the first 3 years
(2009, 2010, 2011), and the remaining amount over
the next 3 years (2012, 2013, 2014). Additional
discussion of what is meant by ‘‘roughly
proportional’’ appears in he full discussion of RFP
for subpart 1 areas in section IV.E.7. of this
preamble.
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would sharply slow momentum to
implement health protective emission
reduction strategies in areas with
unhealthful air quality. It would curtail
the effectiveness of transportation
conformity in areas with inadequate air
quality, including both old and new
ozone nonattainment areas. It would do
this by proposing to eliminate any
further RFP requirements for pollution
reduction in existing 1-hour ozone
areas.
Response: The EPA has developed
anti-backsliding provisions to ensure
continuing progress toward attainment
of the ozone NAAQS. Under these
provisions, areas that are nonattainment
for the 8-hour standard must continue to
meet most obligations for the 1-hour
standard, including RFP requirements.
Those provisions (adopted as part of the
Phase 1 Rule published April 30, 2004)
will ensure areas maintain progress in
achieving emissions reductions in areas
with unhealthful air quality.
Additionally, 8-hour ozone
nonattainment areas with attainment
dates later than 5 years after designation
must meet specified increments of
reductions as provided in more detail
below.
Comment: Another commenter
recommends that EPA not strictly
interpret the CAA requirement of a 15
percent reduction in VOC in the first 6
years. If reductions in VOC would not
assist the area in progress toward
attainment and if an area can provide an
analysis that it is at least as sensitive to
NOX controls, then the area should be
able to reduce NOX emissions for RFP
requirements.
Response: We addressed in general
those comments that recommended
alternatives to the mandatory measures
of subpart 2 (which includes the RFP
requirement) in the response to
comments above under the topic,
‘‘Should prescribed requirements of
subpart 2 apply in all 8-hour
nonattainment areas classified under
subpart 2, or is there flexibility in
application in certain narrowly-defined
circumstances?’’ We conclude in that
section that EPA has no discretion to
broadly waive mandatory requirements.
However, we noted that case law may
provide support for case-by-case
waivers where implementation of a
measure would produce an absurd
result.
Comment: One commenter stated that
EPA should consider highly reactive
VOC reductions that achieve ozone
reductions equivalent to an average of 3
percent per year reduction of VOC and/
or NOX as meeting RFP requirements.
Response: The CAA’s RFP provisions
do not appear to provide for variations
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in the required percent reduction in
VOC based on differences of reactivity
of the various VOC compounds.
However, EPA is participating with a
group called the Reactivity Research
Working Group, along with
representatives from States, industry
and universities, to study the scientific
aspects of reactivity and to try to
determine if more cost-effective and
greater ozone reductions can be
achieved through use of the concept.
The requirement to obtain the required
percent reduction of total VOCs
remains, and if EPA decides to propose
a change, it would be undertaken in a
separate rulemaking action.
2. What is the content and timing of the
plan for addressing the RFP
requirements under section 182(b)(1)
and 182(c)(2)(B) for areas covered under
subpart 2?
[Section VI.I.3 of June 2, 2003
proposed rule (68 FR 32833);
§ 51.910(a)(1)(ii) of the draft and final
regulatory text.]
a. Background
Section 182(b)(1) requires areas
classified as moderate and above to
submit a plan to achieve a 15 percent
reduction in VOC emissions over a 6year period following the baseline year.
Section 182(c)(2)(B) requires serious and
above areas to achieve an average of
nine percent additional emissions
reductions for each subsequent 3-year
period. We proposed two options
regarding how this requirement might
apply for purposes of implementing the
8-hour NAAQS.
(i) Option 1. Require 15 percent VOC
reductions within 6 years after the
baseline year for all areas designated
moderate and above for the 8-hour
ozone NAAQS. After 6 years, all serious
and above areas would be required to
achieve a nine percent reduction in
VOC and/or NOX emissions every 3
years, i.e., an average of three percent
per year, until attainment.
(ii) Option 2. For those areas that have
an approved 15 percent plan for their 1hour ozone SIPs, an additional 15
percent VOC reduction is not necessary.
Subpart 2 areas that have approved 15
percent plans for the 1-hour ozone
standard would be considered to have
met the statutory 15 percent
requirement. Instead, such an area that
is classified as moderate for the 8-hour
standard would be subject to the general
RFP requirements of subpart 1 in the
same manner as subpart 1 areas. Such
an area that is classified as serious and
above for the 8-hour standard would be
subject to the RFP requirement in
section 182(c)(2)(B) and would have to
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include in their SIPs an RFP plan that
would achieve an average of three
percent per year of VOC and/or NOX
over each 3-year period starting at the
end of the baseline year out to their
attainment year.
We recognized in the proposal that for
serious and above areas it would be
difficult to adopt and implement
emission controls that would provide
for the first nine percent emission
reduction within 3 years after
nonattainment designation. Therefore,
consistent with what Congress did
under section 182(b)(1), we proposed to
allow the first RFP increment to be
averaged over 6 years. We proposed that
an area classified serious or above
submit its RFP plan within 2 years after
designation such that it provides for 18
percent emissions reductions (VOC and/
or NOX) over the first 6 years from the
baseline year (e.g., January 1, 2003 to
December 31, 2008 using the proposed
2002 baseline year). Then, within 3
years after designation, submit a plan
that provides 9 percent emissions
reductions (VOC and/or NOX) over each
of the next 3-year periods until the
area’s attainment date (e.g., from
January 1, 2009 to the attainment date).
The proposal noted that this option
recognizes previous efforts by areas that
submitted 15 percent plans as required
under the 1-hour ozone NAAQS and
provides flexibility to States to use a
mix of NOX and VOC reductions as
appropriate to meet the additional ROP/
RFP requirements. For many areas of the
country, particularly in the Eastern U.S.
outside major metropolitan areas, there
is a greater need for NOX reductions
rather than VOC reductions to bring
about reduced ambient ozone levels.
Areas do not have the flexibility to
control NOX under the 15 percent
requirement—NOX substitution is only
allowed under section 182 for the post1996 RFP requirement (three percent
per year averaged over 3 years). We
believe that the statute can be
interpreted to require the mandatory 15
percent VOC reduction only once for a
given area.
Once the 15 percent VOC reduction
requirements have been met, an area
would instead be subject to the other
RFP requirements of the CAA. In some
cases, such as for serious and above
areas, this might result in an obligation
to achieve greater emissions reductions,
i.e., 18 percent rather than 15 percent
for the 6-year period, but the area would
have the flexibility to choose either VOC
or NOX reductions as appropriate. We
indicated in the proposal that we
preferred this second option because it
provides more flexibility for the RFP
plan to be consistent with the area’s
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needs in attaining the standard. The
draft regulatory text incorporated this
option.
The proposal did not specifically
address an 8-hour area that is partially
comprised of one or more 1-hour ozone
nonattainment areas with approved 15
percent plans and one or more areas that
were not previously subject to the 15
percent requirement.
b. Summary of Final Rule
We are adopting the second option
described in the Background above, as
adjusted in response to comment.
1. Final rule for 8-hour areas
comprised in total of one or more 1-hour
nonattainment areas with approved 15
percent plans for the 1-hour standard.
Those 8-hour areas that are composed
entirely of one or more 1-hour areas that
have approved 15 percent plans for their
1-hour ozone SIPs, will be considered to
have met the 15 percent VOC
requirement in section 182(b)(1). Such
areas that are classified as moderate
would instead be subject to the more
general RFP requirements of subpart 1.
As discussed below, the subpart 1
requirement would depend on the
moderate area’s attainment date as
follows:
• Moderate areas that have an
attainment date of 5 years or less after
their 8-hour designation, for which all
portions of the area have previously met
their 15 percent requirements under the
1-hour standard, will be subject to
subpart 1 RFP requirements, which will
be satisfied with measures that
demonstrate attainment as expeditiously
as practicable.
• Moderate areas that have an
attainment date beyond 5 years after
their 8-hour designation, for which all
portions of the area have previously met
their 15 percent requirements under the
1-hour standard, will be subject to
subpart 1 RFP requirements, which will
be satisfied with a plan to demonstrate
15 percent emissions reductions (which
may be either VOC or NOX or a
combination of both) from 2002 to 2008,
and any additional emission reductions
needed for attainment beyond 2008.
Such areas that are classified as
serious or above would be subject to the
RFP requirements of section 182(c)(2)(B)
and would need to submit a plan
achieving an average of 3 percent
reductions per year over the 6 years
following the baseline year and then an
average of 3 percent per year for each
subsequent 3-year period out to the
attainment year.37
37 As discussed below in section 5 (the discussion
of the timing of submission of the RFP plan) the
RFP plan would have to be submitted within 3
years after designation (not 2 years as proposed).
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2. Final rule for 8-hour areas
comprised in part of one or more 1-hour
attainment areas with an approved 15
percent plan for the 1-hour standard and
in part of one or more areas without
approved 15 percent plans for the 1hour standard.
For 8-hour moderate areas that
include all or part of one or more 1-hour
areas with an approved 1-hour 15
percent plan, but also include areas that
were not subject to the 1-hour 15
percent plan, the final rule would allow
the area to choose between two
alternative approaches that are
consistent with the proposed rule.
• Approach 1. Develop a new
baseline and new 8-hour 15 percent
VOC ROP emission reduction target for
the entire 8-hour area. Emissions
reductions that occur after the 2002
baseline emissions inventory year are
creditable except as limited by section
182, as described elsewhere in this final
rule. The reductions must be of VOC
only.
• Approach 2.
• Treat the 8-hour nonattainment area
as divided between portions of the area
that are subject to an approved 15
percent VOC-only plan for the 1-hour
standard and the portions of the area
that are not subject to a 15 percent plan
for the 1-hour standard.
• For those areas not subject to an
approved 15 percent plan for the 1-hour
standard, States must establish a
separate 15 percent VOC target under
subpart 2. VOC emissions reductions to
meet the 15 percent requirement may,
however, come from across the entire 8hour nonattainment area.
• For the portion of the area with an
approved 15 percent plan for the 1-hour
standard, the subpart 1 RFP
requirements will apply if the area is
classified as moderate for the 8-hour
standard and the section 182(c)(2)(B)
RFP requirement will apply if the area
is classified as serious or above for the
8-hour standard. These requirements
would apply as described above for
areas comprised entirely of areas with
approved 15 percent plans for the 1hour standard.
c. Comments and Responses
Comment: One commenter expressed
concern that for a number of subpart 2
areas that were nonattainment for the 1hour standard, especially those
dominated by mobile source emissions
and/or those with existing stringent
stationary source controls, it may be
difficult to achieve another 18 percent
precursor emission reduction within 6
years from the baseline year and then an
additional 3 percent per year precursor
reduction after that until the area’s
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attainment date. Specific areas were
mentioned such as the South Coast
District of California and the HoustonGalveston Area, which the commenter
indicated will be well beyond best
available control technology (BACT)
controls and in some cases at or near
lowest achievable emission rate (LAER)
NOX controls on stationary sources
making them dependent on mobile
source fleet turnover for SIP RFP
emissions reductions. The commenter
further suggested that EPA should have
available approved policy options that
allow areas in such predicaments to
maintain approved SIPs if additional
emissions reductions are not available
to meet RFP requirements and/or if
available emission reduction techniques
might be counterproductive to other
local and regional air quality goals.
Response: We addressed in general
those comments that recommended
alternatives to the mandatory measures
of subpart 2 (which includes the RFP
requirement) in the response to
comments above under the topic,
‘‘Should prescribed requirements of
subpart 2 apply in all 8-hour
nonattainment areas classified under
subpart 2, or is there flexibility in
application in certain narrowly-defined
circumstances?’’ We concluded in that
section that EPA has no discretion to
broadly waive mandatory requirements.
However, we noted that case law may
provide support for case-by-case
waivers where implementation of a
measure would produce an absurd
result. Additionally, we note that
section 182(b)(1)(A)(ii) specifically
addresses the situation where an area
demonstrates that it cannot achieve the
required 15 percent reduction. It
provides that an area may achieve less
than the 15 percent VOC reduction
required where the State demonstrates
(1) NSR requirements apply as they
would in an area classified as extreme
except that the terms ‘‘major source’’
and ‘‘major stationary source’’ shall
include any source with the potential to
emit at least 5 tpy of VOCs; (2) RACT
is required for all major sources (i.e., a
source with the potential to emit at least
5 tons per year of VOCs; and (3) the plan
includes all measures that can feasibly
be implemented in light of technological
achievability.38
Comment: Another commenter
supported EPA in recognizing the
previous efforts of areas to meet ROP
requirements under the 1-hour standard.
The commenter concurred with EPA’s
38 Section 182(c)(2)(B)(ii) also contains a similar
RFP provision for serious and higher classified
areas that allows less than 3 percent of baseline
emissions each year after the initial 15 percent
reduction after designation and classification.
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preferred option, which allows States
the flexibility to choose a combination
of NOX and VOC strategies to meet ROP/
RFP requirements consistent with an
area’s need to meet the standard.
Response: We agree with the
commenter that if an area has already
met the 15 percent VOC emission
reduction requirement for the 1-hour
standard, the area should not be
required to meet that requirement a
second time for the 8-hour standard but
instead will be subject to the other
applicable RFP provisions of the CAA.
Comment: One commenter preferred
Option 1 as more protective of air
quality and more consistent with the
requirements of the CAA. Option 1
would require States to develop RFP
plans based on severity and local
situation. Option 2 has some attractive
features by recognizing progress that
States have already made. This
commenter believed that Option 2 is
problematic, however, because it relies
on plans developed based on 1990 to
1996 emissions. This time period has
passed.
One commenter believed EPA to be
completely without authority to waive
the 15 percent RFP plan requirement,
which is an explicit mandate of subpart
2. A 15 percent ROP plan under the 1hour standard cannot possibly satisfy
the 15 percent RFP plan obligation for
the 8-hour standard, because the new
RFP requirement is designed to
implement a revised NAAQS and is
measured from a different baseline year.
They further believe that EPA offers no
plausible legal rationale for waiving the
15 percent ROP requirement, and,
indeed, none exists. Moreover, although
the agency proposed to require RFP
demonstrations for the first 6 years for
serious and severe areas, there is no
lawful or rational basis for exempting
moderate areas from this statutory
requirement. Allowing States to rely on
their 1-hour 15 percent ROP
demonstrations is further unsupportable
because those demonstrations are
almost certainly no longer valid.
Response: The EPA acknowledges
that under subpart 2 we must require 15
percent VOC reductions for all moderate
and above areas, but we maintain that
if an area has met this requirement
while subject to section 182(b)(1)(A) for
the 1-hour standard, they will not have
to meet it again for the 8-hour standard.
The EPA believes that the CAA is quite
clear that the SIP must provide for a 15
percent reduction in baseline VOC
emissions for some period after 1990 in
an area subject to section 182(b)(1)(A),
and, consequently, the SIP for any area
newly subject to section 182(b)(1)(A)
must provide for a 15 percent reduction
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in VOC baseline emissions. But, EPA
disagrees that the CAA plainly requires
that the SIP for an area must require a
second 15 percent reduction in VOC
baseline emissions under a revised
ozone standard. The EPA believes that
section 182(b)(1)(A) limits our
discretion only to the extent that we
cannot let the SIP for any area classified
as moderate or worse for the 8-hour
standard avoid a demonstration that the
SIP contains sufficient measures to
achieve a 15 percent reduction in VOC
baseline emissions and further limits
our discretion to allow NOX substitution
for the 15 percent RFP demonstration
requirement under section 182(b)(1)(A).
If serious and above areas have
already met the 15 percent requirement
under the 1-hour standard, they must
meet the next RFP requirement, namely,
the section 182(c)(2)(B) RFP
requirement, which will actually
achieve greater reductions, i.e., 3
percent per year over 6 years for a total
of 18 percent, but they can meet it with
either VOC or NOX reductions. For
moderate areas that have already met
the 15 percent VOC emission reduction
requirement for the 1-hour standard,
EPA believes appropriate RFP under
subpart 1 should be achieved. For
purposes of RFP under subpart 1, there
is nothing that limits such reductions to
VOC. This provision simply requires
reasonable annual incremental
reductions towards attainment by the
applicable attainment date, and this
could be achieved by either VOC or
NOX emissions reductions or a
combination of both.
Section 182(b)(1)(A) is the only
statutory provision that limits State
discretion to substitute NOX reductions
for VOC reductions. This applies only
for purposes of the initial 15 percent
reduction requirement for the 6-year
period after the baseline year.
Comment: Another commenter
believed the subpart 2 provisions of the
CAA do not allow for NOX for VOC
substitutions for the initial 15 percent
RFP requirements.
Response: We agree that the 15
percent requirement in section 182(b)(1)
does not allow the substitution of NOX
for VOC. However, the RFP
requirements in section 172(c)(2) and
182(c)(2)(B) are not constrained by that
limitation and either VOC or NOX
emissions reductions may be counted
toward meeting RFP under those two
provisions.
Comment: Some commenters believed
an additional 15 percent VOC reduction
should not be necessary for 8-hour areas
that encompass in whole or in part a 1hour nonattainment area with an
approved 15 percent plan. Such areas
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should simply be required to achieve
whatever NOX or VOC emissions
reductions are needed for attainment.
One commenter noted that the
proposed § 51.910(a)(ii) did not address
all boundary change scenarios
consistent with our proposed approach
found in section VI.I.9. of the June 2,
2003 proposed rule (68 FR 32835).
Response: We agree with the
commenter that an area with an
approved 15 percent plan for the 1-hour
standard is not required to adopt a
second 15 percent plan under section
182(b)(1) for purposes of the 8-hour
standard. However, if a portion of the 8hour area was not subject to an
approved 15 percent plan for the 1-hour
standard, section 182(b)(1) applies to
that portion of the 8-hour area and may
be met by one of two approaches
described above and in the regulatory
text. We agree with the second
commenter who noted that the proposed
rule did not explicitly address all
possible boundary scenarios; we believe
we have fully addressed these different
boundary scenarios in the final rule in
a manner consistent with the proposal.
Comment: A commenter indicated
that they preferred to work with EPA in
the development of an alternative that
will eliminate or minimize the planning
burdens associated with development of
a 15 percent RFP plan for one town. One
alternative might be the development of
a ‘‘comparability demonstration,’’
showing that the town had implemented
the same controls that had been
previously responsible for achieving a
15 percent reduction in VOCs in the lhour ozone nonattainment area
associated with the 8-hour
nonattainment area including this town.
Response: We are willing to work
with individual areas as they develop
their 8-hour 15 percent plans and to
help them avoid unnecessary planning
burdens. We believe that the portion of
an 8-hour area not subject to an
approved 1-hour 15 percent plan may be
able to meet the 15 percent obligation
for the 8-hour standard if the area
adopts the same VOC control measures
(for example, VOC RACT at the same
source thresholds, I/M, etc. * * *) as in
the portion of the 8-hour nonattainment
area subject to a 15 percent plan for the
1-hour standard and if the area has the
same mix of emissions sources as in the
area subject to the 15 percent plan for
the 1-hour standard. We anticipate we
could propose approval of a SIP on this
basis where supported by the record.
Comments on Draft Regulatory Text
Comment: Another commenter
generally supported the RFP provisions
but suggested that in section
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51.910(a)(1)(ii)(A) of the draft regulatory
text, we insert the language shown in
bold:
‘‘An area classified as moderate or
higher that has the same boundaries as
an area for which EPA fully approved a
15 percent plan for the 1-hour NAAQS
is not subject to section 182(b)(1) of the
CAA for the 8-hour NAAQS, but
instead—(A) If classified as moderate, is
subject to RFP under section 172(c)(2) of
the CAA and shall meet that obligation
by submitting 3 years after the effective
date of its designation a SIP revision
that provides for implementation of all
emission reductions of VOCs and/or
NOX needed for attainment by the
beginning of the ozone season in the
area’s attainment year.’’ The commenter
claimed this language is consistent with
the approach EPA has taken in other
provisions of this draft.
Response: The commenter’s concern
is noted. Section 51.910 has been
restructured for reasons noted elsewhere
in this preamble and it addresses the
commenter’s concern.
Comment: One commenter suggested
that § 51.910(a)(3) of the draft regulatory
text be revised to allow (even if
conditional) NOX reductions to be
substituted for VOC reductions (for any
ROP or RFP requirement) whenever
such reductions would ‘‘result in a
reduction in ozone concentrations at
least equivalent to that which would
result from the amount of VOC emission
reductions required.’’
Response: As noted above we do not
believe the CAA allows substitution of
NOX for VOC to meet the 15 percent
requirement of section 182(b)(1).
Comment: One commenter stated that
draft § 51.910(a)(1)(ii) eliminates the 15
percent requirement for areas that have
already achieved this requirement under
the 8-hour standard and supported that
change. However, they further state that
the strict criteria of ‘‘same boundaries’’
should be revisited because there may
be limited changes in the nonattainment
areas ‘‘boundaries’’ when areas are
designated for the 8-hour standard.
Such changes should not negate this
provision. A broader definition needs to
apply to this section to allow for
changes to boundaries in nonattainment
areas between 1-hour and 8-hour
designations where such changes do not
substantially alter the geographical or
population characteristics for the area.
Another commenter supports an
exemption for 8-hour nonattainment
areas that have met the 15 percent ROP
requirement for the 1-hour NAAQS. The
commenter requests that EPA clarify the
criteria that the area must have the same
geographic boundaries to qualify for the
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exemption. This means that in the
geographic areas for which a State has
an approved 15 percent plan, the 15
percent requirement will not apply, and
the 15 percent requirement is only
intended to apply to the new geographic
areas of the 8-hour nonattainment area,
and that the 15 percent reduction of
emissions from the new areas could
come from the entire nonattainment
area to satisfy this requirement.
Response: As we explain in our
summary of the final rule, we have
recognized that there are a variety of
boundary scenarios for 8-hour
nonattainment areas in relation to the
boundaries of areas for the 1-hour
standard. We have modified the draft
regulatory text such that the final rule
speaks in terms of 8-hour areas that
include all or part of an area with an
approved 15 percent plan for the 1-hour
standard. For those portions of the 8hour area with an approved 1-hour 15
percent plan, the 8-hour area is not
required to develop a second 15 percent
plan under section 182(b)(1) for
purposes of the 8-hour standard, but
instead will be subject to section
172(c)(2) if it is an 8-hour moderate area
or subject to section 182(c)(2)(B) if it is
classified as serious or above for the 8hour standard. If the 8-hour area
includes both areas that were subject to
an approved 15 percent plan for the 1hour standard and areas that were not,
then the 8-hour area can choose whether
to develop a section 182(b)(1) 15 percent
plan for the entire 8-hour area or to
develop a 182(b)(1) plan only for the
area not previously subject to such a
plan and to treat the remaining portions
of the area under section 172(c)(2) or
182(c)(2)(B), as described above.
As noted, EPA does not believe the
statute allows it to relieve any area that
has not already met the 15 percent
requirement for the 1-hour standard
from the obligation to meet that
requirement except as provided in
section 182(b)(1)(A)(ii).
3. What baseline year should be
required for the emissions inventory for
the RFP requirement?
[Section VI.I.4. of June 2, 2003
proposed rule (68 FR 32833); § 51.909 of
the draft regulatory text; § 51.910(d) of
the final regulatory text.]
a. Background
The baseline inventory for RFP (under
subpart 2) is used as the starting point
for the determination of a target level of
emissions for the future year RFP and as
the baseline from which creditable
reductions are determined. We
designated ozone nonattainment areas
in April 2004. Under the ‘‘Consolidated
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Emissions Reporting Rule’’ (67 FR
39602; June 10, 2002) revised emissions
inventories are required for the years
2002 and 2005; therefore, we proposed
to require use of the 2002 inventory as
the baseline inventory for the RFP
requirement. This would be the most
recent inventory available at the time of
designation. We issued a memorandum
identifying 2002 as the anticipated
emissions inventory base year for the
SIP planning process to address the 8hour ozone and the PM2.5 standards.39
b. Summary of Final Rule
As set forth in our proposed rule, for
areas designated nonattainment for the
8-hour ozone NAAQS with an effective
date of June 15, 2004, we are requiring
States to use the 2002 inventory as the
baseline inventory for the RFP
requirement. As noted in the proposal,
the inventory for the 2002 calendar year
would be the most recently available
inventory at the time of designation in
2004. However, in response to several
comments, we are allowing States the
option of justifying the use of an
alternative baseline inventory year for
RFP. To justify an alternative, the State
would have to demonstrate how the
alternative year meets the CAA’s
provisions for RFP and provide a
rationale for why it is appropriate to use
the alternative baseline year rather than
2002 to comply with the CAA’s RFP
provisions. We believe that for multiState nonattainment areas, several States
must agree on a single baseline. Even if
a State chooses an alternative baseline
inventory year for RFP, 2002 remains
the valid baseline year for transportation
conformity purposes as described in 40
CFR 93.119. The baseline year test is
used only in conformity determinations
prior to the submission of a SIP that
establishes motor vehicle emissions
budgets (e.g., an RFP SIP). Therefore,
areas using the baseline year test would
continue to use 2002 as the baseline
year for conformity purposes because an
area’s baseline year would not be
changed until an RFP SIP is submitted.
Once an RFP SIP is submitted and the
motor vehicle emissions budgets in that
SIP are found adequate or are approved
the area would no longer use the
baseline year test. Instead the area
would use the adequate or approved
budgets in the RFP SIP in conformity
determinations.
39 Memorandum of November 18, 2002, from
Lydia Wegman and Peter Tsirigotis, ‘‘2002 Base
Year Emission Inventory SIP Planning: 8-hr Ozone,
PM2.5 and Regional Haze Programs.’’ This document
is available at the following Web site: https://
www.epa.gov/ttn/oarpg/
meta.442.1.2002baseinv.pdf.
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71637
The baseline emissions inventory is
calculated as of the effective date of an
area’s nonattainment designation using
the most recent calendar year for which
a complete inventory is required to be
submitted to EPA under subpart A of 40
CFR part 51, subpart A. Under 40 CFR
part 51, subpart A, States are required
to submit a comprehensive inventory on
3-year cycles within 17 months after the
close of the reporting period. Thus, the
2002 inventory was due 17 months after
the December 31, 2002 close of the
reporting period, i.e., was due by June
1, 2004. For those areas designated
nonattainment for the 8-hour ozone
NAAQS effective June 15, 2004 (69 FR
23858; April 30, 2004), the baseline
emissions inventory should be based on
the calendar year 2002 because the 2002
inventory was due under 40 CFR part
51, subpart A, prior to the time of
designation. For areas with an effective
nonattainment designation in the future,
the baseline inventory will be for the
calendar year of the most recent
triennial inventory as of the date of
designation.40 As provided above, the
State may use an alternative baseline
only if it is demonstrated that it is
consistent with the CAA and the State
demonstrates why it is appropriate.
c. Comments and Responses
Comment: Some commenters agreed
there is a reasonable basis to select 2002
as the date of emissions inventories for
the purpose of establishing creditable
reductions from the inventory. States
are not required by the CAA to adopt
the year of the nonattainment
designation for the 8-hour standard as
the basis for their planning, even though
that was the case under the 1990 CAA
Amendments. The commenter claims
there are a variety of measures that
would be implemented after 2002 that
local jurisdictions would like to be able
to account for as new emissions
reductions in their modeling
demonstrations. The commenter thus
believes that reductions between these
years ‘‘should count.’’ In addition, this
was the most recent quality assured/
quality controlled inventory used to
support the States’ recommendations for
proposed nonattainment designations
on July 15, 2003.
Several commenters recommended
that the baseline year (starting the 6-year
period for RFP) be set for the year in
which designations were made (i.e.,
2004).
40 For example, where the effective date of
designation to nonattainment for an area for the 8hour ozone NAAQS is after June 1, 2007 but before
June 1, 2010, the baseline inventory will be for
calendar year 2005.
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Response: The EPA has decided to
establish 2002 as the baseline year for
RFP SIPs in conformity with both the
language of the CAA and the inventory
year cycle. Of reasonable importance is
the need to maintain consistency with
the periodic inventory for use in various
milestone considerations such as RFP,
milestone compliance demonstration,
attainment, and contingency plans. In
addition, while there would be a
difference in the RFP requirement based
on the choice of the RFP baseline, there
should be little if any difference in
terms of emissions reductions needed to
demonstrate timely attainment. If we
use 2002, the baseline may be higher but
areas can take credit for any 2002–2004
emissions reductions from federally
enforceable control measures. If we use
2004, the baseline may be lower but
areas can’t take credit for measures that
produce emissions reductions between
2002–2004. Depending on the area, the
difference should be minimal in terms
of the difference in the amount of
reductions needed to reach attainment
and what new measures are necessary to
get there. We believe it is reasonable to
select an inventory year for which States
were already required to produce an
inventory rather than requiring States to
produce an additional inventory (e.g.,
for 2004) that is not otherwise required.
Moreover, requiring the use of an
inventory for the designation year
would cause delay, as it would take the
States 1–2 years after the end of 2004 to
produce the inventory which would be
the basis for selecting controls to
achieve the necessary reductions for
RFP and for modeling attainment.
However, we are allowing States the
option of justifying the use of an
alternative baseline emission inventory,
provided it meets the requirement of the
CAA’s RFP provisions. As noted above,
the use of an alternative year for the
baseline inventory for RFP does not
change the requirement to use 2002 as
the baseline year for transportation
conformity as described in 40 CFR
93.119.
Comment: Another commenter
referred to EPA’s proposal language
regarding the RFP SIP that would have
required submission of the RFP plan
within 2 years after designation. They
stated that EPA is missing the point in
that the attainment and RFP submission
dates established in subpart 2 are to
allow States a sufficient amount of time
to achieve the mandated goals.
That commenter referred to another
alternative that would amend the
proposal to require a 1990, rather than
2002 baseline for those areas not having
a previously-approved 15 percent RFP
plan. They further commented that
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although a 1990 baseline would not
eliminate the planning burden
associated with this requirement, it
would go far towards minimizing the
necessary additional work.
Response: We disagree with the
commenters who urged use of the 1990
inventories as the baseline for planning
for the 8-hour NAAQS. Use of the 1990
baseline would be unreasonable now
since it would have to be substantially
recalculated due to changes in emission
calculating methodologies. Furthermore,
a 1990 inventory was only required for
nonattainment areas as of enactment of
the 1990 CAA Amendments and
therefore may not exist for a number of
areas that are currently designated
nonattainment for the 8-hour standard.
Finally, we believe that reliance on
emissions reductions that may have
occurred well before 8-hour
designations and classifications should
not be counted as making progress
toward attainment.
Comment: Another commenter noted
that the 18 percent reduction for serious
areas would have to be achieved by
2008. This is 6 years after the base year.
The commenter noted that the 2 years
that would remain after SIP submission
(from the proposed SIP due date of 2006
until 2008) would be totally inadequate
to achieve either the 15 percent
reduction in VOCs or the 18 percent
reduction in VOCs and/or NOX. The
commenter noted the CAA provides for
submission of RFP plans within 3 years
(from 1990) in section 182(b)(1)(A) and
4 years in section 182(c)(2).
Response: The final rule reflects a
change from the proposal to allow
submission of the RFP plan up to 3
years from the date of designation. We
do not believe the RFP provisions of
subpart 2 of the Act provides relief from
the requirement to obtain the specified
percent reductions from the RFP
baseline within the time constraints
specified in those provisions.
Comment: A comment on draft
regulatory text § 51.909 noted that EPA
specified various program milestone
dates, which were derived from the
relationship of these dates to the
expected date of initial designation. The
commenter recommends deleting all
such specific date references from the
regulation, to avoid the need for revising
regulations if the initial designations are
not concluded as expected. This should
be replaced by a generic approach, for
example by requiring the most recent
year’s data to be used as the baseline in
the second sentence of § 51.909.
Deleting the calendar-specific dates
would not change the result if the
designations occur as planned, yet
would allow for more recent data to be
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used if factors beyond the agency’s
control create a delay in designations.
This approach also will allow the
regulation to apply to future area
designation changes, such as areas that
are redesignated nonattainment at some
point in the future. Such specific dates
are more appropriately included as
examples in agency guidance or within
the preamble of a final rule with a
discussion of how they are derived. The
regulation itself should retain only the
generic relationship between the
milestone and the effective date of
designation, which is the approach
taken elsewhere in the rule.
Response: Because the designations
have already taken effect at this point,
we believe it is appropriate to specify
2002 as the presumptive baseline year.
The final version of the rule (now
§ 51.910(d)) provides general language
regarding the appropriate baseline year
for areas that have an effective date of
a nonattainment designation in the
future.41
4. Should moderate and higher
classified areas be subject to prescribed
additional RFP requirements prior to
their attainment date?
[Section VI.I.5 of June 2, 2003
proposed rule (68 FR 32834); no draft
regulatory text; section 51.910(a)(1)(i) of
final regulatory text.]
a. Background
As noted in the proposal, for areas
initially classified moderate and higher
for the 1-hour ozone standard, the
baseline inventory was defined as 1990
in the CAA Amendments. Therefore, the
6-year period for the initial 15 percent
RFP requirement ended in the same year
as the attainment date for moderate
areas, viz., 1996. For areas classified
moderate and higher under the 8-hour
ozone standard, however, we proposed
that the 15 percent RFP target level of
emissions would be calculated for the 6year period after the 2002 baseline year,
i.e., 2003–2008. Moderate areas would
be required to meet an attainment date
no later than 6 years after the area is
designated nonattainment for the 8-hour
standard. Since the effective date of
designation of nonattainment areas is
June 15, 2004, the outside statutory
attainment date would be June 15, 2010.
This leaves approximately a 11⁄2 year
gap between the end of the 6-year
period for the 15 percent RFP
requirement (i.e., December 31, 2008)
and the maximum statutory attainment
41 We note that even though the draft regulatory
text was structured to place the specification of the
baseline year for RFP (as well as for attainment
demonstrations) in § 51.909, the final rule places
the RFP baseline year requirement in § 51.910.
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date. If we were to also require moderate
areas to obtain an additional three
percent per year emission reduction
beyond 2008 for the 11⁄2 additional years
out to 2010, the RFP requirement could
be more than what we believe Congress
intended for moderate areas under
subpart 2. Additional three percent per
year reductions were only required for
serious and higher classified ozone
nonattainment areas. We proposed that
the only specific RFP requirement
applicable for moderate areas is the 15
percent VOC requirement between the
end of 2002 and the end of 2008.
However, section 172(c)(2), which
requires areas to meet RFP generally,
would apply for any period for which
RFP is not addressed in subpart 2. For
purposes of section 172(c)(2), RFP
means annual incremental reductions as
may be required by the Administrator
for purposes of ensuring attainment
[CAA Section 171(1)]. Therefore, we
proposed a moderate area would need to
provide any additional emissions
reductions—VOC and/or NOX—needed
to provide for attainment by the area’s
attainment date. In proposing this
approach for this circumstance, we
interpreted the subpart 1 RFP
requirement to mean that the area must
achieve whatever further reduction is
needed for attainment in the remaining
period prior to the attainment date
(2009 through June 15, 2010).
We proposed that serious and higher
classified areas would need to provide
in their SIPs an additional average of
three percent per year emission
reduction over each subsequent 3-year
period beyond the initial 6-year period
through the attainment year, consistent
with what Congress specified in section
182(c)(2)(B) of the CAA.
b. Summary of Final Rule
In the final rule, we are taking the
approach we proposed. We are not
prescribing additional increments of
reductions for the 11⁄2 years before the
maximum attainment date for moderate
areas. Such areas must provide for any
additional emissions reductions (VOC/
NOX) needed to provide for attainment
by the beginning of the ozone season
prior to the area’s attainment date.42
Serious and higher classified areas
would need to provide in their SIPs an
additional average of three percent per
year emission reduction over each
subsequent 3-year period beyond the
42 We note that areas must implement controls
prior to the beginning of the last full ozone season
preceding the attainment date. For moderate areas
designated as of June 15, 2004, such reductions
would be needed by the beginning of the 2009
ozone season.
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initial 6-year period through the
attainment year.
c. Comments and Responses
Comment: One commenter suggested
that following the statutory timetable
rather than the one proposed by EPA
would eliminate the problem of how to
handle the ‘‘11⁄2 year gap between the
end of the 6-year period for the 15
percent RFP requirement (i.e., December
31, 2008, as proposed by EPA) and the
attainment date.’’ The commenter
continued by saying that no such gap is
contemplated by subpart 2, which
provides in section 18l(b)(l) that
moderate area’s attainment dates and
their 15-percent VOC RFP date are to be
the same: 6 years after their designation
and classification.
Response: As provided in an earlier
response, we do not believe the CAA
requires the end of the 15 percent RFP
period and the attainment date to be the
same.
Comment: Another commenter noted
the proposal states that the only specific
RFP requirement applicable for
moderate areas is the 15 percent VOC
requirement between the end of 2002
and the end of 2008. However, section
172(c)(2) also applies, requiring areas to
meet RFP generally. Therefore, a
moderate area would still also have to
provide any additional emissions
reductions—VOC and/or NOX, i.e.,
whatever is needed to provide for
attainment by the beginning of the
ozone season prior to the area’s
attainment date. The commenter agrees
that any additional emissions
reductions needed to achieve attainment
are the only reductions that should be
required of moderate areas.
Response: We agree with the
commenter, and our rule requires that
for purposes of meeting RFP beyond
2008 until the area’s attainment date,
moderate areas must reduce VOC and
NOX emissions as necessary to attain by
the area’s attainment date.
5. What is the timing of the submission
of the RFP plan?
[Section VI.I.6 of June 2, 2003
proposed rule (68 FR 32834); § 51.910 of
the draft and final regulatory text
(several locations).]
a. Background
As noted in the proposal, section
182(b)(1) requires that moderate and
higher classified areas submit their 15
percent RFP plans within 3 years after
1990. Obviously, applying the statute as
written is absurd, since we are well past
that date. The CAA uses identical
language for identifying area’s
attainment dates under subpart 2. In our
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71639
Phase 1 Rule, for purposes of attainment
dates for the 8-hour NAAQS, we
interpreted the CAA’s language referring
to the date of enactment of the 1990
CAA Amendments to mean the date of
designations for the 8-hour standard.
We noted in the proposal that if we
applied the same interpretation for RFP
plans, i.e., that they should be
submitted within 3 years after the area’s
nonattainment designation date (i.e., in
2007 if the area has an effective
designation in 2004), the plans would
have to be implemented within 1 year
after submission to ensure the 15
percent emissions reductions are
achieved by the end of the relevant 6year period (i.e., December 2008). We
indicated concern that this might not
provide sources with sufficient time to
achieve the reductions by the required
deadline. Therefore, we proposed that
the RFP SIP be submitted within 2 years
after nonattainment designation—
namely by 2006 for areas designated in
2004. This would provide for 2 years for
the State to develop and submit its RFP
plan, and another 2 years for the control
measures to be implemented.
We also proposed that an area
classified serious or above submit
within 2 years after designation its RFP
plan that provides for 18 percent
emissions reductions (VOC and/or NOX)
over the first 6 years from the baseline
year and then submit within 3 years
after designation a RFP plan that
provides nine percent emissions
reductions (VOC and/or NOX) over each
of the next 3-year periods until the
area’s attainment date.
b. Summary of Final Rule
In the final rule, we are taking a
different approach than proposed in
light of concerns raised by States in
public comments. These commenters
stated that they would need more than
2 years for development, adoption and
submission of RFP plans for the
increment of progress over the first 6
years after the baseline year. The EPA
agrees with the several commenters who
urged that 3 years was more consistent
with the CAA. Additionally, 3 years is
a more reasonable time period for
submission because it allows States the
necessary time to move regulatory
actions through their legislative
processes and allows States to consider
RFP in conjunction with their
attainment demonstrations. Therefore,
for moderate and higher classified areas,
the first RFP SIP must be submitted
within 3 years after the area’s
nonattainment designation. For areas
with a June 15, 2004 effective date for
the 8-hour designations, the SIP would
be due by June 15, 2007. This would
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provide up to 3 years for States to
develop and submit RFP plans, and 1
additional year (until the end of 2008)
for control measures to be implemented.
The RFP SIP for any remaining 3-year
periods out to the attainment date
beyond the first 6 years also would be
submitted with the attainment
demonstration, i.e., within 3 years after
designation. However, since States
maintain the flexibility to submit plans
early to provide more time for
implementation of their SIP control
measures, we recommend that States
complete their RFP plans as soon as
possible after designation to provide as
much time as possible for sources to
implement the emissions reductions.
Furthermore, States may also begin
implementing their control measures
before submission to EPA as part of
their SIPs, which would provide
additional time sources may need to
comply.
c. Comments and Responses
Comment: Several commenters
opposed EPA’s proposal to shorten to 2
years the statutory 3-year period for
development and submittal of 15percent VOC RFP plans. They claim this
proposal violates the guarantee of 3
years for plan development to the State
in section 182(b)(l)(A) and is contrary to
EPA’s basic proposed principle that
[quoting from the proposal] ‘‘subpart 2
SIP submittals will be due as a general
matter by the same period of time after
designation and classification under the
8-hour standard as provided in subpart
2 for areas designated and classified at
the time of enactment of the 1990
CAA.’’ The commenters contended that
subpart 2 gives EPA no authority to
shorten the statutory 3-year period. In
contrast, Congress in subpart 1
authorized EPA to set a schedule for
nonattainment SIP submissions.
Congress, therefore, knew how to give
EPA discretion to shorten SIP
submission deadlines according to the
commenters; it did not do so in subpart
2.
Concerning the timing of submission
of the RFP plan, another commenter was
concerned that the States may not have
sufficient photochemical modeling and
ambient air analyses to indicate the best
mix of RFP SIP controls. Additionally,
in areas dominated by mobile source
emissions, it may not be feasible to
implement control measures to achieve
the RFP target within the 2 years after
the proposed required RFP SIP
submission date as EPA has suggested.
The commenter suggested that EPA
develop policy options that allow areas
in such predicaments to maintain
approved SIPs if emissions reductions
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are not available to meet RFP
requirements and/or if available
emission reduction techniques might be
counterproductive to other local and
regional air quality goals.
Another commenter stated revisions
to State emission reduction measures
cannot be adopted easily in a 2-year
time period because they require
administrative action and frequently
State legislation to approve. This period
can lengthen when proposed measures
like enhanced vehicle I/M involve
controversial actions affecting the
public. Logistically, a State must
establish a regulation by administrative
action with public input before (though
sometimes after) such a measure is
approved by the state’s legislature. A
number of jurisdictions’ legislatures are
only in regular session to consider such
measures several months or, in alternate
years. Thus, it is unreasonable for States
to have only 2 years from their
nonattainment designations to adopt
new measures.
Another commenter referenced the
case NRDC v. EPA, 22 F. 3d 1125, 1135
(D.C. Cir., 1994), where the Court
considered the propriety of EPA’s
extension of the deadlines by which
States had to submit elements of their
SIPs. The Court upheld EPA’s decision
to extend the deadline for submission of
a SIP given EPA’s failure to meet its
own deadline for providing certain
necessary guidance to the States. The
Court allowed EPA to use the
extraordinary remedy of a deadline
extension in this instance because
Congress would have intended that the
deadline be extended to provide a party
the full statutory time for acting on the
agency guidance. The commenter
referenced CAA section 126(c) where
EPA may set a compliance deadline ‘‘as
expeditiously as possible, but in no case
later than 3 years after the date of such
finding.’’
One commenter noted that CAA
section 182(b)(1)(A) as modified by
section 181(b)(1) requires for moderate
areas that the RFP SIP be submitted 3
years after designation. The commenter
disagreed with the RFP plan
requirement to submit the plan 2 years
after the effective date of the
nonattainment designation as not being
consistent with or supported by these
CAA sections. The resources involved
in developing, proposing and adopting
any SIP revision are not insignificant. In
order to ensure the most efficient use of
resources, the commenter contended
that EPA should not require this SIP
revision sooner than the submission of
the attainment demonstration, 3 years
after the effective date of the
designations. Allowing States 3 years to
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submit the RFP plan is consistent with
existing CAA requirements.
Response: After consideration of the
comments, we have changed the final
rule to be consistent with the approach
advocated by a number of commenters.
In consideration of the 2004 designation
and the need to achieve the 2008 RFP
reductions by December 2008, it seems
reasonable to EPA that States first be
given sufficient time after designation to
formulate RFP plans. Therefore, the
final rule allows States up to 3 years
after designation to submit their RFP
SIPs. However, to the extent States are
relying on newly developed rules to
meet all or part of the RFP requirement,
we recommend that States adopt those
rules as soon as possible after
designation to provide as much time as
possible for sources to achieve the
emissions reductions.
6. How should CAA restrictions on
creditable measures be interpreted?
Which national measures should count
as generating emissions reductions
credit toward RFP requirements?
[Section VI.I.7 of June 2, 2003
proposed rule (68 FR 32834);
§ 51.910(a)(4) of the draft regulatory
text; § 51.910(a)(3) of the final regulatory
text.]
a. Background
Section 182(b)(1) contains provisions
that limit creditability toward meeting
RFP for certain limited emission
reduction measures required prior to the
enactment of the CAA Amendments of
1990. We noted in the proposal that we
believe these specific restrictions should
continue to apply for purposes of the 8hour NAAQS. The proposal noted that
Congress intended to prevent areas from
taking credit for RFP only for those
specific measures that were already
adopted and in place (or required to be
in place) prior to the date of enactment
of the CAA Amendments of 1990
(November 15, 1990). We said that this
same holds true for the RFP requirement
as it applies to the 8-hour ozone
standard, namely preventing credit
toward the mandatory RFP percent
reductions for continuing reductions
from those specific measures cited in
the CAA that were already adopted and
in place (or required to be adopted and
in place) prior to the date of enactment
of the CAA Amendments of 1990. There
is no indication in the CAA that this
exclusion should be changed. Congress
mandated many emissions reductions in
the 1990 CAA Amendments with no
indication that they should not be
credited to meeting RFP or attainment of
any existing or revised NAAQS.
Therefore, we proposed that all
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emissions reductions that occur from all
Federal and any other measures not
otherwise identified in section
182(b)(1)(C) and (D) and that occur after
the baseline emissions inventory year
would be creditable for the RFP
requirement. A number of examples
demonstrating emissions reductions that
would be creditable toward the RFP
requirement were set forth in our
proposal.
b. Summary of Final Rule
We are taking the approach we
proposed, under which all emissions
reductions that occur after the baseline
emissions inventory year are creditable
for purposes of the RFP requirements in
this section except as specifically
provided in section 182(b)(1)(C) and (D)
and section 182(c)(2)(B) of the CAA. The
restriction imposed by section
182(b)(1)(D) limits crediting reductions
from the following four categories:
• Corrections to or additions of RACT
rules as required by CAA section
182(a)(2)(A).
• Corrections to I/M programs for
areas where the SIP included or was
required to include a schedule for I/M
implementation under the CAA in effect
immediately before November 15, 1990.
• Regulations concerning Reid Vapor
Pressure (RVP) promulgated by EPA
before November 15, 1990 or required to
be promulgated under CAA section
211(h).
• Motor vehicle exhaust or
evaporative emissions measures
promulgated by EPA by January 1, 1990.
c. Comments and Responses
Comment: One commenter supported
EPA’s proposal to allow credit towards
RFP requirements of all emissions
reductions, which occur after the
baseline emissions inventory year
(2002) from all Federal, and any other
measures not otherwise identified under
section 182(b)(1)(D). This would include
reductions from cleaner fuels and
engines, reductions from ongoing 1-hour
SIP controls and VOC reductions from
implementation of MACT standards
after the baseline year. The commenter
stated that this proposed approach
would be critical in a number of areas
that already have stringent stationary
source controls and/or in areas
dominated by mobile source emissions.
Response: The EPA acknowledges this
comment of support for our final action.
Comment: Another commenter
believed that early voluntary emissions
reductions prior to 2003, and not
required under the CAA, should also be
creditable toward RFP requirements.
The commenter recommended that
EPA’s final rule clarify that States be
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allowed credit for RFP for early
voluntary emissions reductions
occurring prior to 2003. As a company
that has proactively taken measures to
reduce NOX emissions through
innovative Combustion Initiative (an
enhanced efficiency technology), the
commenter believed that EPA’s
regulations should take these efforts into
account as they have resulted in real
improvements to air quality. Another
commenter stated that companies who
made voluntary reductions prior to 2003
would be penalized for having
undertaken such voluntary measures
and, thus disallowing credit for these
reductions provides disincentives for
voluntary reductions.
Response: Voluntary reductions that
occur prior to January 1, 2003 will be
reflected in the area’s baseline
inventory. This lower baseline means
that fewer reductions will be needed to
achieve RFP.43 Allowing an area to take
credit for reducing emissions that are
not included in the inventory would
result in ‘‘double counting’’ of those
emissions reductions.
Comment: One commenter suggested
that areas should be able to take credit
for MACT standards that may reduce
VOC for which compliance is required
after the 2002 baseline year. The
commenter said it would be helpful to
States if EPA produced a document
detailing the expected VOC reductions
after implementation of MACT
standards. States could claim these
reductions toward any reductions
required to meet their target. The
commenter suggested that the most
useful way to express the reduction
would be as a percent of the 2002
emissions.
Response: The EPA agrees that areas
can take credit in RFP plans for post2002 VOC reductions from MACT
standards. We are considering whether
to develop the recommended guidance.
Comment: One commenter objected to
EPA’s proposal to allow States to claim
RFP credit from any reductions
achieved through post-1990 adoption of
the types of measures listed in section
182(b)(1)(D). The commenter further
stated that section 182(b)(1)(D) prohibits
granting RFP credit for any measures
contained on the list. Congress wanted
the RFP reductions to be new reductions
rather than emission cuts that would
43 For example, if an area had VOC emissions in
2001 of 100 tons per day, and a source reduces
emissions by 10 tons per day in 2002, the baseline
emissions will be 90 tons per day. Thus, the area
will need to achieve 13.5 tons per day reduction to
meet its 15 percent requirement, rather than 15 tons
per day. However, the area cannot take credit in the
15 percent plan for the 10 tons per day of emissions
that are not part of the baseline inventory.
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71641
have occurred anyway. In the case of 8hour nonattainment areas, the baseline
year will be 2002. Therefore, according
to the commenter, to be consistent with
subpart 2, EPA must disallow RFP
credit for measures listed in section
182(b)(1)(D) adopted any time prior to
2002.
Another commenter urged EPA to
consider a hybrid approach that gives
States credit for approved RFP plans
that go beyond 2002, provided that the
Plan is evaluated on a 2002 baseline.
This approach would give States credit
for ongoing emissions reductions,
recognize the need to address the 8-hour
standard as the ozone standard (rather
than rely on plans developed to meet
the 1-hour standard), and potentially
avoid some unneeded controls.
Another commenter recommended
that EPA not allow emissions reductions
credit for all emissions reductions
occurring after the baseline year.
Emissions reductions to satisfy the RFP
requirements of CAA section 182(b)(1)
and 182(c)(2)(B) are required to be
achieved by submitting ‘‘a revision to
the applicable implementation plan to
provide for * * * emissions
reductions.’’ The commenter argued that
emissions reductions already required
by, or accounted for in, the applicable
implementation plan may not be
credited toward the new RFP
requirements. For example, reductions
that were required to be achieved by SIP
or other requirements, but which were
not achieved in practice prior to the
baseline year, should not be credited
toward meeting the new RFP reductions
required after the baseline year. Only
new measures submitted with the new
SIP revision may be credited for this
purpose.
Response: The EPA believes that, with
certain exceptions (see CAA section
182(b)(1)(C) and (D)), any reductions
that occur after 2002 are creditable
towards RFP and attainment and that it
should not matter when the State
initially adopted or EPA promulgated
the measures that produce those
reductions. The CAA does not mandate
the approaches advocated in the
comments. While the comments cite
phrases in the CAA that might be read
to support the approach advocated in
the comments, EPA believes such an
interpretation is at odds with other
provisions of the CAA. In addition to
the restriction imposed by section
182(b)(1)(D) on crediting certain
measures, section 182(b)(1)(C) places
only two restrictions on creditability of
reductions towards RFP: first,
reductions are creditable if they result
from measures in the applicable
implementation plan, i.e., the approved
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SIP or from rules promulgated by EPA,
or from the applicable requirements 44
that are incorporated into a title V
permit; and secondly, only those
reductions that have actually occurred
after the baseline year and before the
milestone date may be credited towards
a RFP milestone. The requirement that
the reductions result from measures in
the applicable implementation plan or
EPA regulations, or applicable
requirements contained in a title V
operating permit imposes no restriction
that such measures must be enacted
after the date of designation or after the
baseline year. This restriction only
requires that the measure approved into
the SIP be a rule promulgated by EPA
or be an applicable requirement
included in a title V permit issued
before or concurrently with approval of
the RFP SIP revisions, and that the
reductions occur after the baseline year
and before the milestone date.
While this provision limits EPA’s
discretion to allow credit towards the
RFP requirement from any reduction
that does not fit into any of the three
aforementioned classes of measures,
EPA does not see anything in the statute
that mandates the adoption of the
approach advocated in the comments. In
fact, EPA believes the opposite is the
case.
The same argument (i.e., that
creditable RFP measures must be
measures adopted/promulgated after
designation or after the baseline year)
could have been made for the various
programs mandated by the 1990 CAA
Amendments. These mandated
measures included RACT requirements
under section 182(b)(2), Stage II vapor
recovery under section 182(b)(3), motor
vehicle I/M under sections 182(b)(4) and
182(c)(3), RFG under section 211(k), and
the Tier 1 motor vehicle standards
under title II. The EPA believes the
statute is plain that Congress envisioned
that all of these would be adopted after
1990 and in most cases implemented
before 1996 because the statute contains
enforceable deadlines for submission of
the requisite SIP revisions or
promulgation of the EPA rules. In many
cases, they contain required
implementation dates before 1996.
Congress clearly did not limit credit for
RFP for any of these measures. In our
proposed rulemaking, EPA specifically
proposed allowing use of reductions
resulting from any measure as long as
the reductions meet the creditability
criteria of section 182(b)(1)(C) for the
44 Applicable requirements are federallyenforceable requirements under the CAA that are
created elsewhere but incorporated into a title V
permit. See the definition of ‘‘Applicable
requirement’’ in 40 CFR 70.2 and 71.2.
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very reason EPA concluded Congress
did not intend to impose the sort of
limit on creditability advocated in the
comments for the 1-hour standard and
for any revised standard.
In summary, the statute says that only
four specific categories of emissions
reductions are restricted. It does not
refer to or include any post-1990 rules’
emissions reductions as restricted and
only speaks to creditability in terms of
when the reductions occurred, not when
the rules or measures were adopted. As
explained in the proposal and the
preceding paragraphs, Congress had
reason to limit creditability of pre-1990
rules, mandated many post-90 rules and
allowed these rules to be credited
towards post-90 RFP, and nothing in the
statute leads us to believe that Congress
would not have wanted them to also be
creditable to post-2002 RFP. The EPA
believes it is appropriate to allow credit
toward RFP for emissions reductions
other than reductions from the four
categories specified in the CAA
pursuant to section 182(b)(1)(D).
Language that was once pertinent to the
schedule of the 1990 CAA Amendments
should be reinterpreted now to mean
emissions reductions are creditable
toward emissions reductions
requirements to the extent they actually
occur during the relevant ROP period
and after the baseline year.
7. For areas covered only by subpart 1,
how should the RFP requirement be
structured?
[Section VI.I.8. of June 2, 2003
proposed rule (68 FR 32834); § 51.910(b)
of the draft and final regulatory text.]
a. Background
The proposal noted that the RFP
requirement under subpart 1 is more
general than that under subpart 2, and
EPA thus has more flexibility in
determining what RFP means under
subpart 1. For instance, the State may
rely on emissions reductions of VOC or
NOX, or a combination of both to meet
its RFP requirement whereas subpart 2
limits the initial 15 percent to VOC
emissions reductions. However, we
acknowledged the concern about
treating in a similar manner areas under
subpart 1 that have an ozone problem
similar to areas covered under subpart
2.
We proposed scenarios for three types
of subpart 1 areas: (a) Areas with
attainment dates 3 years or less after
designation, (b) Areas with attainment
dates between 3 to 6 years after
designation, and (c) Areas with
attainment dates beyond 6 years after
attainment.
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• Areas with attainment dates 3 years
or less after designation.
We proposed these areas would be
treated similar to areas under subpart 2
that are classified as marginal, which do
not have an RFP requirement. We
proposed such an area would not be
subject to a separate RFP requirement,
but RFP would be met by demonstrating
the area could attain the standard by its
attainment date.
• Areas with attainment dates
between 3 to 6 years after designation.
These areas would have attainment
dates similar to subpart 2 areas
classified as moderate. We proposed
two options for these areas:
• Option 1. This option would
require the RFP plan to be submitted
with the attainment demonstration
within 3 years after designation of the
nonattainment area and RFP would be
met by a SIP that provides for
attainment as expeditiously as
practicable. Where areas have only 3
years after SIP submission before
attainment, this option recognizes that
there may be only a short amount of
time available to achieve any specified
emissions reductions to meet RFP. The
draft regulatory text incorporated this
option.
• Option 2. This option would
require these areas to be treated in a
manner similar to subpart 2 areas
classified as moderate. The RFP SIP
would have to provide for a 15 percent
emission reduction from the baseline
year within 6 years after the baseline
year. The RFP SIP would have to be
submitted within 2 years after
designation. However, since the area is
subject only to subpart 1, VOC or NOX
emissions reductions could be relied on
to meet the 15 percent reduction
requirement, consistent with EPA’s NOX
substitution policy.45 Also, we solicited
comment on whether a percentage other
than 15 percent should be required as
the minimum. Additional measures that
would provide the remaining portion of
the emissions reductions needed for
attainment would have to be submitted
with the area’s attainment
demonstration within 3 years after
designation.
• Areas with attainment dates beyond
6 years after designation.
These areas would have attainment
dates similar to areas classified under
subpart 2 as serious or higher. We
proposed that the RFP plan show
increments of progress from the baseline
emissions inventory year out to the
attainment date. The RFP SIP would
45 NO Substitution Guidance. December 15,
X
1993 (available at https://www.epa.gov/ttn/oarpg/
t1pgm.html).
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first have to provide for a 15 percent
emission reduction from the baseline
year within 6 years after the baseline
year. The 15 percent RFP SIP would
have to be submitted within 2 years
after designation. However, since the
area is subject only to subpart 1, NOX
emissions reductions could be
substituted for some or all of the 15
percent reduction requirement,
consistent with EPA’s NOX substitution
policy. Also, we solicited comment on
whether a percentage other than 15
percent would be more appropriate. For
each subsequent 3-year period out to the
attainment date, another RFP SIP would
have to provide for an additional
increment of progress no less than the
amount of emissions reductions that
would be proportional to the time
between the end of the first increment
to the attainment date. This second RFP
SIP would have to be submitted at the
same time as the attainment
demonstration, namely within 3 years
after designation.
b. Summary of Final Rule
We are finalizing rules for two, rather
than three, categories of areas based on
the CAA’s division of attainment dates
for subpart 1 areas under section
172(a)(2). This provision requires that
subpart 1 areas must attain as
expeditiously as practicable but no later
than 5 years after designation as a
nonattainment area. It also allows the
Administrator to extend the attainment
date beyond that 5 year period ‘‘* * *
for a period no greater than 10 years
from the date of designation as
nonattainment, considering the severity
of nonattainment and the availability
and feasibility of pollution control
measures.’’ The two scenarios for RFP
for subpart 1 areas are based on whether
the area does or does not receive an
extended attainment date. The following
are the two scenarios and the RFP
requirements for each:
Scenario A: Areas with attainment dates
5 years or less after designation (i.e., on
or before June 15, 2009 for areas
designated June 15, 2004).
As noted elsewhere in this preamble,
for areas classified under subpart 1,
emissions reductions needed for
attainment must occur by the beginning
of the ozone season preceding the
attainment date. Thus, to enable a SIP
to demonstrate attainment by June 15,
2009, the area must achieve all
necessary reductions by the beginning
of the 2008 ozone season. The final rule
provides that RFP for these areas would
be met by ensuring emissions
reductions needed for attainment are
implemented as noted above by the
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beginning of the ozone season prior to
the attainment date.
Scenario B: Areas with attainment dates
more than 5 years after designation (i.e.,
beyond June 15, 2009 for those areas
designated June 15, 2004). For these
areas:
• The RFP plan must show
increments of progress from the baseline
emissions inventory year out to the
attainment date.
• The RFP SIP would first have to
provide for a 15 percent emission
reduction from the baseline year
through the 6th year after the baseline
year (e.g., from January 1, 2003 through
December 31, 2008).
• The 15 percent RFP SIP must be
submitted within 3 years after
designation (e.g., by June 15, 2007).
• However, since the area is subject
only to subpart 1, NOX or VOC
emissions reductions (or both) could be
used to achieve the 15 percent emission
reduction requirement.
• For each subsequent 3-year period
out to the attainment date, the RFP SIP
would have to provide for an additional
increment of progress. The increment
for each 3-year period would be a
portion of the remaining emission
reductions needed for attainment
beyond those reductions achieved for
the first increment of progress (e.g.,
beyond 2008 for areas designated
nonattainment in June 2004).
Specifically, the amount of reductions
needed for attainment should be
divided by the number of years needed
for attainment after the first increment
of progress in order to establish an
‘‘annual increment.’’ For each 3-year
period out to the attainment date, the
area must achieve roughly the portion of
reductions equivalent to three annual
increments.46 This second RFP SIP must
46 For example, if the area’s attainment date is
2014, and a total of 30 percent reduction is needed
between the end of 2008 and the attainment date
(a 6-year period) to reach attainment, the ‘‘annual
increment’’ would be 5 percent (i.e., 1⁄6 of 30
percent). Thus, the area must achieve roughly the
portion of reductions equivalent to 15 percent (3 ×
5 percent) during the first 3 years (2009, 2010,
2011), and the remaining amount over the next 3
years (2012, 2013, 2014). By using the word
‘‘roughly’’ in the regulatory text, EPA does not
intend that States would be able to delay substantial
emission reductions from one 3-year period to the
next. Rather, EPA intends this modifier to allow
small deviations from the amount of emission
reductions that would be needed to meet a 3-year
RFP requirement. For example, assume that the
‘‘annual increment’’ of reductions needed for an
area to reach attainment (after the initial 6-year RFP
obligation) is 5 tons per day and that the area has
6 additional years until attainment. Thus, for each
of the two 3-year periods until attainment, the area
would need ‘‘roughly’’ 15 tons per day, so long as
the total for both periods is equivalent to or greater
than 30 tons per day (i.e., the total reductions
needed for attainment). Assuming the area could
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71643
also be submitted within 3 years after
the effective date of designation (i.e., by
June 15, 2007).
While the adopted rule is not
identical to any of the proposed options,
we believe it is a logical outgrowth of
our three proposed scenarios. The
adopted approach is more stringent than
certain of the proposed options and less
stringent than others. Since this final
decision incorporates elements of the
three proposed scenarios, we believe it
is similar in result to the three scenarios
proposed.
c. Comments and Responses
Comment: One commenter stated that
EPA has no authority to adopt ‘‘Option
1’’ for areas with attainment dates
between 3 and 6 years after designation,
because that option would waive any
showing of RFP.
Response: The EPA acknowledges
that Congress prescribed specific RFP
requirements under subpart 2, but for
subpart 1 provided more flexibility.
Our rule does not eliminate RFP
obligations for subpart 1 areas. We are
not requiring any specific percent
reduction for subpart 1 areas with nearterm attainment dates. The measures
that bring about near-term attainment
represent all the reductions that are
reasonable to require as annual
incremental progress towards
attainment. The EPA is not compelled to
require a 15 percent emission reduction
for all subpart 1 areas, especially in
those cases where a full 15 percent is
not needed in order to reach attainment.
However, we believe that it is generally
appropriate to require the full 15
percent for areas with long-term
attainment dates to ensure interim
progress towards attainment.
Comment: Some commenters
supported the proposal that ties the
required RFP showing to the attainment
date. Specifically, these commenters
supported the proposal that areas with
attainment dates of 3 years or less
should have no separate RFP
requirement, consistent with the
requirement applicable to marginal
areas under subpart 2. In addition,
support was shown for Option 1 for
subpart 1 areas with an attainment date
between 3 and 6 years following
designations. Under Option 1, areas
achieve 14 tons per day during the first 3-year
period, and achieve the remaining 16 tons per day
during the second 3-year period, we believe this
would be consistent with achieving ‘‘roughly the
portion of reductions equivalent to three annual
increments.’’ We do not believe, however, that use
of the word roughly allows States to delay
substantial emission reductions. Thus, in the
example above, it would not be appropriate for the
State to delay reductions of several tons per day
until the second 3-year period.
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would have to show an adequate rate of
reduction in order to achieve attainment
by the deadline, but there would be no
specific percentage reduction required.
Response: We acknowledge the
support of these comments.
Comment: Another commenter
believed that a 15 percent emissions
reductions requirement should only be
required where such reductions would
meaningfully advance the date of
attainment. The RFP requirement in
subpart 1 requires that the SIP provide
for ‘‘reasonable further progress,’’ and
where emissions reductions would not
create ‘‘reasonable further progress’’
either in the area itself or in downwind
areas, there is no basis under subpart 1
to require such specific emissions
reductions. They further said that
requiring a potentially expensive
reduction in emissions in those cases
where that reduction would not
improve air quality was not justified
based on a notion of ‘‘equity’’ with
similar areas classified under subpart 2
and noted that such an interpretation
was not required by the statute or
sensible. That some subpart 2 areas
might have to reduce emissions by a
specified percentage even where such
reductions would yield no positive
environmental benefits is an
unfortunate result of the Congress’
decision to limit EPA’s discretion under
subpart 2—which in turn is a result of
a far less sophisticated understanding of
the dynamics of ozone creation in 1990
than exists now—and where EPA has
the discretion not to dictate an
ineffective and inefficient result, it must
exercise that discretion.
Response: We addressed in general
those comments that recommended
alternatives to the mandatory measures
of subpart 2 (which includes the RFP
requirement) in the response to
comments above under the topic,
‘‘Should prescribed requirements of
subpart 2 apply in all 8-hour
nonattainment areas classified under
subpart 2, or is there flexibility in
application in certain narrowly-defined
circumstances?’’ We conclude in that
section that EPA has no discretion to
broadly waive mandatory requirements.
However, we noted that case law may
provide support for case-by-case
waivers where implementation of a
measure would produce an absurd
result.
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8. Where Part of an 8-hour
Nonattainment Area Was a 1-hour
Nonattainment Area With a ROP
Obligation Extending Past 2002, Can
Emissions Reductions From the Area’s
1-hour ROP Plan Be Used as Credit
Toward Meeting the Area’s 8-hour RFP
Plan?
[Section VI.I.9. of June 2, 2003
proposed rule (68 FR 32835); no draft or
final regulatory text.]
a. Background
We proposed the following approach
to address this issue. Where an area has
both 1-hour and 8-hour RFP obligations
for the post-2002 period, the State may
rely on emissions reductions from the 1hour plan in achieving RFP for the 8hour standard. The State could develop
a new baseline and new RFP emission
reduction targets for the entire 8-hour
standard nonattainment area (i.e., the
old 1-hour standard nonattainment area
and any newly added portion of the 8hour standard nonattainment area).
Emissions reductions from measures in
the 1-hour ozone SIP that are achieved
after the 8-hour ozone NAAQS baseline
year could count (subject to creditability
restrictions as discussed above) toward
meeting the RFP requirement for the
entire 8-hour area.
This approach would set a RFP target
for the entire 8-hour ozone
nonattainment area. Under this
approach, the new RFP target for the 8hour standard would replace the
previous 1-hour ROP target (while
ensuring that, at a minimum, the
emissions reductions required to meet
the old target are met; see 40 CFR
51.905(a)(1)(iii)).
b. Summary of Final Rule
We are adopting the approach from
the proposal.
c. Comments and Responses
Comment: One commenter agreed
with the approach outlined in the
proposal but cautioned that the States
would have to ensure that the target is
at least as stringent as the 1-hour ROP
target, thus ensuring no backsliding on
the 1-hour NAAQS requirements. Under
this approach, the State would have to
develop a new baseline and new RFP
emission reduction targets for the entire
8-hour standard nonattainment area.
Emissions reductions from measures in
the 1-hour ozone SIP that are achieved
after the 8-hour ozone NAAQS baseline
year could count (subject to credibility
restrictions as discussed in the proposed
rulemaking) toward meeting the RFP
requirement for the entire 8-hour area.
The new RFP target for the 8-hour
standard would replace the previous 1-
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hour ozone target (while ensuring that,
at a minimum, the emissions reductions
required to meet the old target are met).
Response: We agree with the
commenter that the emission reduction
targets under the 8-hour standard must
be at least as stringent as the 1-hour
targets. Section IV.E.3. of this preamble
discusses the requirements for RFP for
several situations relative to the area’s
former obligations under the 1-hour
standard and the current obligations
under the 8-hour standard. The
obligations of an area under the antibacksliding provisions of 40 CFR
51.905(a)(1)(iii) would still apply,
meaning that emissions reductions
under the 1-hour ROP requirements
would still be required as if the 1-hour
standard had never been revoked.
Therefore, the new 8-hour emission
target for the 8-hour area would be
logically at least as stringent as under
the 1-hour area for a given time period.
9. Will EPA’s ‘‘Clean Data Policy’’
Apply for Purposes of 8-hour RFP,
Attainment Demonstrations and Other
Related Requirements?
[Section VI.I.10 of June 2, 2003
proposed rule (68 FR 32835); no draft
regulatory text; section 51.918 of final
rule.]
a. Background
As noted in the proposal, we issued
a policy on May 10, 1995, which allows
EPA to determine that an area has
attained the standard and that certain
planning requirements (e.g., RFP and
attainment demonstrations) will not
apply so long as the area remains in
attainment.47 This is referred to as the
‘‘Clean Data Policy.’’ We proposed that
this policy would remain effective for
purposes of areas that EPA determines
have attained the 8-hour ozone NAAQS.
b. Summary of Final Rule
In the proposed rule, we indicated
that the Clean Data Policy, which we
had applied under the 1-hour standard,
should apply for purposes of the 8-hour
standard. We are adopting this
approach. In this action EPA is
finalizing the statutory interpretation
that is embodied in the policy. The text
of the final rule encapsulates the
statutory interpretation set forth in the
policy. Determinations as to whether
individual areas have attained the 847 Memorandum of May 10, 1995, ‘‘RFP,
Attainment Demonstration, and Related
Requirements for Ozone Nonattainment Areas
Meeting the Ozone National Ambient Air Quality
Standard,’’ from John S. Seitz, Director, Office of
Air Quality Planning and Standards. Available at:
https://www.epa.gov/ttn/oarpg/t1/memoranda/
clean15.pdf.
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hour standard and thus qualify for
application of the policy will be made
in the context of rulemakings for those
individual areas.
The EPA has applied the Clean Data
Policy in rulemakings under the 1-hour
ozone standard to both subpart 1 areas,
e.g., San Francisco Bay Area (69 FR
21717; April 22, 2004) and subpart 2
areas, e.g., St. Louis, Missouri (68 FR
25418; May 12, 2003). The EPA will also
apply the policy to both subpart 1 and
subpart 2 areas under the 8-hour
standard.
c. Comments and Responses
Comment: One commenter stated that
EPA’s ‘‘Clean Data Policy’’ is unlawful
with respect to both the 1-hour and 8hour NAAQS. A commenter argued that
EPA also has no authority to waive the
attainment demonstration and RFP
plans mandated by subpart 2 on the
pretext that an area has clean data. The
CAA unambiguously requires these
plans for any area designated
nonattainment for the pollutant ozone,
and gives EPA no power whatsoever to
waive such plan requirements.
Several other commenters supported
the continued use of the ‘‘Clean Data
Policy.’’
Response: The EPA believes that the
Clean Data Policy comports with the
provisions of the CAA in regard to
attainment demonstrations, ROP plans,
RACM, contingency measures and other
related requirements. The Clean Data
Policy, issued on May 10, 1995, sets
forth EPA’s interpretation that where
EPA has determined that an area has
attained the standard, certain SIP
requirements are suspended (e.g., RFP)
for so long as the area remains in
attainment.
As set forth in its May 10, 1995
policy, EPA believes it is reasonable to
interpret the provisions regarding RFP
and attainment demonstrations, along
with certain other related provisions, as
not requiring further submissions to
achieve attainment for so long as the
area is in fact attaining the standard.
Under the policy, EPA is not granting an
exemption from any applicable
requirements under part D. Rather, EPA
has interpreted these requirements of
subparts 1 and 2 as not applying for so
long as the area remains in attainment
with the standard. This is not a waiver
of requirements that by their terms
apply; it is a determination that certain
requirements are written so as to be
operative only if the area is not attaining
the standard.
The EPA has explained in other
rulemaking actions on the 1-hour ozone
standard its rationale for the
reasonableness of this interpretation of
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the CAA and incorporates these
explanations by reference. See, for
example, 67 FR 49600 (July 31, 2002);
65 FR 37879 (June 19, 2000) (CincinnatiHamilton, Ohio-Kentucky); 61 FR 20458
(May 7, 1996) (Cleveland-Akron-Lorain,
Ohio); 66 FR 53094 (October 19, 2001)
(Pittsburgh-Beaver Valley,
Pennsylvania); 60 FR 37366 (July 20,
1995); 61 FR 31832–33 (June 21, 1996)
(Grand Rapids, MI); 60 FR 36723 (July
18, 1995) (Salt Lake and Davis Counties,
Utah); 68 FR 25418 (May 12, 2003) (St.
Louis, Missouri); 69 FR 21717 (April 22,
2004) (San Francisco Bay Area). The
EPA has also set forth its legal rationale
for the Clean Data Policy in briefs filed
in the 10th, 7th, and 9th Circuits, and
hereby incorporates those briefs insofar
as relevant here. See Sierra Club v. EPA,
No. 95–9541 (10th Cir.), Sierra Club v.
EPA, No. 03–2839, 03–3329 (7th Cir.),
Our Children’s Earth Foundation v.
EPA, No. 04–73032 (9th Circuit).
As stated in the policy, the attainment
demonstration, RFP requirements and
contingency measure requirement are
designed to bring an area into
attainment. Once this goal has been
achieved, it is appropriate to suspend
the obligation that States submit plans
to meet these goals, so long as the area
continues to attain the relevant
standard.
The Tenth, Seventh and Ninth
Circuits have upheld EPA rulemakings
applying the Clean Data Policy. See
Sierra Club v. EPA, 99 F. 3d 1551 (10th
Circuit, 1996), Sierra Club v. EPA, 375
F. 3d 537 (7th Circuit, 2004) and Our
Children’s Earth Foundation v. EPA, No.
04–73032 (9th Circuit, June 28, 2005)
memorandum opinion.
Comment: A commenter said that
although subpart 2 contains some
narrowly crafted exceptions [e.g., CAA
182(b)(1)(A)(ii)], there are no exceptions
based on clean data. In the past, EPA
has cited a Tenth Circuit decision,
Sierra Club v. EPA, 99 F. 3d 1551 (10th
Circuit, 1996), as supporting the Clean
Data Policy. The commenter contended
that case was wrongly decided and has
been superseded by the Supreme Court
decision in Whitman v. American
Trucking Assoc., Inc., 531 U.S. 457
(2001). There, the Court held that
subpart 2 eliminates regulatory
discretion previously allowed to EPA
under subpart 1, and noted that subpart
2 prescribes large parts of
nonattainment programs, for example,
section 182. The requirements for RFP
and attainment demonstrations are
among those subpart 2 nonattainment
programs that Congress prescribed by
law, thereby eliminating EPA discretion
to accept something less. See also Sierra
Club v. EPA, 293 F. 3d 155 (D.C. Circuit,
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71645
2002) (holding that EPA is without
authority to infer exceptions to
attainment deadlines and to explicit
subpart 2 requirements for RFP plans).
Response: The EPA believes that the
Tenth Circuit correctly decided Sierra
Club v. EPA and that the comments
misconstrue both Whitman and Sierra
Club v. EPA, 293 F. 3d 155 (D.C. Circuit,
2002) (Sierra Club 2002). The Sierra
Club 2002 case addressed the statutory
requirements applicable to an area not
attaining the standard. The issue of the
requirements of part D of title I of the
CAA that must continue to be met by
areas that EPA has determined are
monitoring attainment of the standard
was not before the court. As discussed
below, the Sierra Club 2002 decision
upheld EPA’s determination that the
RACM provision under section 172(c)(1)
requires only additional measures that
could contribute to RFP or attainment,
which is an element of EPA’s
application of the Clean Data Policy. To
this limited extent, Sierra Club 2002 is
relevant to EPA’s interpretation that the
policy will apply for the 8-hour ozone
standard, and the decision supports
EPA’s interpretation. However, the other
issues addressed in the decision
(extension of the statutory attainment
date for areas affected by ozone
transport, the content of a
demonstration of RFP toward
attainment, and whether contingency
measures must be submitted as part of
an attainment demonstration or plan for
RFP) did not relate to the Clean Data
Policy or how the subpart 2
requirements apply to areas attaining
the standard.
The issue addressed by the Clean Data
Policy is whether an area that has
attained the standard (as evinced by air
quality monitoring data) still needs to
submit a demonstration of how the area
will achieve enough reductions to
demonstrate that it will ‘‘attain the
NAAQS,’’ a plan to obtain reasonable
periodic reductions towards the goal of
attainment and other related
requirements.
The EPA continues to believe that the
statutory requirement for an attainment
demonstration—a SIP revision which
identifies the level of future reductions
needed to achieve the NAAQS and any
additional adopted measures needed to
achieve these future reductions—is
written so as to be inapplicable once the
NAAQS is attained.
In addition, EPA believes that the
RACM requirements are a ‘‘component’’
of an area’s attainment demonstration
under section 172(c)(1). General
Preamble 57 FR 13560; April 16, 1992.
Thus, since for the same reason the
attainment demonstration no longer
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applies by its own terms, RACM also no
longer applies. The EPA has
consistently interpreted this provision
to require only implementation of
potential RACM measures that could
contribute to reasonable further progress
or to attainment. General Preamble 57
FR 13498; April 16, 1992. Thus, where
an area is already attaining the standard,
no additional RACM measures are
required.48
Likewise, EPA concludes that the
provision for RFP—a plan for annual
incremental reductions leading to
attainment—is also expressed in terms
that show that RFP is unnecessary in
areas attaining the standard. For areas in
attainment, there is no longer a need to
plan for measures to meet that goal.
Similarly, EPA continues to believe that
the contingency measure requirements
of section 172(c)(9) no longer apply in
an area that is attaining the standard
since those ‘‘contingency measures are
directed at ensuring RFP and attainment
by the applicable date.’’ (See 57 FR
13564; April 16, 1992). The section
182(c)(9) contingency measure
requirement also no longer applies once
an area has attained the standard.
Section 172(c)(2) of the CAA and the
related provisions of subpart 2 provide
that RFP is required only where an area
continues to violate the standard. By
definition, the ‘‘reasonable further
progress’’ provision requires only such
reductions in emissions as are necessary
to attain the NAAQS by the attainment
date. If an area has attained the
standard, the stated purpose of the RFP
provision has been fulfilled. Also,
section 172(c)(1) and the related
provisions of subpart 2 require SIPS to
provide for attainment of the NAAQS.
(See also section 182(b)(1)(A)(i) which
requires that SIPS for moderate ozone
nonattainment areas must ‘‘provide for
such specific annual reductions in
emissions of [VOCs] and [NOX] as
necessary to attain the [ozone NAAQS]’’
by the applicable attainment date).
When an area has attained the NAAQS,
there is no need for a plan
demonstrating how it will reach
attainment, and thus the attainment
demonstration provision no longer
applies. Similarly section 172(c)(9) and
the related provisions of subpart 2
provide that SIPs in nonattainment
48 [The EPA’s interpretation that the statute
requires only implementation of RACM measures
that would advance attainment was upheld by the
United States Court of Appeals for the Fifth Circuit
(Sierra Club v. EPA, 314 F. 3d 735, 743–745, 5th
Cir. 2002) and by the United States Court of
Appeals for the D.C. Circuit (Sierra Club v. EPA,
294 F. 3d 155, 162–163, D.C. Cir. 2002). See also
the final rulemakings for Pittsburgh-Beaver Valley,
Pennsylvania, 66 FR 53096 (October 19, 2001) and
St. Louis, 68 FR 25418 (May 12, 2003).]
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areas shall provide for contingency
measures to be undertaken if the area
fails to make RFP or to attain the
NAAQS by the applicable attainment
date. Since contingency measures are
required only if RFP or attainment is not
achieved, there is no need for them
where the area has attained the
standard. The language of these
statutory provisions indicates that when
an area has attained the standard these
requirements no longer apply as the
purpose of these provisions—
attainment—has been accomplished.
The EPA believes that Whitman does
not provide a basis to reconsider our
position on the Clean Data Policy. In
Whitman, the Court was addressing
EPA’s stated approach that subpart 2
did not apply for purposes of
implementing the 8-hour NAAQS. In
the Phase 1 rule, EPA addressed the
Court’s decision and concluded that
subpart 2 does apply. The issue here is
not whether it applies, but how those
requirements apply under a specific
situation where an area has attained the
NAAQS. That issue was not addressed
by the Court in Whitman. The decision
in Whitman has no bearing on the
question of whether an area that has
demonstrated attainment must
nonetheless submit an attainment
demonstration plan and related
requirements. Thus, Whitman does not
undermine the Tenth Circuit’s reasoning
in Sierra Club v. EPA, 99 F. 3d 1551
(10th Circuit, 1996). See also the postWhitman decisions in Sierra Club v.
EPA, 375 F. 3d 537 (7th Circuit, 2004),
and Our Children’s Earth Foundation v.
EPA, No. 04–73032, memorandum
opinion (9th Circuit, June 28, 2005)
rejecting challenges to the Clean Data
Policy and upholding redesignation
actions based on the policy.
10. How will RFP be addressed in Tribal
areas?
[Section VI.I.11. of June 2, 2003
proposed rule (68 FR 32835); no draft or
final regulatory text.]
a. Background
The TAR provides flexibility for
Tribes in the preparation of a TIP to
address the NAAQS. As mentioned in
the proposed rulemaking, the TAR
provides the Tribes with the ability to
develop TIPs to address and implement
the NAAQS in Indian country. It further
provides the Tribes with flexibility to
develop these plans in a modular way,
as long as the elements of their TIPs are
reasonably ‘‘severable.’’ For example,
each TIP submission must include a
demonstration that the Tribe has
authority to develop and run its
program, the ability to enforce its rules,
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and the capacity and resources to
implement the program it adopts.
Therefore, it may include one or two
source-specific requirements but may
not include provisions for RFP and
other SIP requirements. The proposal
noted that these TIPs can be an
important step in addressing an overall
air quality plan to achieve health and
environmental goals on Tribal lands.
Where a Tribe chooses not to address a
specific planning element, EPA may be
obligated to step in. Such action would
not preclude a Tribe from addressing
those elements at a later time.
b. Summary of Policy
We intend to take the approach noted
in the proposal. There is no regulatory
text for this intention.
c. Comments and Responses
No comments were received on this
portion of the proposal.
11. How will RFP targets be calculated?
[Section VI.I.12. of June 2, 2003
proposed rule (68 FR 32836); § 51.910(c)
of the draft and final regulatory text.]
a. Background
We proposed a methodology for the
calculation of RFP target levels of
emissions that is based on the method
we developed for the 1-hour standard,
while taking into account our
interpretation of CAA restrictions on
creditable emissions and our proposal to
use the 2002 inventory as the baseline
inventory for the RFP requirement. The
CAA specifies four types of measures
that were not creditable toward the 15
percent RFP requirement. These are:
(1) Any measure relating to motor
vehicle exhaust or evaporative
emissions promulgated by the
Administrator by January 1, 1990.
(2) Regulations concerning Reid
Vapor Pressure (RVP) promulgated after
1990 or required under section 211(h).
(3) Measures required under section
182(a)(2)(A) to correct deficiencies in
SIPs regarding VOC RACT regulations
required prior to enactment of the CAA
Amendments of 1990.
(4) State regulations submitted to
correct deficiencies in I/M existing or
required programs.
These four types of measures were all
expected to result in a decrease in
emissions between 1990 and 1996. Of
these four types of measures, RACT and
I/M program corrections and the 1992
RVP requirements were completely in
place by 1996 and therefore are already
accounted for in the 2002 baseline. As
a result, they would produce no
additional reductions between 2002 and
2008 or later milestone years.
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However, the pre-1990 Federal Motor
Vehicle Control Program (FMVCP) will
continue to provide additional benefits
during the first two decades of the 21st
century as remaining vehicles meeting
pre-1990 standards are removed from
the vehicle fleet. Because these benefits
are not creditable for RFP purposes, in
order to calculate the target level of
emissions for future RFP milestone
years (i.e., 2008, 2011, etc.), States must
first calculate the reductions that would
occur over these future years as a result
of the pre-1990 FMVCP. We proposed
three methods to properly account for
the non-creditable reductions when
calculating RFP targets for the 2008 and
later RFP milestone years.
b. Summary of Final Rule
The calculation methods have been
revised slightly from those in the
proposal. The revisions now account for
NOX reductions and take account of
other mobile emissions models other
than the MOBILE model. The methods
appear as appendix A to this preamble.
These methods are consistent with the
requirements of sections 182(b)(1)(C)
and (D) and 182(c)(2)(B) of the CAA.
c. Comments and Responses
Comment: One commenter agreed that
the base emission level should be
decreased by reductions that occur from
the pre-1990 FMVCP standards (1990
I/M program and fuel RVP of 9.0 or 7.8
psi). However, the commenter further
recommended that the reductions from
pre-1990 FMVCP standards be
calculated using the I/M program and
fuel properties in effect during the new
baseline year of 2002.
The commenter claimed an advantage
of the recommended change is that it
removes from the non-creditable
reductions from the pre-1990 FMVCP
standards, creditable reductions from
controls implemented prior to 2003
(such as improvements to the I/M
program or cleaner gasoline).
The commenter claimed that the EPA
proposal specifies using the MOBILE6
command NO CAA in the calculation of
the non-creditable emissions reductions.
The commenter concurred that this
command could be used, but recognized
that some of the controls in effect during
2002 cannot be modeled with this
command. (Refer to technical specifics
of this comment in the response to
comment document).
Response: The EPA does not agree
with the commenter that the noncreditable pre-1990 FMVCP reductions
should be calculated using the I/M
program and fuel properties in effect
during the new baseline year of 2002.
Including the I/M program and fuel
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properties in effect in 2002 in the
calculation of non-creditable reductions
would not accurately account for
reductions that are the result of pre1990 Federal motor vehicle control
measures. The EPA believes that the
methods provided in the final rule
accurately identify the non-creditable
reductions from pre-1990 motor vehicle
standards and provide appropriate
credit for all post-1990 control
measures.
justification. Substitutions are restricted
to intrastate areas unless two or more
States involved reach mutual agreement.
The EPA notes that in all cases the
distances in the policy provide only a
general policy presumption that, if used,
would need data resources in the record
showing that reductions from sources in
the specific locations in attainment
areas benefit the nonattainment area.
See LEAN v. EPA, 382 F. 3d 575 5th
Circuit, 2004.
12. Should EPA continue the policy of
allowing substitution of controls from
outside the nonattainment area within
100 kilometers for VOC and 200
kilometers for NOX?
[Section VI.I.2. of June 2, 2003
proposed rule (68 FR 32833); no draft or
final regulatory text.]
b. Summary of Final Rule
States may continue to rely on
emissions reductions from outside the
nonattainment area for credit toward
their RFP obligations.49 In doing so,
States should ensure that the reductions
meet the standard tests of creditability
(permanent, enforceable, surplus, and
quantifiable) and are shown to be
beneficial toward reducing ozone in the
nonattainment area.
a. Background
The proposal noted [68 FR 32833] that
EPA currently has a policy that allows
States to take credit for RFP for NOX and
VOC controls that occur outside the
nonattainment areas [‘‘Guidance for
Implementing the 1-Hour Ozone and
Pre-Existing PM10 NAAQS, December
29, 1997’’]. Specifically, the guidance
allows credit for VOC reductions
occurring up to 100 km outside the area
and for NOX reductions occurring up to
200 km outside the area (statewide
where a regional NOX control strategy is
being implemented). The policy
indicates that credit may be taken only
for emissions reductions from measures
not otherwise mandated by the CAA. As
explained in the policy, EPA believes
that this additional flexibility for
crediting reductions outside
nonattainment areas is consistent with
the CAA. We noted in the proposed
policy that reductions from outside a
nonattainment area within the
geographic limits contribute to progress
toward attainment within the area (61
FR 65758).
Under this approach, the geographic
area for substitution of VOC emissions
reductions is 100 km from the
nonattainment area and the geographic
area for substitution of NOX reductions
is 200 km from the nonattainment area
with the possibility for additional
expansion of the NOX substitution area
as follows. Nitrogen oxides emissions
reductions from anywhere within the
State may be credited for those States
that participate in a regional NOX
control strategy such as the NOX SIP
Call. All other States implementing a
NOX substitution strategy for RFP would
be restricted to a distance of 200 km
from the nonattainment area, unless a
substitution for a greater distance is
accompanied by adequate technical
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c. Comments and Responses
Comment: Several commenters
supported this feature of EPA’s proposal
regarding RFP because it allows the
States flexibility to tailor control
strategies to address the issues specific
to a particular nonattainment area.
The commenters supported
codification (68 FR 32833, column 1) in
the final rule of the December 29, 1997
guidance memo (‘‘Guidance for
Implementing the 1-Hour Ozone and
Pre-Existing PM10 NAAQS’’) that allows
emissions reductions from outside the
nonattainment area to be creditable
toward RFP. One commenter agreed that
States ought to be able to account for
regional emissions in their attainment
demonstrations. On the other hand, the
commenter was concerned that the
Agency might allow jurisdictions to
‘‘credit’’ emissions reductions from
sources up to 100 km for VOC and 200
km for NOX toward 15 percent RFP
plans, and this in turn could encourage
jurisdictions in need of these tonnage
49 Last September, the EPA Office of Inspector
General submitted a report (outside the rulemaking
process) outlining concerns and recommendations
with respect to the potential for double counting of
emissions reductions and problematic equity issues.
U.S. EPA Office of the Inspector General. In
responding to that report, we indicated that we
would consider the various recommendations as we
assess existing policies and guidance in parallel to
the rulemaking for implementing the 8-hour ozone
standard. [Evaluation Report: EPA and States Not
Making Sufficient Progress in Reducing Ozone
Precursor Emissions In Some Major Metropolitan
Areas. Report No. 2004–P–00033. September 29,
2004.] [Memorandum from Jeffrey R. Holmstead to
J. Rick Beusse, ‘‘Response to the Office of the
Inspector General (OIG) Evaluation Report, EPA
and States Not Making Sufficient Progress in
Reducing Ozone Precursor Emissions in Some
Major Metropolitan Areas,’’ Report No. 2004–P–
00033. December 29, 2004. March 25, 2005.]
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reductions to regulate without a sound
basis. The commenter contended that
while ozone is known to be a ‘‘regional
pollutant,’’ EPA has failed to establish
in this rulemaking any technical basis
for allowing States to impose
regulations on sources outside the
nonattainment area boundaries without
independent justification of the impact
of such sources on an area’s failure to
attain the standard.
Response: We developed our 1997
policy as a result of the modeling results
relating to the NOX SIP Call (see, for
example, 63 FR 57355, October 27,
1998, and 69 FR 21604, April 21, 2004).
These modeling analyses demonstrate
that significant contribution to
nonattainment resulted not only from
source emissions within a
nonattainment area but also from source
emissions over a much broader area. Not
only can these emissions from outside
the nonattainment area affect air quality
within the nonattainment area, in some
cases it might be necessary to include
and control emission sources located in
the nearby areas in order to attain the
standard. We believe it is appropriate to
allow States to take credit for reductions
from sources outside their
nonattainment areas where data indicate
that those emissions affect air quality in
the nonattainment areas.
We note that section 182(c)(2)(C),
which provides for the substitution of
NOX controls for VOC, speaks in terms
of reductions of ozone concentrations
rather than strictly reductions in
emissions. This provision led us to
conclude that Congress’ intent for the
ROP requirement is to lower ozone
concentrations within the
nonattainment area. It is consistent with
that intent that emissions reductions
from outside the nonattainment area
that will reduce ozone concentrations in
the nonattainment area should be
creditable in RFP demonstrations. We
also believe that the CAA is clear that
both the 15 percent plan requirement of
section 182(b)(1) and the 3 percent per
year requirement of section 182(c)(2) are
specific varieties of RFP requirements.50
Section 171(1) of the CAA states that,
for purposes of part D of title I, RFP
‘‘means such annual incremental
reductions in emissions of the relevant
air pollutant as are required by this part
or may reasonably be required by the
50 The EPA notes that paragraph (1) of subsection
182(b) is entitled ‘‘Plan Provisions for Reasonable
Further Progress’’ and that subparagraph (B) of
paragraph 182(c)(2) is entitled ‘‘Reasonable Further
Progress Demonstration,’’ thereby making it clear
that both the 15 percent plan requirement of section
182(b)(1) and the 3 percent per year requirement of
section 182(c)(2) are specific varieties of RFP
requirements.
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Administrator for the purpose of
ensuring attainment of the applicable
NAAQS by the applicable date.’’ Thus,
whether dealing with the general RFP
requirement of section 172(c)(2), or the
more specific RFP requirements of
subpart 2 for classified ozone
nonattainment areas (i.e., the 15 percent
plan requirement of section 182(b)(1)
and the 3 percent per year requirement
of section 182(c)(2)), the purpose of RFP
is to ensure attainment by the applicable
attainment date. Emissions reductions
strategies applied to sources outside the
nonattainment area may help decrease
ambient ozone levels within the
designated area. Since RFP/ROP is
progress towards attainment, specific,
annual emissions reductions from
geographic areas outside the
nonattainment area boundaries that
contribute to lower ambient ozone
levels in the nonattainment area would
fall within the scope of ‘‘such annual
incremental reductions in emissions of
the relevant air pollutant as are required
* * * for the purpose of ensuring
attainment of the applicable NAAQS by
the applicable date.’’
Comment: One commenter requested
clarification that if the 100 km/200 km
area extends into adjacent States that
reductions in those States should also
be creditable, especially with regard to
the implementation of Federal
measures.
Response: We intend to look into this
issue further in the future as part of the
overall reassessment of the 100 km/200
km credit issue.
Comment: Another commenter
expressed confusion by the provision to
allow creditable reductions be made
outside nonattainment areas. They
asked if reductions made outside a
nonattainment area actually bring that
nonattainment area into compliance
with the standard, then shouldn’t those
outside areas be designated
nonattainment by definition? The
commenter contended that this
contradiction is unacceptable, and a
fatal flaw of current designation efforts
and this implementation proposal.
Response: The commenter appears to
be commenting on the designation
process as well as the implementation
rule. To the extent that the commenter
has concerns about the process EPA
used for designating areas as
nonattainment, those issues should have
been raised prior to the time EPA
promulgated designations in April 2004.
The EPA is not taking any action in this
rulemaking to establish the procedures
for designating areas or to designate
areas. In the designation process that
was completed in April 2004, EPA
provided guidance to areas regarding
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how to determine the boundaries of
nonattainment areas in light of the
statutory definition of ‘‘nonattainment,’’
which provides that an area will be
designated nonattainment if it is either
violating the NAAQS or is a ‘‘nearby’’
area that ‘‘contributes to ambient air
quality’’ in an area that is violating the
standard.51 The CAA does not establish
a hard-and-fast set of rules for
determining ‘‘nearby’’ or ‘‘contributes
to,’’—i.e., it does not specify a distance
that is nearby or a specific level of
emissions that is deemed to ‘‘contribute
to’’ nonattainment. Nor did EPA
establish a hard-and-fast set of rules;
rather the guidance provided a broad set
of factors for States and EPA to consider
in determining the boundaries of each
nonattainment area. Thus, it is not
inconsistent with the statute that there
are areas that were not designated
nonattainment, but that have emissions
that affect air quality in a nonattainment
area.
Comments on Draft Regulatory Text
Comment: One commenter
recommended that EPA state, either in
the preamble to this rule or in the rule
itself, that any VOC emissions
reductions within 100 km and any NOX
emissions reductions within 200 km of
the nonattainment boundary, including
reductions in adjacent States, are
creditable for RFP plan purposes. They
also suggested that EPA provide that
reductions from voluntary measures
should be incorporated into the baseline
emissions inventory calculation.
Another commenter stated that EPA
does not specify in § 51.910(a)(4) that in
areas where the 3 percent annual
reduction is required, those reductions
must be achieved within the statutorily
defined baseline ‘‘area.’’ [CAA section
182(b)(1)(B)]. The commenter stated that
we issued initial NOX substitution
guidance in 1993 that required RFP
reductions to be achieved from sources
within the designated nonattainment
area. The commenter noted that
subsequently, we attempted to
unlawfully allow RFP reductions to be
obtained from sources within the
modeling domain. The commenter
advocated that we clarify that the CAA
requires creditable reductions to be
obtained only from sources within the
designated nonattainment areas.
Response: We believe that the policy
does not need to be incorporated into a
rule. Since areas must include record
51 Memorandum from John Seitz, ‘‘Boundary
Guidance on Air Quality Designations for the 8Hour Ozone National Ambient Air Quality
Standards (NAAQS or Standard).’’ March 28, 2000.
Found at: https://www.epa.gov/ozonedesignations/
guidance.htm.
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support for application of the policy in
an area demonstrating that emissions
from regulated sources affect ambient
air quality in the specific nonattainment
area, individual rulemaking in the
context of an area’s SIP must be
conducted in any event to implement
the policy. The EPA believes that any
reductions that in fact result in
improved air quality within the
nonattainment area can be credited to
RFP demonstrations. Voluntary
emissions reductions that are used to
satisfy RFP requirements—or any
requirements under the CAA—must
meet EPA’s criteria for creditability of
such reductions, particularly the
inclusion in the baseline of the
emissions from the sources that would
be producing the voluntary reductions.
As explained elsewhere in response to
another comment on the policy of
allowing substitution of controls from
outside the nonattainment area within
100 km for VOC and 200 km for NOX,
EPA disagrees with the comment that
the CAA limits the scope of creditable
emissions reductions to only those
reductions in emissions emanating from
within the nonattainment area
boundaries. We also address elsewhere
the comment relating to allowance of
RFP credit from emissions reductions
outside the State in which the
nonattainment area is located.
13. When must RFP emissions
reductions be achieved?
[Section VI.I. of June 2, 2003 proposed
rule (several locations starting at 68 FR
32832); several locations including
§ 51.910(a)(1) of the draft and final
regulatory text.]
a. Background
Section 51.910(a)(1) of the draft
regulatory text provided that for areas
initially designated nonattainment for
the 8-hour NAAQS, the initial 6-year
period for RFP shall run from January 1,
2003 to December 31, 2008. Section
182(c)(2)(B), applicable to serious and
above areas, requires that RFP be
continued out to the attainment date.
Therefore, § 51.910(a)(2) of the draft
regulatory text provided, ‘‘For each area
classified as serious or higher under
§ 51.903, the State must submit no later
than 3 years after the effective date of
the area’s nonattainment designation a
SIP revision consistent with section
182(c)(2)(B) of the CAA for each 3 year
period following the initial 6-year
period addressed under paragraph
(a)(1)(ii)(B) of this section until the
area’s attainment date. For areas
initially designated nonattainment for
the 8-hour NAAQS the 3-year periods
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referenced in section 182(c)(2)(B) of the
Act shall begin January 1, 2009.’’
In applying the requirement of section
182(c)(2)(B), it is necessary to know the
attainment date for the area. The
attainment date is not necessarily the
maximum allowed under part D of the
CAA, but must be ‘‘as expeditious as
practicable’’ but no later than the
maximum statutory date (e.g., 9 years
after designation for a serious area).
Thus, for purposes of determining the
period for which RFP is needed, the
State must have completed an
attainment demonstration and RACM
analysis (discussed elsewhere in this
preamble) to demonstrate that the
attainment date selected is as
expeditious as practicable.
There are several other provisions that
bear on the issue of when emissions
reductions must be achieved for
purposes of the RFP requirements. The
Phase 1 Rule, § 51.900(g) sets forth the
following definition: ‘‘Attainment year
ozone season shall mean the ozone
season immediately preceding a
nonattainment area’s attainment date.’’
Also, § 51.908 52 (What is the required
time frame for obtaining emission
reductions to ensure attainment by the
attainment date?) provides: ‘‘For each
nonattainment area, the State must
provide for implementation of all
control measures needed for attainment
no later than the beginning of the
attainment year ozone season.’’ Thus, if
the latest attainment date allowed by the
CAA for a serious area designated in
2004 is June 15, 2013, the (complete)
ozone season preceding that date would
occur in 2012. However, if all of the
reductions necessary to achieve
attainment are in place prior to that
ozone season, then the most expeditious
attainment date would in fact be just
after the end of that ozone season in
2012 (assuming the RACM analysis did
not compel a more expeditious
attainment year). Thus, in light of the
Phase 1 rule, the latest possible
attainment date for all areas will be just
after the end of the ozone season in the
year prior to the outside attainment date
identified in the statute for the area’s
classification.53
Consistent with the manner in which
ROP plans under the 1-hour ozone
standard were developed, the RFP
baseline for 2002 will have a typical
summer day tons/day basis. As such,
the attainment year target will also be a
typical summer day target. Thus, the
52 With
this rulemaking, this provision is codified
as 40 CFR 51.908(d).
53 With the exception of areas with year-round
ozone seasons, in which case the latest attainment
date may be earlier in the year of the outside
attainment date identified in the statute.
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71649
target level of emissions must be met by
the attainment date of the attainment
year.54
As noted above, section 182(c)(2)(B)
requires that RFP be continued out to
the attainment date. Thus, to some
extent, the RFP requirement may help
determine the attainment date. In the
example discussed above of a serious
area, the first milestone year after 2008
by which an annual average of 3 percent
emissions reductions would have to be
achieved over each 3-year period (i.e., 9
percent over 3 years) would be 2011,
with an additional annual average of 3
percent per year between the end of
2011 and the attainment year (if the
attainment year is beyond 2011). The
maximum statutory attainment year
under the discussion above would be
2013, but, for the reasons explained
above concerning the date by which
emissions reductions must be achieved,
the actual maximum attainment year
would generally be the year prior, viz.,
2012. If for example this area needs an
additional 7 percent emission reduction
for attainment purposes beyond 2008,
however, RFP would require
implementation of the entire 7 percent
no later than the end of 2011. Since that
is the amount needed for attainment, the
area would actually achieve attainment
by 2011, and the attainment date would
then have to be no later than 2011. If the
area did not achieve this 7 percent
reduction until the end of 2011, the RFP
requirement in this case could not
require the full 9 percent reduction.
Thus, since RFP is only needed up to
the attainment date, should the area
achieve the 7 percent earlier in the year
it would have achieved attainment and
no further ROP would be required.
Therefore, in this example, RFP would
not require more reductions than
needed for attainment. Furthermore, the
RFP requirement by itself would not
force an attainment year earlier than
2011 for this case (e.g., 2010—2 years
after 2008), since the 7 percent
reduction over 2 years is greater than an
annual average of 3 percent, which is
beyond that required by the RFP
requirement. In summary, RFP
reductions end at the attainment date,
and as shown the RFP requirement
would not result in emissions
reductions greater than needed for
attainment.
b. Summary of Final Rule
For each area classified as moderate
or higher, the State’s 15 percent VOC
54 Note that 40 CFR 51.900(g) defines ‘‘Attainment
year ozone season’’ as the ozone season
immediately preceding a nonattainment area’s
attainment date.
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emission reduction plan must provide
for the emissions reductions to be
achieved by the end of the 6-year period
after the baseline year. The 6-year
period referenced in section 182(b)(1) of
the CAA shall begin January 1 of the
year following the year used for the
baseline emissions inventory. For areas
initially designated nonattainment for
the 8-hour NAAQS, the 6-year period
runs from January 1, 2003 to December
31, 2008.
For each area classified as serious or
higher, the State’s RFP plan must
provide a 3 percent annual emission
reduction requirement averaged over
every 3-year period after the initial 6year period. For areas initially
designated nonattainment for the 8-hour
NAAQS, the first 3-year period would
run from January 1, 2009 to December
31, 2011. The final increment of
progress must be achieved no later than
the attainment date for the area.
To summarize, for areas designated
nonattainment for the 8-hour NAAQS
with an effective date of June 15, 2004,
the rule would establish the following:
• The 6-year period in section
51.910(a)(1)(i)(A) and (ii)(C)(1) would
run from January 1, 2003 to December
31, 2008.
• The first 3-year period in section
51.910(a)(1)(i)(B) would run from
January 1, 2009 to December 31, 2011.
• The baseline emissions inventory in
section 51.910(d) would be for calendar
year 2002.
The April 1992 General Preamble
provides:
c. Comments and Responses
The EPA’s 1992 guidance on
calculating the 15 percent emission
target 55 contained the following:
No comments were received on the
proposal concerning the timing of
emissions reductions needed for RFP.
14. Banked Emission Reduction Credits
(Including Shutdown Credits)
Can pre-baseline emission reduction
credits be used to satisfy the RFP
requirement? [No discussion in June 2,
2003 proposal; no draft or final
regulatory text.]
a. Background
This topic was not discussed in the
proposed rulemaking, but we believe
that questions that have arisen on this
topic bear some discussion here.
The CAA provides the following
definition in section 182(b)(1)(D)
regarding the 15 percent VOC RFP
requirement:
Baseline emissions. For purposes of
subparagraph (A), the term ‘‘baseline
emissions’’ means the total amount of actual
VOC or NOX emissions from all
anthropogenic sources in the area during the
calendar year of the enactment of the Clean
Air Act Amendments of 1990, excluding
* * * [emphasis added.]
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The adjusted base year inventory (i.e.,
baseline emissions) must contain only actual
emissions occurring in the base year, 1990,
within the designated nonattainment area
boundaries. The baseline emissions should
not include pre-enactment banked emission
credits since they were not actual emissions
during the calendar year of enactment [57 FR
13507; April 16, 1992; emphasis added].
and
Pre-enactment banked emissions reductions
credits are not creditable toward the 15
percent progress requirement. However, for
purposes of equity, EPA encourages States to
allow sources to use such banked emissions
credits for offsets and netting. When States
use such banked credits for offsets and
netting to the extent otherwise creditable
under the Part D NSR regulations, these preenactment emissions credits must be treated
as growth. Consequently, this ‘‘growth’’ must
be accounted for, as is the case with all other
anticipated growth, in order to ensure that it
does not interfere with the 15 percent rate of
progress requirement (which is ‘‘net’’ of
growth). In addition, when such growth
emissions are used as offsets, they must be
applied in accordance with the offset ratio
prescribed for the area of concern (e.g., 1.3
to 1 for severe areas, etc.). All pre-enactment
banked credits must be included in the
nonattainment area’s attainment
demonstration for ozone to the extent that the
State expects that such credits will be used
for offsets or netting prior to attainment of
the ambient standards. Credits used after that
date will need to be consistent with the area’s
plan for maintenance of the ambient standard
[57 FR 13508].
4.3 Pre-enactment Banked Emissions
Reduction Credits. If the State has an
emissions credit bank that meets the EPA’s
requirements under an earlier policy
statement [56], the State is allowed to use its
pre-enactment banked emissions reduction
credits to facilitate the location of new
sources in nonattainment areas during the
1990–1996 period. However, because these
reduction credits represent emissions that are
not included in the 1990 base year inventory,
any additional emissions that result from the
use of banked credits must be treated as
growth in order to ensure that the 15 percent
55 Guidance on the Adjusted Base Year Emissions
Inventory and the 1996 Target for the 15 Percent
Rate-of-Progress Plans. Ozone/Carbon Monoxide
Programs Branch, U.S. Environmental Protection
Agency, Office of Air Quality Planning and
Standards, Research Triangle Park, NC 27711. EPA–
452/R–92–005. October 1992.
56 51 FR 233 ‘‘Emissions Trading Policy
Statement; General Principles for Creation, Banking
and Use of Emission Reduction Credits; Final
Policy Statement and Technical Issues Document.’’
December 4, 1986. This document has been
replaced by Improving Air Quality with Economic
Incentive Programs, January 2001, available at
https://www.epa.gov/region07/programs/artd/air/
policy/search.htm.
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VOC emissions reduction requirement is
achieved. Also, it is important to note that
the use of pre-enactment banked emissions
credits must be in accordance with the offset
ratios prescribed in the CAA Amendments
(e.g., 1.3 to 1 in severe areas.)
The 1992 guidance document
provides an example calculation of the
above guidance.
b. Interpretation for 8-Hour Ozone
NAAQS
The guidance provided above is still
relevant for banked emission reduction
credits in relation to the RFP
requirement for the 8-hour ozone
standard. However, because the rule for
implementing the 8-hour ozone
standard uses a 2002 baseline year, the
above guidance should be read—for
purposes of implementing the 8-hour
ozone RFP requirement—by substituting
‘‘pre-enactment banked emission
credits’’ with ‘‘pre-2002 banked
emission credits.’’ A pre-2002 banked
emission credit is one that was
generated before January 1, 2002 and
that is certified in a bank that EPA has
approved for such purposes. For a
discussion of the use of shutdown/
curtailment credits for offsets and
netting, see section V.B.1.a of this
preamble. For a discussion of the use of
emission reduction credits for offsets
and netting, see section V.D.5 of this
preamble.
F. Are contingency measures required in
the event of failure to meet a milestone
or attain the 8-hour ozone NAAQS?
[Section VI.J. of June 2, 2003 proposed
rule (68 FR 32837); no draft or final
regulatory text.]
1. Background
Under the CAA, 8-hour ozone
nonattainment areas subject only to
subpart 1, as well as those classified
under subpart 2 as moderate, serious,
severe, and extreme must include in
their SIPs contingency measures
consistent with sections 172(c)(9) and
182(c)(9), as applicable. Contingency
measures are additional controls to be
implemented in the event the area fails
to meet a RFP milestone or fails to attain
by its attainment date. These
contingency measures must be fully
adopted rules or measures which are
ready for implementation quickly upon
failure to meet milestones or attainment.
For additional background
information, see the Proposal (68 FR
32802, June 2, 2003). Other related
information can be found in the
following applicable guidance
documents:
• ‘‘Contingency Measures for Ozone
and Carbon Monoxide (CO)
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Redesignations,’’ Memorandum from
G.T. Helms, Chief, Ozone/Carbon
Monoxide Programs Branch, June 1,
1992,
• ‘‘Procedures for Processing
Requests to Redesignate Areas to
Attainment,’’ Memorandum from John
Calcagni, Director, Air Quality
Management Division, September 4,
1992,
• ‘‘Guidance for Growth Factor,
Projections, and Control Strategies for
the 15 percent Rate-of-Progress Plans,’’
(EPA–452/R–93–002), March 1993,
• ‘‘Early Implementation of
Contingency Measures for Ozone and
Carbon Monoxide (CO) Nonattainment
Areas,’’ Memorandum from G.T. Helms,
Chief, Ozone/Carbon Monoxide
Programs Branch, August 13, 1993,
• ‘‘Guidance on Issues Related to the
15 Percent Rate-of-Progress Plans,’’
Memorandum from Michael H. Shapiro,
Acting Assistant Administrator for Air
and Radiation to the Regional Division
Directors, August 23, 1993,
• ‘‘Clarification of Issues Regarding
the Contingency Measures that are due
on November 15, 1993 for Moderate and
Above Ozone Nonattainment Areas,’’
Memorandum from D. Kent Berry,
Acting Director, Air Quality
Management Division, November 8,
1993, and
• ‘‘Guidance on the Post 1996 Rate-ofProgress Plan (ROP) and Attainment
Demonstration,’’ (EPA–452/R–93–015),
January 1994.
2. Summary of Final Rule
We are adopting the approach taken
in our proposal. All subpart 1 and
subpart 2 areas other than marginal
areas are required to adopt contingency
measures to be implemented in the
event of failure to meet a RFP milestone
or to attain the 8-hour ozone NAAQS.
The contingency measures SIP should
accompany the attainment
demonstration SIP required for
submission by June 15, 2007.
It should be noted that the CAA
requires States to identify contingency
measures that will go into effect without
further action on the part of the State or
EPA. We believe this language means
that contingency measures should be
adopted regulations but also recognize
that some additional State or local
action may be necessary (such as
notification of sources) before
implementation.
Under subpart 2, areas that are
nonattainment for the 8-hour ozone
NAAQS that have unused adopted
contingency measures for the 1-hour
ozone NAAQS may use those measures
as appropriate as contingency measures
for the 8-hour NAAQS.
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For subpart 1 areas, States should
follow EPA’s existing guidance for
subpart 2 areas. We intend to provide
additional guidance only if needed.
3. Comments and Responses
Comment: Two commenters raised
concerns about the difficulty some areas
may have in identifying what they
referred to as ‘‘reserve’’ or ‘‘unused’’
measures for the 1-hour standard that
could be used as contingency measures
for the 8-hour standard for subpart 2
areas. These commenters requested
protection for areas that have no
‘‘leftover’’ measures to be used in the
event of failure to meet the milestone.
The commenters contended that EPA
needs to have policies that do not
penalize areas that have implemented
all feasible measures to attain the
standard and may not have any
identified contingency measures left.
Response: The commenters appear to
be asking EPA to drop the requirement
for a nonattainment area SIP to contain
contingency measures. The commenters
have not provided a legal rationale why
they believe it is possible to do this. The
purpose of contingency measures is to
have a quickly implementable backup
plan of action should primary measures
fail to bring a nonattaining area to the
requisite level (be it attainment of the
NAAQS or meeting a RFP milestone). It
is up to each State to determine what
measures the State will commit to
implement should failure occur. We
note that States may rely on regional
and national control measures as well as
local control measures to meet the
contingency measure obligation.
A list of example contingency
measures has been provided. See
section 9.5 of ‘‘Guidance for Growth
Factor, Projections, and Control
Strategies for the 15 percent Rate-ofProgress Plans,’’ (EPA–452/R–93–002),
March 1993. The States have the
responsibility of determining what
contingency measures are most
appropriate for their area(s). To allow
nonattaining areas with seemingly few
potential contingency measures to opt
out of the contingency measure
requirement is counter to the
contingency measure provision in the
CAA. The EPA does not see any way to
interpret the clear language of the
statute other than as requiring
contingency measures in all
nonattainment areas other than marginal
subpart 2 areas. It should also be noted
that the CAA’s requirement for an area’s
SIP to demonstrate attainment by the
attainment date is not limited to the
adoption only of those measures that are
‘‘feasible.’’
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Comment: One commenter alleged
EPA’s proposal to allow Federal
measures that result in additional
emissions reductions beyond RFP or
attainment to qualify as contingency
measures is legally invalid. The
commenter further stated that
contingency measures must consist of
control requirements that will be taken
off the shelf and undertaken if and
when a RFP or attainment failure
occurs. In other words, contingency
measures must be new measures not
Federal or local measures that already
exist.
Response: The CAA states that
contingency measures are to be
‘‘specific measures to be undertaken if
the area fails to make reasonable further
progress, or to attain * * * by the
attainment date.’’ The April 16, 1992
General Preamble provided the
following guidance: ‘‘States must show
that their contingency measures can be
implemented with minimal further
action on their part and with no
additional rulemaking actions such as
public hearings or legislative review. In
general, EPA will expect all actions
needed to affect full implementation of
the measures to occur within 60 days
after EPA notifies the State of its
failure.’’ (57 FR 13512). This could
include Federal measures and local
measures already scheduled for
implementation.
The EPA has approved numerous SIPs
under this interpretation—i.e., that use
as contingency measures one or more
Federal or local measures that are in
place and provide reductions that are in
excess to the attainment demonstration
or RFP plan. (62 FR 15844, April 3,
1997; 62 FR 66279, December 18, 1997;
66 FR 30811, June 8, 2001; 66 FR 586
and 66 FR 634, January 3, 2001.) The
key is that the statute requires extra
reductions that are not relied on for RFP
or attainment and that are in the
demonstration to provide a cushion
while the plan is revised to meet the
missed milestone. In other words,
contingency measures are intended to
achieve reductions over and beyond
those relied on in the attainment and
RFP demonstrations. Nothing in the
statute precludes a State from
implementing such measures before
they are triggered. In fact, a recent court
ruling upheld contingency measures
that were previously required and
implemented where they were in excess
of the attainment demonstration and
RFP SIP. See LEAN v. EPA, 382 F. 3d
575 5th Circuit, 2004.
Comment: One commenter supported
EPA’s proposal to continue to observe
existing policies regarding contingency
measures for areas covered under
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subpart 2 for the 8-hour standard.
Additionally, the commenter
anticipated that EPA’s additional
guidance on the contingency measure
requirement for subpart 1 will be
patterned after the subpart 2
requirement.
Response: The EPA acknowledges the
commenter’s support of our proposal
that subpart 2 8-hour ozone
nonattainment areas may rely on our
existing contingency measure guidance.
As provided above, both subpart 1 and
subpart 2 areas should rely on that
guidance for purposes of adopting
contingency measures.
G. What requirements should apply for
RACM and RACT for 8-hour ozone
nonattainment areas?
[Section VI.K. of June 2, 2003
proposed rule (68 FR 32837); § 51.912 in
draft and final regulatory text.]
The first subsection of this section
covers RACT and the second subsection
covers RACM.
1. Reasonably Available Control
Technology (RACT)
a. Background
As described in more detail in the
June 2 proposal, subpart 1 of part D
includes a requirement that an
attainment plan provide for the
implementation of all RACM as
expeditiously as practicable, including
such reductions that may be obtained
through RACT. Under subpart 2,
marginal areas are required to correct
pre-1990 RACT requirements and new
RACT requirements are specified for
moderate and above ozone
nonattainment areas. Additionally,
States must adopt RACT for all areas in
an OTR. The RACT requirement applies
to both ozone precursors—NOX and
VOC. Since 1990, we have issued
guidance documents on the RACT
requirements in subpart 2. Prior to
enactment of the CAA Amendments of
1990, EPA also issued detailed guidance
documents on RACT for ozone
nonattainment area SIPs.57
Section 183(c) of the CAA requires
EPA to ‘‘revise and update such
documents [i.e., Control Techniques
Guidelines and Alternative Control
Techniques] as the Administrator
determines necessary.’’ As new or
updated information becomes available
States should consider the new
information in their RACT
determinations. States should consider
57 The EPA defined RACT as the lowest emission
limitation that a particular source is capable of
meeting by the application of control technology
that is reasonably available considering
technological and economic feasibility (44 FR
53762; September 17, 1979).
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the new information in any RACT
determinations or certifications that
have not been issued by the State as of
the time such an update becomes
available.58
The June 2, 2003 proposal addressed
several aspects of the RACT
requirement. For subpart 1 areas, we
proposed several options. We proposed
in one option to interpret the CAA in a
manner similar to that under subpart 2
by requiring areas covered under
subpart 1 to face different RACT
requirements based on the magnitude of
the ozone problem in the area (i.e., the
area’s design value). In another option,
we proposed that RACT would be met
if the area were able to demonstrate
attainment of the standard as
expeditiously as practicable with
emission control measures in the SIP.
We also proposed as an early attainment
incentive that RACT would be met in an
area which demonstrates attainment
within 3 years and submits the
demonstration within 1 year. We
proposed the RACT submittal dates for
subpart 1 areas would be within 2 years
after designation.
For subpart 2 areas, we proposed to
apply RACT as specified in subpart 2.
We proposed (in the draft regulatory
text) to require that States submit their
subpart 2 RACT SIPs within 2 years
after the nonattainment designation. In
addition, we proposed the date for
affected sources to implement RACT in
subpart 2 areas would be 30 months
after the required submittal date. We
also proposed that States may use
current EPA guidance in making RACT
determinations; consequently, in some
cases, sources previously evaluated
under the 1-hour ozone RACT
requirement and sources subject to the
NOX SIP Call cap-and-trade program
could be determined to meet the 8-hour
ozone RACT requirement.
58 In addition, EPA is considering related
recommendations from the Air Quality
Management Work Group to the Clean Air Act
Advisory Committee (CAAAC) dated January 2005
[available at: https://www.epa.gov/air/caaac/
aqm.html#library] in response to the recent
National Research Council report on Air Quality
Management in the United States (January 2004)
[available for sale; individual pages available for
viewing at https://www.nap.edu/books/0309089328/
html]. One of the recommendations to the CAAAC
is that ‘‘for the SIPs States are required to submit
over the next several years, EPA and States, locals,
and Tribes should promote the consideration of
multipollutant impacts, including the impacts of air
toxics, and where there is discretion, select
regulatory approaches that maximize benefits from
controlling key air toxics, as well as ozone, PM2.5
and regional haze.’’ As part of this effort, EPA
intends in the future to develop updated technology
guidance with respect to source categories emitting
multiple pollutants in large amounts. At this time,
however, we think it is unlikely that updated
technology guidance will be available in time for
the RACT SIPs due in 2006.
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b. Summary of Final Rule
For subpart 1 areas that do not request
an attainment date extension (i.e., an
attainment date beyond 5 years after
designation), RACT will be met with
control requirements sufficient to
demonstrate that the NAAQS is attained
as expeditiously as practicable. The
RACT submittal date for these areas is
the same as the submittal date for the
attainment plan. This submission date is
no later than 3 years after designation.
For subpart 1 areas that request an
attainment date extension (i.e., an
attainment date beyond 5 years after
designation), the State shall submit the
RACT SIP with its attainment date
extension request.59 For subpart 2
moderate and above areas, and areas
within an OTR, RACT is required with
the RACT submittal and is due 27
months after designation. States must
require sources to implement RACT no
later than the first ozone season or
portion thereof which occurs 30 months
after the required submittal date.
Where a RACT SIP submission
(separate from the attainment
demonstration) is required (except
certain subpart 1 areas, as described two
paragraphs prior to this, and except
certain sources subject to the NOX SIP
Call or CAIR, as described below), State
SIPs implementing the 8-hour standard
must assure that RACT is met, either
through a certification that previously
required RACT controls represent RACT
for 8-hour implementation purposes or
through a new RACT determination.
States may use existing EPA guidance in
making RACT determinations. Where a
State has adopted and EPA has
approved a control measure as RACT for
a specific major stationary source or
source category for the 1-hour ozone
NAAQS, and absent data indicating that
the previous RACT determination is no
longer appropriate, the State may
submit a certification that the source is
subject to a SIP-approved RACT
requirement. Such certification shall be
accompanied by appropriate supporting
information, such as consideration of
information received from public
commenters.
For purposes of meeting the NOX
RACT requirement, the State need not
perform (or submit) a NOX RACT
analysis for sources subject to the state’s
emission cap-and-trade program where
the cap-and-trade program has been
adopted by the State that meets the NOX
SIP Call requirements or, in States
achieving CAIR reductions solely from
EGUs, the CAIR NOX requirements. The
EPA believes that the SIP provisions for
59 This is generally expected with the submission
of the attainment demonstration.
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those sources meet the ozone NOX
RACT requirement. A State that is
relying on this conclusion for the
affected sources should document this
reliance in its RACT SIP.
Additionally, RACT is considered met
for cement kilns and stationary internal
combustion engines that are subject to a
SIP approved as meeting the NOX SIP
Call obligation to install and operate
controls that are expected to achieve at
least a 30 percent and 82 percent
reduction, respectively, from
uncontrolled levels. A State that is
relying on this conclusion for the
affected sources should document this
reliance in its RACT SIP.
A State may meet the NOX RACT
requirement by showing that the
weighted average emission rate from a
broad range of sources in the
nonattainment area subject to RACT
meet RACT requirements.
At their discretion, States are free to
conduct a case-by-case RACT
determination for any source—or RACT
determinations or certifications for
groups of sources.
As discussed below in greater detail,
States may use information gathered
from prior BACT or LAER analyses, to
the extent it remains valid, to help
complete a RACT determination.
Similarly, emissions standards
developed under 111(d) and NSR/PSD
settlement agreements may be
considered. This will allow States, in a
number of cases, to rely on these prior
determinations for purposes of showing
that a source is meeting RACT
requirements.
For VOC sources subject to MACT
standards, States may streamline their
RACT analysis by including a
discussion of the MACT controls and
considerations relevant to VOC RACT.
We believe that this will allow States, in
many cases, to rely on the MACT
standards for purposes of showing that
a source has met VOC RACT.
Consistent with the proposed
regulatory text for this rule [section
51.912(b)(1)], the final rule provides
that, for purposes of meeting the RACT
obligations under section 182(b)(2)(C) of
the CAA for major stationary sources of
VOCs and under section 182(f) of the
CAA for major stationary sources of
NOX, the definition of major stationary
source in section 302 of the CAA, as
modified by the major source definition
in either section 182(b), (c), (d) or (e) of
the CAA as applicable to the area’s
classification, applies.
Although we drafted more extensive
regulatory language for several aspects
of the RACT program in the proposal,
we believe it is sufficient to describe
EPA’s views on the details of the RACT
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program in today’s preamble and in
other guidance [e.g., the NOX
Supplement to the General Preamble,
November 25, 1992 (57 FR 55620)].
Thus, some detailed portions of the
proposed regulatory text regarding
RACT were not retained in the final rule
(in particular paragraph (b)(2) ‘‘Prior
RACT Determinations’’).
c. Comments and Responses
Comments: For subpart 2 ozone
nonattainment areas, several States
expressed agreement with the proposed
approach for implementing RACT
consistent with section 182 of the CAA.
Response: The EPA agrees with these
comments.
Comments: For subpart 1 ozone
nonattainment areas, EPA received
several comments for and against the
options proposed for addressing RACT.
Several State and industry
commenters supported EPA’s proposed
approach that RACT would be met if the
area is able to demonstrate attainment of
the standard as expeditiously as
practicable with emission control
measures in the SIP. The reasons
provided by these commenters were
generally as follows: States should be
able to use their discretion in
determining which control strategies are
the most effective in addressing a
particular area’s air quality problem;
flexibility is needed as areas differ in
sensitivity to NOX and VOC reductions;
EPA’s regional modeling shows these
requirements are unnecessary in many
areas; and many of these areas violate
the ozone standard primarily or entirely
due to transport.
The EPA also received comments,
primarily from several States and
environmental groups, opposing the
approach that RACT would be met by
control measures that are part of a SIP
demonstrating attainment of the
standard as expeditiously as practicable.
These commenters made the following
points: since section 172(c)(1) of the
CAA explicitly mandates RACT ‘‘at a
minimum’’ in all nonattainment areas,
Congress plainly intended to require
RACT as a floor level of control
technology in addition to any measures
needed to demonstrate timely
attainment; even where RACT does not
advance attainment, it is needed in
order to reduce the severity and number
of violations; under this approach, the
statutory RACT provisions add nothing
to the statutory attainment mandate—
which violates basic canons of statutory
interpretation; RACT in nonattainment
areas will substantially reduce transport
of ozone and ozone precursors; for
equity reasons, sources in similar areas
should be subject to the same control;
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71653
and RACT is a useful tool that should
not be abandoned through flexibility
mechanisms.
Response: The general RACT
provision under subpart 1 in the statute,
is found in section 172(c)(1). It is a
portion of the RACM provision found in
that same section. Our long-standing
interpretation of the RACM provision is
that areas need only submit such RACM
as will contribute to timely attainment
and meet RFP, and that measures which
might be available but would not
advance attainment or contribute to RFP
need not be considered RACM. This
interpretation has been upheld in
several recent court cases. See Sierra
Club v. EPA, 294 F.39 155, 162 (D.C.
Circuit, 2002) (concerning the
Metropolitan Washington, D.C.,
attainment demonstration) and Sierra
Club v. EPA, No. 01–60537 (5th Circuit,
2002) (concerning the Beaumont
attainment demonstration). Since
subpart 1 RACT is a portion of RACM,
these cases also support a conclusion
that, where we are dealing only with
section 172 RACT, it is reasonable to
require only such RACT as will meet
RFP and advance attainment. In view of
these court cases, EPA disagrees with
the comments listed above opposing the
approach that, in subpart 1 areas, RACT
would be met by control measures in a
SIP demonstrating attainment of the
standard as expeditiously as practicable
and meeting RFP.
The EPA generally agrees with
comments that States should have
flexibility to determine which control
strategies are the most effective in
reaching attainment as expeditiously as
practicable and providing for RFP, and
the CAA gives primary authority to
States and local governments to select
the mix of controls necessary to meet
the NAAQS. In addition, EPA believes
that section 172(c) is not the appropriate
section of the CAA to address the
transport of ozone and ozone
precursors; EPA has conducted and is
conducting rulemaking pursuant to
sections 110 and 126 for that purpose.
Finally, some commenters suggested,
for equity reasons, that sources in
similar areas should be subject to the
same control. In the proposal, EPA
suggested subpart 1 and 2 areas with the
8-hour ozone design values above 91
ppb should be subject to VOC and NOX
RACT requirements. The EPA also
proposed that RACT would be met in an
area which demonstrates attainment
within 3 years and submits the
demonstration within 1 year. In the final
rule, EPA has addressed equity concerns
by taking portions of these two
proposals, such that subpart 1 and
subpart 2 areas with attainment
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deadlines longer than 5 years after
designation must meet the same RACT
requirements. We believe longer than 5
years is more appropriate than the 3
years proposed for this requirement
since this approximates the maximum
attainment date for subpart 2 (moderate)
areas subject to RACT and since this
approach is consistent with the manner
in which ROP/RFP requirements are
treated in the final rule.
Therefore, in subpart 1 areas that do
not request an extension beyond the
initial 5 years after designation, the final
rule indicates that RACT would be met
by the emission control measures in a
SIP that demonstrates attainment of the
standard as expeditiously as practicable
and meets RFP. In addition, the final
rule requires subpart 1 areas with
maximum attainment deadlines longer
than 5 years after designation to meet
the same RACT requirements as subpart
2 areas. This approach minimizes the
RACT inequity with subpart 2 areas and
provides flexibility for subpart 1 areas
demonstrating attainment within 5
years.
Comment: One commenter believes
that new marginal nonattainment areas
should be subject to RACT under the 8hour standard just as they would have
been subject to RACT immediately prior
to the CAA Amendments of 1990.
Response: Section 182(a) provides
that marginal and higher classified areas
for the 1-hour standard with pre-1990
RACT obligations had to submit
corrections to their RACT rules within
6 months after classification under the
1990 CAA Amendments. To the extent
that any 8-hour ozone nonattainment
areas did have this obligation, they
already met it. See footnote 60 in the
June 2, 2003 proposal. The CAA does
not require RACT for marginal areas
other than the obligation to ‘‘correct’’
pre-1990 RACT requirements.
Comment: The EPA received several
comments for and against the proposal
that States may use a prior RACT
determination with respect to the 1-hour
ozone standard for purposes of meeting
the RACT requirements for the 8-hour
ozone standard. Further, EPA received
comments on the proposal that a new
RACT determination is required in cases
where the initial RACT analysis under
the 1-hour standard for a specific source
or source category concluded that no
additional controls were necessary.
Several State and industry
commenters supported EPA’s proposed
approach that a prior RACT analysis
under the 1-hour ozone standard should
meet RACT requirements under the 8hour standard where major sources or
source categories were previously
reviewed and controls applied to meet
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RACT. These commenters stated that
RACT is not specific to any particular
ozone standard, such that once a source
has met RACT, it has met RACT,
whether or not the ozone standard is
revised to become more (or less)
stringent; just as with the 15 percent
VOC requirement, the statute provides
no basis for duplicative imposition of
RACT; and there is no basis in the
statute to read in a new requirement for
RACT. In addition, some industry
commenters stated that EGUs which
meet title IV NOX control requirements
would also meet the NOX RACT
requirement.
The EPA also received comments
from several States opposing EPA’s
proposed approach. These commenters
believe the NOX and VOC guidance is
too old, needs updating and, in the case
of NOX controls, the improvement over
the last 3 years has been dramatic with
controls previously considered to be
BACT (and therefore generally
considered at the time to be more
stringent than RACT) are now
considered to be merely RACT. In
addition, one State suggested the
presumptive RACT level should be
revised to at least 85 percent control or
that NOX RACT should be defined as up
to $10,000/ton of pollutant removed.
Two States disagreed with EPA’s
proposal that a new RACT
determination should be required in
cases where the initial RACT analysis
under the 1-hour NAAQS found that no
additional controls were necessary for a
specific source or source category. They
indicated such re-analysis would be an
unwise use of resources because it
would not yield significant benefits.
Further, they do not agree that a RACT
determination is warranted for major
VOC or NOX sources not in existence
during the previous RACT
determination, because new sources in
1-hour nonattainment areas have been
permitted pursuant to the requirements
for NSR and, where applicable, have
already been subject to more stringent
control requirements.
Several State and industry
commenters recommended that RACT
requirements apply for major sources in
any portion of the 8-hour nonattainment
area not subject to a RACT program for
the 1-hour standard.
Response: In 1992, EPA set
presumptive NOX RACT for boilers as
combustion modification, consistent
with title IV acid rain requirements. For
all other NOX stationary source
categories, EPA guidance in 1994
indicated States should consider in their
RACT determinations technologies that
achieve 30–50 percent reduction within
a cost range of $160–1300 per ton of
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NOX removed. In the NOX SIP Call Rule,
we reviewed all major NOX source
categories and stated in the final rule
that the NOX SIP Call controls, at less
than $2,000/ton, represent reductions
beyond those required by RACT. The
suggestion of one State that EPA’s RACT
guidance should be revised to reflect 85
percent control and $10,000/ton of
pollutant removed is inconsistent with
EPA’s previous conclusions regarding
what level of control represents RACT
and because the comment lacked
supporting documentation that the
suggested values represent feasible
control levels for the many source
categories affected by the RACT
program.
Many areas subject to the major
source RACT requirement under the 8hour ozone standard have previously
addressed the RACT requirement with
respect to the 1-hour ozone standard.
For example, major sources located in
States of the Ozone Transport
Commission were subject to the NOX
RACT requirement in the mid-1990s.
We believe that, in many cases, a new
RACT determination under the 8-hour
standard would result in the same or
similar control technology as the initial
RACT determination under the 1-hour
standard because the fundamental
control techniques, as described in the
CTGs and ACTs, are still applicable. In
cases where controls were applied due
to the 1-hour ozone RACT requirement,
we expect the incremental emissions
reductions from application of a second
round of controls would be small and,
therefore, the cost for advancing that
small additional increment of reduction
would not be reasonable. In such cases,
EPA believes the cost per ton of NOX
removed associated with installing a
second round of RACT controls (and
perhaps the removal of initial RACT
controls) is likely to be beyond the costs
assumed in our current guidance noted
above ($160–$1300/ton). In contrast, a
RACT analysis for uncontrolled sources
would be much more likely to find that
RACT level controls are economically
and technically feasible.
The CTGs and ACTs for VOC were
completed over a period from the late
1970s to mid-1990s and have not been
updated. The CTGs are still used to
presumptively define VOC RACT. The
EPA issued NOX ACT documents
between 1992 and 1995. In September
2000, updates to the NOX ACT
documents were completed for
stationary internal combustion engines
and cement kilns. The NOX and VOC
ACTs describe available control
techniques and their cost effectiveness,
but do not define presumptive RACT
levels as the CTGs do. Updating the
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ACTs would not, by itself, change EPA’s
NOX or VOC RACT guidance, but it
could provide information that would
lead to a new conclusion as to which
control measures constitute RACT for a
specific source or source category. Since
RACT can change over time as new
technology becomes available or the
cost of existing technology decreases,
EPA does not agree with comments that
once a source has met RACT, it has met
RACT whether or not the ozone
standard is revised.
We agree that progress has been made
in improving the cost effectiveness of
some NOX and VOC controls. States and
other interested parties should consider
available information that may
supplement the CTG and ACT
documents. In cases where additional
information is presented, for example,
as part of notice-and-comment
rulemaking on a RACT SIP submittal,
States (and EPA) would necessarily
consider the additional data in
reviewing what control obligation is
consistent with RACT. Similarly, we
encourage States to use the latest
information available in making RACT
determinations, whether that
information is in CTGs, ACTs, or
elsewhere.
The EPA agrees that it is more
efficient for EPA to broadly assess what
is RACT for a specific source category
than for States to conduct source-bysource RACT determinations, especially
considering that States need to initiate
RACT programs in the near future (as
discussed in a separate comment/
response). The EPA’s current RACT
guidance may be used for purposes of
the 8-hour standard. At the same time,
we agree with comments that many of
the CTGs/ACTs have not been revised
since issued and thus may not provide
the most accurate picture of current
control options. Therefore, we believe
States must consider new information
that has become available and certify
that a 1-hour ozone RACT
determination, even where controls
were required, still represents an
appropriate RACT level of control for
the 8-hour ozone program. In the
alternative, the State should revise the
SIP to reflect a modified RACT
requirement for specific sources or
source categories.
In summary, we believe the current
NOX and VOC RACT guidance,
including CTGs and ACTs, may
continue to be used by States in making
RACT determinations with respect to
the 8-hour ozone standard. States
should ensure that their SIPs accurately
reflect RACT based on the current
availability of technically and
economically feasible controls.
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Therefore, in portions of 8-hour ozone
nonattainment areas where major
sources or source categories were
previously reviewed and controls
applied to meet the RACT requirement
under the 1-hour standard, States
should review and, if appropriate,
accept the initial RACT analysis as
meeting the RACT requirements for the
8-hour standard. Absent data indicating
that the previous RACT determination is
no longer appropriate, the State need
not submit in its SIP a new RACT
requirement for these sources. In such
cases, the State should submit a
certification as part of its SIP revision,
with appropriate supporting
information, such as consideration of
new data, that these sources are already
subject to SIP-approved requirements
that still meet the RACT obligation.
There are cases where the initial RACT
analysis under the 1-hour standard for
a specific source or source category
concluded that no additional controls
were necessary. In such cases, a new
RACT determination is needed to
consider whether more cost-effective
control measures have become available
for sources that were not previously
regulated. A re-analysis may determine
that controls are now economically and
technically feasible and should be
required to meet RACT. Furthermore, in
this situation, we expect the
incremental emissions reductions to be
significant, compared to the
uncontrolled emissions levels. Thus, the
cost per ton of emissions controlled is
more likely to make controls
‘‘reasonably available’’ than where a
source had already installed controls to
meet RACT for the 1-hour standard. In
all cases where additional information
is presented as part of notice-andcomment rulemaking, including a RACT
SIP submittal for sources previously
controlled, States (and EPA) must
consider the additional information as
part of that rulemaking.
We agree with several State and
industry comments that RACT
requirements apply for major sources in
any portion of the 8-hour nonattainment
area not subject to a RACT program for
the 1-hour standard.
Some commenters objected to EPA’s
proposal that any major VOC or NOX
source that did not exist during a
previous RACT determination must be
subject to a RACT determination as part
of the SIP for the 8-hour ozone standard.
These commenters stated that the BACT
or LAER provisions would assure at
least RACT level controls on such
sources. We agree this should be true in
many cases, but not all. The BACT/
LAER analyses do not automatically
ensure compliance with RACT since the
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regulated pollutant or source
applicability may differ and the
analyses may be conducted many years
apart. States may, however, rely on
information gathered from prior BACT
or LAER analyses for the purposes of
showing that a source has met RACT to
the extent the information remains
valid. We believe that the same logic
holds true for emissions standards for
municipal waste incinerators under
CAA section 111(d) and NSR/PSD
settlement agreements. Where the State
is relying on these standards to
represent a RACT level of control, the
State should present their analysis with
their determination during the SIP
adoption process.
For VOC sources subject to MACT
standards, States may streamline their
RACT analysis by including a
discussion of the MACT controls and
relevant factors such as whether VOCs
are well controlled under the relevant
MACT air toxics standard, which units
at the facility have MACT controls, and
whether any major new developments
in technologies or costs have occurred
subsequent to the MACT standards. We
believe that there are many VOC sources
that are well controlled (e.g., through
add-on controls or through substitution
of non-VOC non-HAP materials for VOC
HAP materials) because they are
regulated by the MACT standards,
which EPA developed under CAA
section 112. Any source subject to
MACT standards must meet a level that
is as stringent as the best-controlled 12
percent of sources in the industry.
Examples of these HAP sources that
may effectively control VOC emissions
include organic chemical plants subject
to the hazardous organic NESHAP
(HON), pharmaceutical production
facilities, and petroleum refineries.60
We believe that, in many cases, it will
be unlikely that States will identify
emission controls more stringent than
the MACT standards that are not
prohibitively expensive and are thus
unreasonable. We believe this will allow
States, in many cases, to rely on the
MACT standards for purposes of
showing that a source has met VOC
RACT.
Comments: Some commenters
pointed out that many companies have
employed averaging programs for NOX
SIP Call compliance and want this
option preserved under the 8-hour
ozone standard since requiring sources
60 However, there are some MACT categories for
which it may not be possible to determine the
degree of VOC reductions from the MACT standard
without additional analysis; for example, the
miscellaneous metal parts and products (40 CFR
part 60, subpart MMMM) due to the uncertainty of
the compliance method that will be selected.
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to individually meet NOX RACT
requirements would greatly increase the
costs of compliance at sources already
subject to the NOX cap-and-trade
program without achieving greater
emissions reductions.
Response: In some cases, a facility or
a group of sources in a nonattainment
area might choose to meet NOX RACT
by adopting an emissions averaging
concept within the area; e.g., overcontrolling one or more large units and
not controlling other units. We agree
with comments that emission averaging
and cap-and-trade programs such as the
NOX SIP Call Rule achieve emissions
reductions at lower costs. The EPA’s
NOX RACT guidance, published on
November 25, 1992 (57 FR 55625), was,
in part, for the purpose of ‘‘enhancing
the ability of States to adopt marketbased trading systems for NOX’’ and to
encourage States to ‘‘structure their
RACT requirements to inherently
incorporate an emissions averaging
concept (i.e., installing more stringent
controls on some units in exchange for
lesser control on others).’’ EPA believes
that such cap-and-trade programs are
beneficial ways to achieve the greatest
overall reductions in the most costeffective manner. Consistent with
previous guidance,61 EPA continues to
believe that RACT can be met on
average by a group of sources within a
nonattainment area rather than at each
individual source. Therefore, states can
show that SIP provisions for these
sources meet the ozone RACT
requirement using the averaging
approach.
Finally, EPA believes that sources
complying with the NOX SIP call
trading system meet their RACT
obligation, for reasons explained later in
this section.
Comments: Several State and industry
commenters supported EPA’s proposed
approach concerning RACT and the
NOX SIP Call. These commenters stated
that the level of emissions reductions
required by the NOX SIP Call is far
greater than the level of reductions
achieved by controls that have been
determined to be NOX RACT. One State
encouraged EPA to provide this
approach to other areas subject to
approved cap-and-trade programs in
addition to those areas affected by the
NOX SIP Call.
61 The EPA’s NO RACT guidance (NO General
X
X
Preamble at 57 FR 55625) encourages States to
develop RACT programs that are based on
‘‘areawide average emission rates.’’ Thus, EPA’s
existing policy provides for States to submit a
demonstration as part of their RACT submittal
showing that the weighted average emission rate
from sources in the nonattainment area subject to
RACT meet RACT requirements.
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The EPA also received comments,
primarily from several States and
environmental groups, opposing the
approach. These commenters stated that
there are no exceptions to the RACT
mandates in either subpart 1 or subpart
2 for sources subject to NOX SIP Call
cap-and-trade programs, and EPA is
without authority to invent such an
exception. Because the NOX SIP Call’s
cap-and-trade program does not require
emission control technologies to be
installed at a particular source, some
commenters conclude that RACT
requirements are necessary and
appropriate to ensure that all sources
implement at least a minimum level of
control. One State indicated there have
been numerous cases where sources
subject to the NOX SIP Call have not had
to install controls comparable to RACT.
Commenters also suggested that RACT
is intended to be a benchmark for
control technology at individual
stationary sources, not a level of
regional reductions. In addition, some
commenters noted that the NOX SIP Call
requirements are specific to the ozone
season, where RACT requirements are
year-round. Consequently, these
commenters recommended that EPA
should also consider non-ozone related
nitrogen issues, including fine particles,
visibility, nitrification and acidification
of watersheds and eutrophication of
coastal waters all of which would be
reduced with year-round controls.
Response: In 2009, when sources in
areas designated nonattainment for the
8-hour standard in June 2004 must
comply with RACT, the NOX SIP call
trading program is subsumed by the
CAIR trading program. As described
below, EPA believes that sources meet
ozone NOX RACT requirements if they
comply with the NOX SIP Call trading
program or, in States where all CAIR
reductions are achieved by EGUs, rules
implementing CAIR. Accordingly, a
State need not perform a NOX RACT
analysis for non-EGU sources that after
2008 continue to be subject to a SIP that
regulates those non-EGU sources
equally or more stringently than the
State’s current rules meeting the NOX
SIP call. In a NOX SIP Call State that
ensures such reductions from nonEGUs, the State need not perform a NOX
RACT analysis for EGU sources if the
State retains a summer season EGU
budget under CAIR that is at least as
restrictive as the EGU budget that was
approved in the State’s NOX SIP call
SIP. In addition, the State need not
perform a NOX RACT analysis for EGUs
subject to a State cap-and-trade program
that meets CAIR and achieves CAIR
NOX reductions solely from EGUs. As
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noted above, the SIP should document
that the State is relying on EPA’s
conclusion in this preamble that these
levels of control meet RACT for the
covered sources.
The EPA believes the RACT mandate
in subpart 1 and subpart 2 applies in
specific geographic areas but does not
necessarily require every major source
to install controls. For example, as
discussed in a separate comment/
response, where we are dealing only
with subpart 1 RACT, we only require
such RACT as will advance attainment
or meet RFP. Thus, EPA does not agree
with commenters who conclude that
RACT requirements are necessary and
appropriate to ensure that all sources
implement at least a minimum level of
control or that RACT is intended to be
a benchmark for control technology at
all individual stationary sources.
Some commenters pointed out that
the NOX SIP Call requirements are
specific to the ozone season, yet RACT
requirements are year-round. Although
there are some exceptions, EPA agrees
that RACT usually is an application of
controls year-round; thus, there would
be non-ozone-related nitrogen benefits,
including fine particles, visibility,
nitrification and acidification of
watersheds and eutrophication of
coastal waters due to year-round
controls. While the commenters are
correct that the NOX SIP call reductions
must be achieved during the 5 months
of the ozone season critical for high
ozone concentrations for affected States,
we believe that the RACT requirement
will be satisfied for sources covered by
the NOX SIP Call. In addition to
operating advanced controls at least in
the ozone season, many sources have
installed combustion controls that
function all the time; emissions
reductions from these controls will
occur year round.
(i) NOX SIP Call: All States submitting
SIP revisions to meet the NOX SIP Call
(October 27, 1998; 63 FR 57356) elected
to require large boilers and turbines to
comply with an emissions cap-and-trade
program consistent with EPA’s model
cap-and-trade rule. As a result, the
covered sources are already subject to a
stringent control program.62 As
described in the June 2, 2003 proposal,
these sources collectively achieve more
emissions reductions within the SIP
62 The cost of purchasing allowances will often be
higher than the cost for achieving a RACT level of
control. In the 1998 NOX SIP Call Rule, average
costs of compliance were estimated at about $1500/
ton and average RACT level costs are less than
$1300/ton. Recent estimates of the projected cost of
allowances are about $2000–4000/ton (NOX Budget
Trading Program, 2003 Progress and Compliance
Report, August 2004, EPA–430-R–04–010).
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Call area than would be required by
application of RACT requirements to
each source in that area. At the time that
EPA promulgated the NOX SIP Call rule,
EPA estimated that in the NOX SIP Call
control case, EGUs would achieve a 64
percent reduction beyond the base case
requirements,63 and that the non-EGUs
subject to the States’ cap-and-trade
program would achieve a 60 percent
reduction from uncontrolled levels.64
These EGU and non-EGU reductions
were clearly beyond the 30–50 percent
expected from a RACT program.65 We
stated in the final NOX SIP Call rule that
the reductions achieved by that program
‘‘. . . represent reductions beyond those
required by Title IV or Title I RACT.’’
In addition, because the cap-and-trade
program covers units serving a 25
megawatt generator, it may achieve
emission reductions from many units
that are below the general NOX RACT
threshold of 100 tpy for sources in the
East.
EPA generally has the discretion to
determine whether a State submitted
rule is consistent with the RACT
requirements for a particular source in
the context of approving individual
RACT SIPs. The NOX SIP Call is
estimated to achieve a beyond-RACT
degree of control regionally, and sources
were required to install any controls
needed for compliance no later than
May 2004. Under these circumstances,
EPA believes that the NOX SIP call
constitutes RACT for those sources
covered by the NOX SIP Call, regardless
of the manner of compliance of
individual sources (e.g., control
equipment installation or purchase of
allowances from other sources). EPA is
making this finding now for all areas in
the NOX SIP call region, such that States
need not submit RACT analyses for
sources subject to the NOX SIP call that
are in compliance with a SIP approved
as meeting the NOX SIP call. A State
that is relying on this conclusion for
affected sources should document this
reliance in its RACT SIP.
Whether our judgment that non-EGU
sources subject to the NOX SIP Call
trading system meet RACT will
continue to apply in the future depends
upon how the State chooses to make the
63 The EPA’s 1992 NO RACT guidance provides
X
that the controls required under title IV of the CAA
are RACT controls and specifies emission rates
three times larger than the rates later used for coalfired units in the NOX SIP Call (0.45–0.50 lb/
mmBtu versus 0.15). Base case refers to the
situation absent NOX SIP call controls.
64 63 FR 57434–5.
65 Memorandum of March 16, 1994, from D. Kent
Berry re: ‘‘Cost-Effective Nitrogen Oxides (NOX)
Reasonably Available Control Technology (RACT).’’
U.S. Environmental Protection Agency, Research
Triangle Park, North Carolina.
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transition from the NOX SIP Call trading
system to the CAIR trading system. After
2008, EPA will no longer administer the
NOX SIP Call trading system and will
only administer the CAIR trading
system. A State subject to the NOX SIP
Call has three choices for the transition.
One, a State can bring its non-EGU
sources that are subject to the NOX SIP
Call trading program into the CAIR
trading program with the same
emissions budget allowed by the State’s
current NOX SIP Call rules. Two, a State
can adopt a SIP that regulates those nonEGU sources at least as stringently as
the State’s current NOX SIP Call rules,
but does not move those sources into
the CAIR trading program. Three, a State
can adopt a new SIP that meets its NOX
SIP Call responsibilities, in whole or in
part, by regulating sources other than
the non-EGU sources regulated by the
State’s current NOX SIP Call trading
program rules. We believe it is unlikely
that States will choose the third option,
given that its non-EGU sources already
would have complied with the NOX SIP
Call requirements. Under the first two
options, we believe that these non-EGU
sources would continue to satisfy
RACT. Under the third option, the State
would need to determine whether nonEGU sources that had participated in the
NOX SIP Call trading program continue
to meet RACT (either individually, or
through averaging among sources within
the nonattainment area).
Finally, as proposed, in cases where
States have adopted controls for cement
kilns consistent with the NOX SIP Call
(i.e., 30 percent reduction), the State
may choose to accept the NOX SIP Call
requirements as meeting the NOX RACT
requirements for the 8-hour standard
and need not perform a new NOX RACT
analysis for those sources. In its RACT
SIP submission, the State should
identify the cement plants that are
subject to NOX SIP Call controls and
that, therefore, are already subject to a
SIP-approved requirement consistent
with RACT. The EPA received
comments from States supporting the
proposal. Similarly, EPA believes a
State may choose to accept the Phase II
NOX SIP Call control level for stationary
internal combustion engines 66 as
meeting the NOX RACT requirements
and identify these obligations as RACT
level controls in its RACT SIP.
(ii) CAIR: The EPA has determined
that EGU sources complying with CAIR
requirements meet ozone NOX RACT
requirements in States where CAIR
reductions are achieved from EGUs
only.
As discussed more fully in the CAIR
final rulemaking, EPA has set the 2009
CAIR NOX cap at a level that, assuming
the reductions are achieved from EGUs,
would result in EGUs installing
emission controls on the maximum total
capacity on which it is feasible to install
emission controls by those dates. The
2015 NOX cap is specifically designed to
eliminate all NOX emissions from EGUs
that are highly cost effective to control
(the first cap represents an interim step
toward that end).67 In general, we
expect that the largest-emitting sources
will be the first to install NOX control
technology and that such control
technology will gradually be installed
on progressively smaller-emitting
sources until the ultimate cap is
reached.
We do not believe that requiring
source-specific RACT controls on EGUs
in nonattainment areas will reduce total
NOX emissions from sources covered by
CAIR below the levels that would be
achieved under CAIR alone.
Furthermore, we believe that sourcespecific RACT could result in more
costly emission reductions on a per ton
basis. If States chose to require smalleremitting sources in nonattainment areas
to meet source-specific RACT
requirements by 2009 (the required
compliance timing for RACT), they
would likely use labor and other
resources that would otherwise be used
for emission controls on larger sources.
Because of economies of scale, more
boiler-makers and other resources may
be required per megawatt of power
generation for smaller units than larger
units. Thus, the cost of achieving such
reductions would be greater on a per ton
basis. In any event, the imposition of
source-specific control requirements on
a limited number of sources also
covered by a cap-and-trade program
would not reduce the total emissions
from sources subject to the program.
Under a cap-and-trade program such as
CAIR, there is a given number of
allowances that equals a given emission
level. Source-specific control
requirements may affect the temporal
distribution of emissions (by reducing
banking and thus delaying early
reductions) or the spatial distribution of
emissions (by moving them around from
one place to another), but it does not
affect total emissions. If source-specific
requirements were targeted at the units
that can be controlled most cost
effectively, then the imposition of
source-specific controls would achieve
the same result as the projected CAIR
cap-and-trade program. If not, however,
66 As described in the April 21, 2004 rule (69 FR
21608).
67 CAIR achieves about 80% of its NO emission
X
reductions in 2009 (remainder in 2015).
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the imposition of source-specific
requirements would make any given
level of emission reduction more costly
than it would be under the cap-andtrade program alone. Thus, the
combination of source-specific RACT
and CAIR would not reduce the
collective total emissions from EGUs
covered by CAIR, but would likely
achieve the same total emissions
reductions as CAIR alone, in a more
costly way. As a result, we believe that
EGUs subject to the CAIR NOX controls
meet the definition of RACT for NOX (in
States that require all CAIR NOX
reductions from EGUs). EPA is making
this finding now for all areas in the
CAIR region, such that States need not
submit RACT analyses for sources
subject to CAIR that are in compliance
with a SIP approved as meeting CAIR.
Under CAIR, a State may elect to meet
its State budget for NOX emissions
solely through requiring reductions
from EGUs or through requiring
reductions from a combination of
sources, including non-EGUs. If the
State requires reductions from sources
other than EGUs, it is not eligible to
participate in the EPA-administered
CAIR trading program. Additionally,
separate provisions of the CAIR rule
allow States to choose to allow large
NOX sources that are not EGUs to optin to the program. If only part of the
CAIR reductions are required from
EGUs, and the balance of the reductions
obtained from non-EGU sources, then
the stringency of CAIR EGU control
would be diminished to some extent (an
amount that cannot be determined until
a State submits a SIP indicating which
sources are participating in the
program). Therefore, in these cases, the
above rationales for our judgment that
CAIR satisfies RACT would not apply.
However, even where a State allows optins from other source categories to meet
CAIR emission levels, if a State
transitions from the NOX SIP call level
of control to CAIR by the first two
transition options for non-EGUs
discussed above, the NOX RACT
requirement would be met for EGUs
(and the State would not need to
conduct RACT analyses for these EGUs)
if the State retains a summer season
EGU budget under CAIR that is at least
as restrictive as the EGU budget that was
set in the state’s NOX SIP call SIP.
Otherwise, the State would need to
conduct RACT analyses for EGUs (either
on an individual basis, or using the
averaging approach within the
nonattainment area).
For clarity, we would note that a State
has discretion to require beyond-RACT
NOX reductions from any source
(including CAIR or NOX SIP Call
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sources), and has an obligation to
demonstrate attainment as expeditiously
as practicable. In certain areas, States
may require NOX controls based on
more advanced control technologies to
provide for attainment of the ozone
standards.
Comments: Several States expressed
support for the proposed RACT
submittal date of 2 years after
designation for subpart 1 and subpart 2
areas. Other commenters suggested the
RACT submittal date for subpart 1 areas
should be 3 years after designation in
order to coincide with the attainment
demonstration submittal deadline and
to allow a more efficient use of
resources. In addition, comments from
industry suggested a 48–60 month
period is needed for installation of
controls, rather than the 30 month
period proposed.
Response: As described in an earlier
comment/response, in subpart 1 areas
that do not request an extension of their
attainment date, RACT is met with the
control requirements associated with a
demonstration that the NAAQS is
attained as expeditiously as practicable.
The EPA agrees with commenters that it
would be more efficient, in these areas,
if the date for submittal of the RACT
rules were to coincide with submittal of
the attainment demonstration since
RACT is closely tied to the attainment
demonstration. Therefore, in the final
rule, the RACT submittal date for these
areas is the same as the submittal date
for the attainment plan, which is 3 years
after designation (June 2007). Although
EPA is not setting a specific RACT rule
implementation deadline for these
areas, as provided in the Phase 1 rule,
all controls necessary for attainment
must be implemented by the beginning
of the attainment year ozone season. For
example, States would need to require
implementation no later than May 1,
2008 where the area has a June 15, 2009
attainment date.68 In some cases, the
time from State rule adoption to
installation of controls by sources may
be relatively short; in other cases,
sources may need more time. Therefore,
EPA encourages States to adopt rules
expeditiously (prior to the June 2007
deadline, where possible) so that
sources have more than sufficient time
to install the controls prior to the start
of the attainment year ozone season.
For subpart 2 moderate and above
areas and areas within an OTR, the final
rule is similar to provisions in section
182 of the CAA which require States to
submit RACT rules for these areas
within 24 months after the designation.
68 This assumes the ozone season in this example
begins May 1.
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Several commenters supported this
approach. Since some States may rely
on submittal of SIP revisions meeting
CAIR to also satisfy RACT for some
sources, the final rule extends the
proposed RACT submittal date of 24
months to 27 months after designation
(September 15, 2006), to be consistent
with the date for submittal of the CAIR
SIP (September 10, 2006).
For areas subject to the 27-month
RACT submittal date, EPA believes the
proposed 30-month period for
installation of controls is reasonable,
given that this is the statutorilyprescribed period 69 (for the areas
covered under subpart 2) and based on
our prior experience with States
adopting and implementing RACT
requirements. For instance, subsequent
to submission of the NOX RACT SIP
revisions for the 1-hour standard subject
to the 30-month CAA period, EPA
approved NOX RACT SIP submittals in
some areas which had been exempt
from the requirements, including the
Dallas and Houston areas, which
required implementation within 2 years
from the State adoption date. Also, the
EPA recently determined that a 24month period is adequate for stationary
internal combustion engines to install
low emission combustion controls
(April 21, 2004; 69 FR 21633).
The 48 to 60-month period (June 15,
2011) for installation of controls
suggested by some commenters was not
adequately supported with a
justification that more time is necessary.
In addition, as described in an earlier
comment/response, EPA anticipates that
many sources which applied controls
due to RACT requirements with the 1hour ozone standard will not need to
install new controls for the 8-hour
standard. Thus, because fewer sources
will be subject to new requirements to
meet RACT for the 8-hour standard than
were subject to the 1-hour standard,
there will be less demand for control
equipment. States and many sources
face a reduced burden compared to the
same CAA requirement in the 1990s.
Since the ozone season (40 CFR part
58, appendix D) does not begin for many
areas until May 1, however, for areas
with an effective date of designation of
June 15, 2004, the final rule allows
sources until the beginning of the area’s
2009 ozone season (generally May 1,
69 In the 1990 CAA Amendments, Congress
specifically added RACT requirements for major
sources in section 182. Section 182 required the
RACT rules to be implemented ‘‘as expeditiously as
practicable’’ but no later than 30 months after the
submittal deadline.
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2009) rather than March 15, 200970 to
install controls. Installation of controls
before the 2009 ozone season is
sufficient to provide the benefits for
timely attainment of the ozone standard
in areas with a 2010 or later attainment
date.71 And the short delay (generally
between March 15, 2009 and May 1,
2009) will cause no harm since it is
prior to the ozone season, which is
when ozone levels are most likely to be
at harmful levels. Sources meeting NOX
RACT through compliance with CAIR
would be subject to the CAIR NOX caps
beginning January 1, 2009. Additionally,
some areas have ozone seasons that
begin earlier than March 15, 2009 and
would need to ensure sources are
complying by that earlier date.
For subpart 1 areas that request an
attainment date extension (i.e., an
attainment date beyond 5 years after
designation), the final rule sets the
RACT submittal and implementation
dates the same as required for subpart
2 moderate and above areas, except
subpart 1 areas are required to submit
the RACT SIP with its attainment date
extension request.
2. Reasonably Available Control
Measures (RACM)
a. Background
As noted in the June 2, 2003 proposed
rule, subpart 1 of part D includes
general requirements for all designated
nonattainment areas, including a
requirement that a nonattainment plan
provide for the implementation of all
RACM as expeditiously as practicable,
including such reductions that may be
obtained through RACT. We have also
issued guidance for implementing the
RACM provisions of the CAA that
interprets that provision to require a
demonstration that the State has
adopted all reasonable measures to meet
RFP requirements and to demonstrate
attainment as expeditiously as
practicable and thus that no additional
measures that are reasonably available
will advance the attainment date or
contribute to RFP for the area.72 The
70 57 months from June 15, 2004 effective date of
designation (27 months to submission plus 30
months to implementation).
71 Note, since the CAA requires attainment as
expeditiously as practicable, some moderate
nonattainment areas may have an attainment date
earlier than June 15, 2010.
72 ‘‘State Implementation Plans; General Preamble
for Proposed Rulemaking on Approval of Plan
Revisions for Nonattainment Areas’’ 44 FR 20372 at
20375. ‘‘Provide for implementation of all
reasonably available control measures (RACM) as
expeditiously as practicable, insofar as necessary to
assure reasonable further progress and attainment
by the required date * * *’’
‘‘State Implementation Plans; General Preamble
for the Implementation of Title I of the Clean Air
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RACM requirement, which is set forth
in section 172(c)(1) of the CAA, applies
to all nonattainment areas that are
required to submit an attainment
demonstration, whether covered under
only subpart 1 or also subpart 2. The
June 2, 2003 proposal noted that EPA
had issued policies and procedures
related to RACM. The draft regulatory
text (section 51.912(d)) provided that for
each nonattainment area required to
submit an attainment demonstration
under § 51.908, the State would have to
submit with the attainment
demonstration a SIP revision
demonstrating that it has adopted all
control measures necessary to
demonstrate attainment as expeditiously
as practicable and to meet any RFP
requirements.
b. Summary of final rule
Section 51.912(d) of the final rule
reflects our proposal and draft
regulatory text. For each nonattainment
area required to submit an attainment
demonstration under § 51.908, the State
must submit with the attainment
demonstration a SIP revision
demonstrating that it has adopted all
control measures necessary to
demonstrate attainment as expeditiously
as practicable and to meet any RFP
requirements.
In the CAIR rulemaking (May 12,
2005, 70 FR 25221 et seq.), EPA found
that the control installations projected
to result from the CAIR NOX and SO2
caps in 2009 and 2010 would be as
much as feasible from EGUs across the
Act Amendments of 1990; Proposed Rule.’’ 57 FR
13498 at 13560 (April 16, 1992). In part this
guidance said, ‘‘The EPA * * * indicated that
where measures that might in fact be available for
implementation in the nonattainment area could
not be implemented on a schedule that would
advance the date for attainment in the area, EPA
would not consider it reasonable to require
implementation of such measures. The EPA
continues to take this interpretation of the RACM
requirement.’’ As an example, with regard to one
possible list of measures (TCMs under section
108(f) of the Act) that guidance said, ‘‘* * * based
on experience with implementing TCM’s over the
years, EPA now believes that local circumstances
vary to such a degree from city-to-city that it is
inappropriate to presume that all section 108(f)
measures are reasonably available in all areas. It is
more appropriate for States to consider TCM’s on
an area-specific, not national, basis and to consider
groups of interacting measures, rather than
individual measures.’’
‘‘Guidance on the Reasonably Available Control
Measures (RACM) Requirement and Attainment
Demonstration Submissions for Ozone
Nonattainment Areas.’’ John S. Seitz, Director,
Office of Air Quality Planning and Standards.
November 30, 1999. Web site: www.epa.gov/ttn/
oarpg/t1pgm.html.
Memorandum of December 14, 2000, from John
S. Seitz, Director, Office of Air Quality Planning
and Standards, re: ‘‘Additional Submission on
RACM from States with Severe One-Hour Ozone
Nonattainment Area SIPs.’’
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CAIR region by those dates. EPA
concluded that the CAIR compliance
dates represent an aggressive schedule
that reflects the limitations of the labor
pool, and equipment/vendor
availability, and need for electrical
generation reliability for installation of
NOX emission controls. We believe that
the CAIR rule appropriately reflects the
constraints the EGU sector faces in
achieving NOX reductions (and the
CAIR SO2 reductions) in a way that is
as expeditious as practicable. States
should recognize these constraints in
developing their own compliance
schedules for NOX emission controls in
meeting their CAIR and RACM
responsibilities. However, the CAIR rule
did not specify which sources should
install emissions control equipment or
reduce emission rates to a specific level
in order to meet the SO2 and NOX caps
under CAIR.
Based on our experience developing
the NOX SIP Call, CAIR, and the
proposed Clear Skies Legislation, we
believe that many power companies will
develop their strategies for complying
with CAIR based, in part, on
consultations with air quality officials
in the areas in which their plants are
located. Because power plants are
generally major emission sources, the
operators of those plants typically have
ongoing relationships with State and
local officials that will be involved in
developing air quality plans. We are
aware that, in the past, companies have
worked with air quality officials to meet
their emission control obligations under
a cap-and-trade approach such as the
NOX SIP Call while also addressing the
concerns of air quality officials about
the air quality impacts of specific
plants. This has led to controlling
emissions from power plants located in
or near specific ozone nonattainment
areas. A number of companies have
indicated that such collaboration will be
even more important as the States in
which they are located address multiple
air quality goals (e.g., visibility,
interstate air pollution, local attainment
of standards for multiple pollutants).
The EPA expects similar
consultations between States and power
sector companies on which plants will
be controlled under CAIR, considering
local attainment needs in planning for
CAIR compliance. This consultation
might promote opportunities to provide
improved air quality earlier for large
numbers of people. Power companies
may identify economic advantages in
situating CAIR controls to help the local
area attain; for example, it might need
to control fewer facilities for the area to
reach attainment. These benefits may
outweigh any additional marginal costs
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the company might incur by forgoing
less costly controls on another more
distant plant. In any event, the intent of
these consultations would not be to
upset market behavior or incentives.
With respect to ozone, we anticipate
that these consultations will affect
individual control decisions for a few
areas.
In this regard, EPA notes that CAIR
SIPs will be due in 2006, while local 8hour ozone attainment plans will be due
in 2007. The EPA suggests that
consultations on location of CAIR
controls would be timely during State
development of the CAIR SIP.
As States implement the RACM
provisions in conjunction with their
attainment demonstration, we recognize
that for some moderate areas and some
subpart 1 areas it may be difficult to
demonstrate attainment in less than 5
years due to the time needed to adopt
and implement controls, and the need to
achieve significant emissions reductions
to advance the attainment date.
However, the State will need to assess
RACM to determine whether the
attainment date could be sooner than 5
years from designation for each
nonattainment area.
EPA believes that while areas
projected to attain within 5 years of
designation as a result of existing
national measures should still be
required to conduct a RACM analysis,
such areas may be able to conduct a
limited RACM analysis that does not
involve additional air quality modeling
beyond that used for the attainment
demonstration. A limited analysis of
this type could involve the review of
available reasonable measures, the
estimation of potential emissions
reductions, the evaluation of the time
needed to implement these measures,
and anticipated levels of regional
controls affecting ozone in the
nonattainment area. In lieu of
conducting air quality modeling to
assess the impact of potential RACM
measures, existing modeling
information could be considered in
determining the magnitude of emissions
reductions that could significantly affect
air quality and potentially result in
earlier attainment. If the State, in
consultation with EPA, determines from
this initial, more limited RACM analysis
that the area may be able to advance its
attainment date through implementation
of reasonable measures, then the State
must conduct a more detailed RACM
analysis, involving air quality modeling
analyses, to assess whether it can
advance the attainment date.
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c. Comments and Responses
Comment: One commenter asked that
we clarify whether old SIP measures
become RACM.
Response: Under EPA’s policy
concerning RACM, there are no
measures that are automatically deemed
RACM. The determination of whether a
SIP contains all RACM requires an areaspecific analysis that there are no
additional economically and
technologically feasible control
measures (alone or in conjunction with
others) that will advance the attainment
date.73 The April 16, 1992, ‘‘General
Preamble’’ provides some guidance on
measures that the State should consider
in making its RACM determination,
including ‘‘any measure that a
commenter indicates during a public
comment period is reasonably available
should be closely reviewed by the
planning agency to determine if it is in
fact reasonably available for
implementation in the area in light of
local circumstances.’’ Such measures
can be rejected as not being RACM if
they will not advance attainment or
provide for RFP or if they are not
economically or technologically
feasible.
Comment: One commenter
recommended that EPA revise its policy
permitting SIPs to exclude otherwise
feasible and potentially RACM that
achieve emissions reductions in
increments less than the amount
necessary to advance the attainment
date by a full year. The commenter
believed this was an onerous standard
that has stymied development of new
control measures, particularly
transportation control measures. The
commenter believed EPA’s RACM
standard is especially harmful to the
ability to provide SIP credit for Smart
Growth land use, due to the long
timeframe over which land is developed
and redeveloped. The commenter
believes that ever-increasing
suburbanization of our nation inflates
the growth rate in VMT, thereby
neutralizing improvements in vehicle
emissions. The commenter claimed that
a significant air quality improvement
strategy for the 21st Century is compact
mixed use pedestrian-friendly
development near frequent transit and
believed that changing land use plans in
this direction will benefit air quality by
reducing the rate of growth in VMT and
emissions. The commenter
recommended that EPA be aware of this
and revise its RACM standard to
encourage local governments to alter
their land use plans by providing a
73 Ibid.
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mechanism to give credit for air quality
beneficial land use changes.
Response: We do not believe our
RACM policy has ‘‘stymied’’
development of new control
technologies. New emission reduction
technologies have surfaced and
continue to surface to meet market
demands resulting in part from CAA
requirements, which include the
requirements to demonstrate attainment
as expeditiously as practicable and to
make RFP toward attainment. In
addition, control measures that produce
emissions reductions can be approved
into SIPs whether or not such measures
meet the definition of RACM. Our
RACM policy merely interprets the CAA
as not mandating measures that do not
contribute to expeditious attainment
and timely RFP. The policy does not
limit the potential for States to develop
any control measures they wish,
including land use measures. In fact, we
have prepared a separate guidance
document on how areas can develop
and receive SIP credit for land use
control measures.74 We conclude,
however, that to require areas to adopt
and implement as RACM every control
technology or measure that obtains a
small amount of emissions reductions—
even if such measure would not
advance the attainment date or is not
required to meet RFP requirements—is
not justified. Such a policy would be
extremely burdensome to planning
agencies, would detract from the effort
to develop more reasonable and
effective controls to meet the NAAQS,
and would not be necessary to meet the
statutory goal of expediting attainment.
For these reasons, and because such a
requirement is not mandated by the
statute, we are not adopting such a
policy.
Comment: One commenter believed
that the RACM requirements for subpart
1 areas should be designed so as to not
require extensive and unneeded control
due to the fact that in most or all cases
these controls will not be needed for the
area to attain.
Response: We believe the current
RACM guidance, which applies to both
subpart 1 and subpart 2 areas, works to
avoid extensive and unneeded controls,
while ensuring that areas meet the
health-based NAAQS as expeditiously
as practicable.
Comment: One commenter believed
our RACM guidance provides only
minimum requirements to ensure
attainment as expeditiously as
74 Improving Air Quality Through Land Use
Activities; Transportation and Regional Programs
Division, Office of Transportation and Air Quality,
U.S. Environmental Protection Agency. EPA420–R–
01–001. January 2001.
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practicable and believes that every
nonattainment area must be required to
consider adoption of measures that have
been implemented in other areas,
including the South Coast of California,
so as to achieve progress and attainment
as expeditiously as practicable. An area
should be allowed to reject such
measures only upon a showing that they
are not practicable due to specified
unique circumstances. The commenter
urged that given the importance of this
issue to fair, expeditious and lawful
implementation of the 8-hour standard,
EPA’s final 8-hour standard
implementation rule must explicitly
require compliance with this guidance.
Response: To meet the RACM
provision of the CAA, the State must
determine as part of its attainment
demonstration whether there are
additional measures that are feasible
that would expedite attainment. In
addition, EPA’s RACM policy indicates
that areas should consider all candidate
measures that are potentially available,
including any that have been suggested
for the particular nonattainment area.75
Although areas should consider all
available measures, including those
being implemented in other areas such
as California, areas need adopt measures
only if they are both economically and
technologically feasible and will
advance the attainment date or are
necessary for RFP. This interpretation of
the section 172 requirements has
recently been upheld by several courts.
See, e.g., Sierra Club v. EPA, et al., 294
F. 3d 155 (D.C. Circuit, 2002).
Comment: Several commenters agreed
with our proposal to require that the
RACM analysis and measures be
submitted within 3 years after the
effective date of designation for the 8hour NAAQS.
Response: We acknowledge the
support of the comments on the
submission timing of the RACM
requirements.
H. How will the section 182(f) NOX
provisions be handled under the 8-hour
ozone standard?
[Section VI.L. of June 2, 2003
proposed rule (68 FR 32840); § 51.913 in
draft and final regulatory text.]
75 In ‘‘AState Implementation Plans; General
Preamble for the Implementation of Title I of the
Clean Air Act Amendments of 1990; Proposed
Rule,’’ we noted in the discussion of the RACM
requirement that ‘‘In addition, any measure that a
commenter indicates during the public commenter
period is reasonably available for a given area
should be closely reviewed by the planning agency
to determine if it is in fact reasonably available for
implementation in the area in light of local
circumstances.’’ The discussion of RACM in that
document contains other relevant history
concerning the RACM requirement.
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1. Background
While NOX emissions are necessary
for the formation of ozone in the lower
atmosphere, a local decrease in NOX
emissions can, in some cases, increase
local ozone concentrations. This
potential ‘‘NOX disbenefit’’ resulted in
Congress including the NOX exemption
provisions in section 182(f) of the CAA
for areas classified under subpart 2.
Section 182(f) requires States to apply
the same requirements to major
stationary sources of NOX as are applied
to major stationary sources of VOC
under subpart 2. The relevant
requirements are RACT and
nonattainment major NSR for major
stationary sources of NOX in certain
ozone nonattainment areas and
throughout States in the OTR.76 In
addition, section 182(f) specifies
circumstances under which these NOX
requirements would be limited or would
not apply (‘‘NOX exemption’’). Further,
areas granted a NOX exemption under
section 182(f) may be exempt from
certain requirements of EPA’s motor
vehicle I/M regulations and from certain
Federal requirements of general and
transportation conformity.77
In the June 2, 2003 action, we
indicated the NOX requirements and
exemption provisions in section 182(f)
would apply for subpart 2
nonattainment areas and in OTRs.78 In
addition, we proposed to allow subpart
1 nonattainment areas to seek a NOX
exemption, where appropriate. Further,
we proposed that areas previously
granted a NOX exemption under the 1hour ozone standard would need to
request an exemption for purposes of
the 8-hour standard in order to account
for any new information that may point
to a different conclusion with respect to
the 8-hour standard. Recently, we
invited comment 79 on draft guidance
intended to update the existing 1-hour
ozone guidance 80 regarding section
182(f) for application to the 8-hour
ozone program. We issued the updated
76 See 57 FR 55622 (‘‘Nitrogen Oxides
Supplement to the General Preamble,’’ published
November 25, 1992).
77 As stated in EPA’s I/M (November 5, 1992; 57
FR 52950) and conformity rules (60 FR 57179 for
transportation rules and 58 FR 63214 for general
rules), certain NOX requirements in those rules do
not apply where EPA grants an areawide exemption
under section 182(f).
78 68 FR 32840.
79 September 1, 2004 at 69 FR 53378.
80 The EPA’s primary guidance regarding section
182(f) is contained in the ‘‘Guideline for
Determining the Applicability of Nitrogen Oxide
Requirements under Section 182(f),’’ issued by John
S. Seitz, Director, Office of Air Quality Planning
and Standards, to the Regional Division Directors,
December 16, 1993.
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71661
final guidance regarding section 182(f)
on January 14, 2005.81
2. Summary of Final Rule
As proposed, the final rule allows a
person to petition the Administrator for
a NOX exemption under section 182(f)
for an area classified under subpart 2 or
located in an OTR or under our
regulations for any other area designated
nonattainment for the 8-hour ozone
NAAQS. As with the 1-hour ozone
standard, the NOX exemption provision
in section 182(f) applies to subpart 2
ozone nonattainment areas and in a
section 184 OTR. In addition, the final
rule extends to subpart 1 ozone
nonattainment areas the opportunity to
petition the Administrator for an
exemption from nonattainment major
NSR and/or RACT requirements in a
manner consistent with section 182(f)
provisions. The petition must contain
adequate documentation that the
provisions of section 182(f) and/or our
regulations are met. We recently
issued 82 updated guidance on
appropriate documentation regarding
section 182(f) for application to the 8hour ozone program. In addition, the
final rule states that a section 182(f)
NOX exemption granted under the 1hour ozone standard does not relieve
the area from any requirements under
the 8-hour ozone standard. That is, a
new petition with respect to 8-hour
ozone must be submitted to EPA and
must be approved by EPA before an area
is exempt from any 8-hour ozone
standard NOX requirements.
3. Comments and Responses
Comments: Several commenters
supported EPA’s proposal to make NOX
waivers available to 8-hour
nonattainment areas and all areas in an
OTR under either subpart 1 or subpart
2, pursuant to the provisions of section
182(f) of the CAA. Some commenters
stated that requiring a new NOX waiver
for the 8-hour standard amounts to
rescinding the existing waivers. Another
commenter asked what is needed to
maintain an exemption. One commenter
stated that EPA should make it clear
that there is no presumption that a NOX
waiver granted under section 182(f) of
the CAA for the 1-hour ozone standard
81 Memorandum dated January 14, 2005,
‘‘Guidance on Limiting Nitrogen Oxides (NOX)
Requirements Related to 8-Hour Ozone
Implementation’’ from Stephen D. Page, Director,
Office of Air Quality Planning and Standards, to Air
Directors, Regions I–X.
82 Memorandum dated January 14, 2005,
‘‘Guidance on Limiting Nitrogen Oxides (NOX)
Requirements Related to 8-Hour Ozone
Implementation’’ from Stephen D. Page, Director,
Office of Air Quality Planning and Standards, to Air
Directors, Regions I–X.
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is continued for the 8-hour standard.
Other commenters recommended that
the NOX waiver should automatically
apply for the 8-hour ozone standard in
areas where EPA previously granted a
NOX waiver under the 1-hour ozone
standard. One commenter stated that the
technical basis for granting waivers
under the l-hour NAAQS remains valid.
Response: We agree with comments
supporting the proposal to apply the
section 182(f) exemption provisions to
subpart 2 nonattainment areas and
OTRs and to extend these protections to
subpart 1 areas through regulation.
Since a NOX exemption granted for
the 1-hour ozone standard was
completed through notice-and-comment
rulemaking, the exemption remains
effective for the 1-hour standard unless
and until EPA completes rulemaking to
remove or revise the waiver for a
specific area. This rulemaking on the 8hour ozone implementation program
does not rescind any existing 1-hour
NOX waiver provision.
However, for areas previously granted
a NOX waiver under the 1-hour ozone
standard, a petitioner would need to
seek a new waiver for purposes of the
8-hour ozone standard. The EPA does
not believe NOX waivers—including
those granted under the 1-hour ozone
standard—should always be permanent.
As sources are regulated and the mix of
pollutants is altered, circumstances
could show that NOX reductions will
begin to provide a benefit. In several
cases, the 1-hour NOX waiver has been
removed in subsequent rulemaking
actions.83 Indeed, when EPA issued
waivers under the 1-hour ozone
standard, we stated that the NOX
waivers would be removed where new
information became available and the
rationale for the initial NOX waiver no
longer was supported. For example, the
waiver may be removed through
rulemaking if subsequent modeling data
demonstrated an ozone attainment
benefit from NOX emission controls.
Given that many NOX waiver actions
were based on air quality and dispersion
modeling analyses made in the mid1990s for purposes of the 1-hour
standard, EPA believes that newer data
and analyses should be used to
determine if a NOX waiver under the 8hour ozone standard is warranted. Many
NOX waivers were simply based on
whether an area had ambient air quality
showing attainment of the 1-hour ozone
standard; this is not an appropriate basis
for a waiver under the 8-hour ozone
83 E.g: Recision of NO waiver for the Dallas-Fort
X
Worth area on April 20, 1999 (64 FR 19283). Also,
the temporary waiver for Houston and Beaumont
(originally granted April 19, 1995, expired
December 31, 1997). (60 FR 19515).
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standard since areas may be attaining
the 1-hour standard but exceeding the 8hour standard. Some NOX waivers were
based on dispersion modeling. In some
cases, the modeling later proved
inadequate as attainment was not met in
the forecast year. In other cases, those
modeling analyses have been replaced
with more recent analyses. The EPA
believes that NOX waivers under the 8hour ozone standard should be
supported by analyses specific to the 8hour ozone standard and should
consider relevant information
developed after the 1-hour waivers were
granted.
The EPA believes the NOX waivers
may not be granted except through
notice-and-comment rulemaking action.
That is, since EPA approval of a waiver
request would change SIP requirements,
EPA must conduct notice-and-comment
rulemaking on that request. The EPA
believes this requirement precludes
automatic approval of 8-hour NOX
waiver requests based on previously
issued 1-hour NOX waivers.
Comment: Some commenters urged
EPA to expand the section 182(f) waiver
to VOC RACT as well as NOX RACT.
One commenter states that EPA has
substantially more discretion under
subpart 1 than it does under subpart 2,
and to fail to exercise that discretion to
avoid ineffective and inefficient
requirements (through NOX and VOC
waivers) would be irresponsible, and an
abuse of its discretion.
Response: The EPA disagrees with
these comments. We do not see any
provision in the CAA that would give us
the authority to create such an
exemption. While Congress could have
created a VOC waiver at the same time
the section 182(f) NOX waiver
provisions were enacted, Congress
chose not to do so. The Congress further
provided for additional review and
study under section 185B ‘‘to serve as
the basis for the various findings
contemplated in the NOX provisions’’
(H.R. Rep. 490 at 257). Under section
185B, EPA, in conjunction with the
National Academy of Sciences (NAS),
conducted a study on the role of ozone
precursors in tropospheric ozone
formation. The final section 185B report
incorporates this NAS report along with
an EPA report addressing the
availability and extent of NOX controls.
With respect to VOC, the NAS report
states that ‘‘control of VOCs never leads
to a significant increase in ozone.’’ 84
Thus, the section 185B report does not
support a waiver provision for VOC.
84 December 1991 NAS report, Rethinking the
Ozone Problem in Urban and Regional Air
Pollution, page 377.
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While dispersion modeling analyses
show that NOX emissions reductions
can be counterproductive under certain
circumstances (the reason for the NOX
waiver provision), we do not see a
similar case for VOC.
Comment: One commenter stated that
the draft guidance does not contain a
discussion of the linkages between
182(f) NOX exemptions and certain
other regional NOX reduction
requirements such as the NOX SIP Call
and the proposed ‘‘Clean Air Interstate
Rule.’’ The commenter believed EPA
has an obligation to assess the impact of
any section 182(f) exemption request
under the provisions of section
110(a)(2)(D), including the potential for
emissions exempted from controls to
contribute to downwind nonattainment
or to interfere with the maintenance of
any NAAQS.
Response: As discussed in section 4.2
of the draft 8-hour exemption guidance,
EPA encourages States/petitioners to
include consideration of air quality
effects that may extend beyond the
designated nonattainment area. States
should consider such impacts since they
are ultimately responsible for achieving
attainment in all portions of their State
and for ensuring that emissions
originating in their State do not
contribute significantly to
nonattainment in, or interfere with
maintenance by, any other State.
However, EPA believes NOX exemptions
under section 182(f) of the CAA and
interstate transport of emissions under
section 110(a)(2)(D) of the CAA can be
considered independently. Section
110(a)(2)(D) requires States to reduce
emissions from stationary and/or mobile
sources where there is evidence
showing that such emissions would
contribute significantly to
nonattainment or interfere with
maintenance in other States. In some
cases, then, EPA may grant an
exemption from certain NOX
requirements and, in a separate action,
require NOX emission decreases under
section 110(a)(2)(D). Thus, a NOX
exemption doesn’t affect an obligation
of a State to meet a NOX budget
established under a NOX SIP Call or
other transport rule.
I. Should EPA promulgate a NSR
provision to encourage development
patterns that reduce overall emissions?
[Section 0.9. of the June 2, 2003
proposed rule (68 FR 32849). No draft
or final regulatory text.]
Note: Section V of this preamble below
addresses rules for NSR for the 8-hour ozone
standard. This section addresses only the
June 2, 2003 proposal related to Clean Air
Development Communities (CADC).
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1. Background
In the June 2, 2003 proposal, we
considered two options designed to
recognize the air quality benefits which
can accrue when areas site new sources
and plan development in a manner that
results in overall reduced emissions. We
proposed to define a community that
changes its development patterns in
such a way that air emissions within the
nonattainment area are demonstrably
reduced as a CADC. As a result of
becoming a CADC, an area would obtain
a certain amount of flexibility in its NSR
program.
In the first option, we proposed that
a CADC would have a more flexible
NSR program by: (1) Being subject to
subpart 1 NSR as opposed to subpart 2
NSR; (2) lowering NSR major source
thresholds for these areas to make them
similar to the thresholds for PSD areas;
and (3) allowing areas that meet certain
development criteria (development
zones) to receive NSR offsets from State
offset pools. In the second option, we
proposed that a CADC would be able to
receive a pool of NSR offset credits
equal to the reduced emissions from
new development patterns. Credits from
the pool could be provided to any new
or modified source in a ‘‘development
zone’’ as offsets.
We also requested comments on the
options and encouraged comments
suggesting other ways of encouraging
development patterns that would result
in lower emissions.
2. Summary of Final Rule
The EPA is not at this time issuing
any rule related to CADCs.
3. Comments and Responses
Comments: The EPA received
numerous comments on the proposal,
some supporting and others opposing
the CADC provision. A number of the
commenters noted that the proposal did
not appear to have enough detail. A
summary of the comments appears in
the response to comment document.
Response: The EPA appreciates the
many comments it has received on this
section. The EPA agrees with a number
of commenters that while the ideas in
this section are interesting and designed
to achieve useful goals, much more
work is needed in a separate effort to
work through the many issues involved.
Therefore, EPA will not move forward
with this particular effort at this time.
However, EPA does not plan to ignore
the issue. The EPA will be looking to
bring a group of stakeholders together to
see if the group can come up with and
support one or more ways that we can
use existing programs and authorities to
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create positive incentives and tools for
communities to reduce sprawl. The
process will not be designed to work
only through the specific issues in
establishing a program to encourage
CADCs as outlined in the proposal, but
will be open to all ideas.
Issues related to community
development, land use and ‘‘sprawl’’
will have transportation and air quality
implications. Therefore, EPA will work
closely with DOT in addressing these
issues.
J. How will EPA ensure that the 8-hour
ozone standard will be implemented in
a way which allows an optimal mix of
controls for ozone, PM2.5, and regional
haze?
[Section VI.P. of June 2, 2003
proposed rule (68 FR 32852); no draft or
final regulatory text.]
1. Background
As noted in the proposal, in many
cases, States will be developing
strategies to attain both the 8-hour
ozone and PM2.5 NAAQS in the same
nonattainment area or in nonattainment
areas that have some area or areas in
common. Additionally, requirements for
regional haze apply to all areas. Certain
ozone control measures may also be
helpful as part of a PM2.5 control
strategy or a regional haze plan.
Similarly, controls for PM2.5 may lead to
reductions in ozone or regional haze.
Because the precursors for ozone and
PM2.5 may be transported hundreds of
kilometers, regional scale impacts may
also be relevant to consider. While EPA
expects that strategies to decrease ozone
concentrations will not adversely affect
strategies to attain the PM2.5 NAAQS,
we also believe integration of ozone,
PM2.5, and regional haze planning will
reduce overall costs of meeting multiple
air quality goals.
2. Summary of final rule
We are encouraging each State with
an ozone nonattainment area that
overlaps or is nearby a PM2.5
nonattainment area to take all
reasonable steps to coordinate the SIP
development processes for these
nonattainment areas and to coordinate
the development of these SIPs with the
state’s SIP to address the reasonable
progress goals for regional haze.
Specifically, EPA encourages States
conducting modeling analyses for ozone
to separately estimate effects of a
strategy on the following: mass
associated with sulfates, nitrates,
organic carbon, elemental carbon, and
all other species. However, while we
believe such coordination may reduce
the overall costs to States for
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implementing these programs, this final
rule does not require the State to
coordinate these three planning efforts.
3. Comments and Responses
Comments: Several commenters
supported EPA’s recommendation for
States to integrate planning for 8-hour
ozone, PM2.5, and regional haze. These
commenters agreed that the integration
of ozone, PM2.5 and regional haze
controls will reduce the overall costs of
meeting multiple air quality goals and
that EPA should continue to
synchronize the SIP planning
requirements for these pollutants to aid
in this integration. One commenter
asked EPA to clarify that this analysis is
not an approvability issue associated
with an 8-hour attainment
demonstration. Other commenters
recommended that EPA require
nonattainment areas to perform an
integrated control strategy assessment to
ensure ozone controls will not preclude
optimal controls for secondary fine
particles and visibility impairment.
Response: We recognize the
importance of integrating planning for
8-hour ozone, PM2.5, and regional haze
as much as possible, given the overlap
in technical work and likely control
strategies. None of the commenters,
however, has identified legal authority
that allows EPA to require
nonattainment areas to perform an
integrated control strategy assessment to
ensure ozone controls will not preclude
optimal controls for secondary fine
particles and visibility impairment.
Therefore, we will continue to
encourage States to coordinate their
work, but it is not a requirement and,
thus, not an approvability issue.
Comments: Other commenters
encouraged EPA to identify flexibility so
that areas may be provided more time if
they are developing a multi-pollutant
strategy. Commenters stated that it is
imperative that SIP obligations and
attainment dates with respect to these
regulated air pollutants be harmonized
and that regulatory requirements and
deadlines be closely coordinated. One
commenter stated this may require
certain deadlines be extended and that
they believe Congress would not be
opposed to extending deadlines in the
name of efficiency.
Response: To the extent our legal
authority allows, we are working to
harmonize SIP timelines for ozone,
PM2.5, and regional haze. This 8-hour
ozone implementation rule is
necessarily based on the existing CAA
and does not assume any changes to the
CAA that may occur in the future. Thus,
we cannot extend the submission dates
for 8-hour ozone SIPs so that they match
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the later submission dates for PM2.5 and
regional haze SIPs. However, there is a
substantial overlap in planning periods
that will allow States to coordinate
planning efforts among programs,
without postponing implementation.
K. What emissions inventory
requirements should apply under the 8hour ozone NAAQS?
[Section VI.Q. of June 2, 2003
proposed rule (68 FR 32853); § 51.915 in
draft and final regulatory text.]
1. Background
Section 182(a)(1) requires that
marginal and above ozone
nonattainment areas submit an emission
inventory 2 years after designation as
nonattainment in 1990. For
nonattainment areas classified under
subpart 2 for the 8-hour ozone standard,
we proposed to interpret this to mean
that an emission inventory would be
required 2 years after designation (i.e.,
in 2006 if EPA designates areas in 2004).
The Consolidated Emission Reporting
Rule (CERR) in 40 CFR part 51, subpart
A, requires States to submit
comprehensive statewide triennial
emission inventories, beginning with
the 2002 inventory year, regardless of an
area’s attainment status. Because these
emission inventories will be available,
we proposed that the data elements
required for emission inventories by the
CERR could be used to prepare the
emissions inventories under the 8-hour
NAAQS. The draft regulatory text,
however, did not contain a specific
requirement that the emission inventory
be submitted as a SIP revision within 2
years after designation.
For subpart 1 areas, section 172,
paragraphs (b) and (c)(3) require
submission of the nonattainment area
emission inventory as part of the SIP by
a date established by EPA, which cannot
be later than 3 years after designation as
a nonattainment area. However, the June
2, 2003 proposal did not specify a
deadline for submission of the emission
inventory for subpart 1 areas.
The proposal also noted that we
would be updating the April 1999
‘‘Emissions Inventory Guidance for
Implementation of Ozone and
Particulate Matter National Ambient Air
Quality Standards (NAAQS) and
Regional Haze Regulations,’’ EPA–454/
R–99–006. This guidance has been
updated and now is available as:
‘‘Emission Inventory Guidance for
Implementation of Ozone and
Particulate Matter National Ambient Air
Quality Standards (NAAQS) and
Regional Haze Regulations’’, EPA–454/
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R–05–001.85 This guidance
complements the CERR by providing
guidance on how to prepare data for
emissions inventory SIP submissions.
emissions inventory under the 8-hour
ozone NAAQS. Also, EPA expects the
States to consult the guidance document
‘‘Emission Inventory Guidance for
Implementation of Ozone and
Particulate Matter National Ambient Air
Quality Standards (NAAQS) and
Regional Haze Regulations’’, EPA–454/
R–05–001, and to submit inventories
that are appropriate for the geographic
area at issue and consistent with this
guidance.86 We expect the State to
include in its SIP submission
documentation explaining how the
emissions data were calculated.
2. Summary of Final Rule
Section 51.915 of the final rule
reflects our June 2, 2003 proposal but is
different from the draft regulatory text.
To ensure comprehensive treatment of
emission inventory requirements, the
final rule contains language addressing
the deadlines for submission of
emission inventories for both subpart 1
and subpart 2 areas. The deadlines
reflect the statutory requirements of no
later than 3 years after designation for
a subpart 1 area, and no later than 2
years after designation for subpart 2
areas. Existing emissions reporting
requirements in 40 CFR part 51, subpart
A are sufficient to satisfy the emissions
inventory data requirements under the
8-hour ozone NAAQS. Consistent with
the statutory schedule in section
182(a)(1) of the CAA, the final
regulatory text in section 51.915
requires submission of an emission
inventory no later than 2 years after
designation as part of a subpart 2 SIP.
Consistent with the statutory schedule
in paragraphs (b) and (c)(3) of section
172 of the CAA, the final regulatory text
in section 51.915 requires submission of
an emission inventory no later than 3
years after designation as part of a
subpart 1 SIP.
In its guidance titled, ‘‘Public Hearing
Requirements for 1990 Base-Year
Emissions Inventories for Ozone and
Carbon Monoxide Nonattainment
Areas,’’ September 29, 1992, EPA set
forth its interpretation of a ‘‘de
minimis’’ deferral of the public hearing
requirement and the requirement for
EPA to approve or disapprove emissions
inventories under section 110(k). The
EPA intends to follow this guidance in
implementation of the emissions
inventory requirements under the 8hour ozone standard, under which areas
could defer holding public hearings on
their inventories and EPA could defer
approving such inventories until the
time the areas adopt and submit their
attainment demonstrations and/or RFP
plans.
Existing emissions reporting
requirements in 40 CFR part 51, subpart
A can be applied to determine the data
elements required for emissions
inventories under the 8-hour ozone
NAAQS (see, e.g. Tables 2A, 2B, 2C, and
2D). Where appropriate, the State may
use the data elements developed under
part 51, subpart A in preparing its
3. Comments and Responses
Comment: Several commenters said
that the proposal does not discuss
specific requirements above and beyond
those in the CERR. However, the
proposal does mention one EPA
guidance document, ‘‘Emissions
Inventory Guidance for Implementation
of Ozone and Particulate Matter
National Ambient Air Quality Standards
(NAAQS) and Regional Haze
Regulations’’. This document states that
‘‘The EPA developed this guidance
document to complement the CERR and
to provide specific guidance to State
and local agencies and Tribes on how to
develop emissions inventories for 8hour ozone, PM2.5, and regional haze
SIPs.’’ Since the 8-hour emissions
inventory requirements are the same for
the CERR, there should be no
additional, special requirements needed
in emissions inventory development for
the proposed 8-hour rule.
Response: In its proposal, when EPA
referred to the CERR emissions
inventory requirements as satisfying
requirements for emissions inventories
under the 8-hour standard, EPA was
referring to the requirements for data
elements. The EPA did not mean to
imply that the emissions inventories
developed under the CERR, which are
statewide, would satisfy all aspects of
SIP inventories developed for SIP
submissions under the 8-hour standard.
While the CERR sets forth requirements
for data elements, EPA guidance
complements these requirements and
indicates how the data should be
prepared for SIP submissions. The 2002
emission inventory submitted as a SIP
element under the 8-hour ozone SIP
process is not necessarily the same as
the 2002 emission inventory submitted
under the CERR. The two inventories
differ in some important ways. For
example, the CERR inventory was due
June 1, 2004, while the SIP inventory
due dates are later. Because of this time
85 (available at: https://www.epa.gov/ttn/chief/
eidocs/eiguid/)
86 The CERR requires emissions inventory data on
a statewide basis.
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lapse, the State may choose to revise
some of the data from the CERR when
it prepares its SIP inventory because of
improvements in emission estimates.
The SIP inventory also must be
approved by EPA as a SIP element and
is subject to public hearing
requirements where the CERR is not.
Because of the regulatory significance of
the SIP inventory, EPA will need more
documentation on how the SIP
inventory was developed by the State as
opposed to the documentation required
for the CERR inventory. In addition, the
geographic area encompassed by some
aspects of the SIP submission inventory
will be different from the statewide area
covered by the CERR emissions
inventory. The guidance document
‘‘Emissions Inventory Guidance for
Implementation of Ozone and
Particulate Matter National Ambient Air
Quality Standards (NAAQS) and
Regional Haze Regulations’’ 87 provides
details on how States should prepare
their emission inventory SIP submittals
and discusses these and other relevant
topics. If a State’s 2005 emission
inventory (or a later one) becomes
available in time to use for an area
subsequently redesignated
nonattainment, then that inventory
should be used. We also encourage the
cooperation of the Tribes and the State
and local agencies in preparing their
emissions inventories.
Comment: One commenter was
concerned with the timing of the release
of the final version of the NONROAD
model (used to estimate mobile source
emissions from nonroad sources). The
commenter agreed that the draft version
out for comment during the comment
period was superior to previous
calculation methodology and should be
used for planning purposes. However,
EPA needs to be cognizant of how
disruptive to the planning process it is
for new versions of emissions models to
be released and incorporated in the
middle of the development of a SIP. The
commenter strongly encourages EPA to
expedite the review and approval of any
new models that will ultimately be used
by States.
Response: We acknowledge that the
timing of the release of new models can
sometimes complicate the SIP planning
process. In this case, the timing of the
final release of the NONROAD is
dependent on the timing of the new
nonroad standards final rule. We will do
what we can to expedite the release of
a new version of NONROAD that
reflects the emissions benefits of the
87 EPA–454/R–05–001, August 2005 (available at:
https://www.epa.gov/ttn/chief/eidocs/eiguid/
index.html).
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nonroad rule as soon as possible. In
addition, we intend to provide guidance
on the use of NONROAD that allows for
completion of ongoing work with the
current version of NONROAD if
switching to the new version would
cause significant delay. The EPA has
included similar language in previous
SIP policy guidance for the MOBILE
model.
Comment: One commenter urged EPA
to improve the quality of PM2.5 rates in
MOBILE6.2 so that areas will have a
more reliable tool for creating a 2002
base-year inventory and for developing
SIP revisions. The commenter was
concerned about developing PM2.5
emissions inventories because PM2.5
emissions factors in MOBILE6.2 are
based largely on the old Part #5
emission model and are not as
sophisticated as the rates for CO, NOX,
and VOC. The commenter also
expressed concern about the lack of
knowledge and techniques available for
performing on-road mobile source fine
particulate emissions inventories.
Metropolitan Planning Organizations
(MPOs) and air quality agency staff need
to have a more reliable tool and
acceptable methods for creating base
year PM2.5 inventories and for SIP
planning.
Response: This comment is not
directly relevant to the 8-hour ozone
implementation rule. However in the
interest of providing clarification on the
issues raised by the commenter, we
provide the following background
information. Particulate emission factors
in MOBILE6.2 are based on the best
technical information available at the
time the model was developed and we
believe that it is the best available tool
for estimating on-road emission factors
for PM2.5. We are currently collecting
additional PM data which will be
incorporated in future versions of the
EPA mobile source emission factor
model. We continue to work to improve
models and inventory methods for all
pollutants. We have released technical
guidance on the use of MOBILE6.2 and
on methods for developing annual
inventories in SIPs and conformity
analyses to help MPOs and air quality
agency staff perform on-road mobile
source fine particulate analyses.
Comment: One commenter stated that
since the CERR requires inventories
every 3 years, that the CERR should
replace the Emission Statement
Reporting Program (ESRP) requirement,
which was required before the CERR
was adopted.
Response: The ESRP is statutorily
prescribed in section 182 (a)(3)(B) of the
CAA. The emission statement
requirement satisfies a different need
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from the periodic emissions inventory
requirement, namely that affected
sources themselves have to report to the
State their updated emissions
information, whereas the emissions
inventory requirement is a requirement
on States to compile and make available
to EPA an emissions inventory. We
believe that the ESRP is a
complementary program to the CERR
and makes it easier for States to satisfy
their CERR reporting requirements by
providing data to the States from the
sources.
Comment: One commenter said that
persistent inaccuracies in official
emissions inventories have hindered
regulatory acknowledgment and
mitigation of the automobile VOC and
CO gross polluter problem. The EPA
should develop realistic emissions
inventories and require States to do the
same. Known errors in these inventories
continue to misdirect emission
reduction efforts. In particular, too little
focus has been placed on the potential
for rapid, substantial VOC and CO
reductions from the in-use automobile
fleet.
Response: We agree that realistic
emissions inventories are important to
properly direct emission reduction
efforts. Current emission factor models
and inventory methods are far superior
to previous models and methods and we
are working to continually improve
models and methods for developing
emissions inventories for on-road and
nonroad vehicles and equipment.
Comment: One commenter stated that
the official emissions inventories
generated and used by EPA and State
regulatory agencies for SIP planning and
implementation have been shown
repeatedly to suffer from serious
inaccuracies and biases. Problems with
inventories include errors in the total
amount of emissions, as well as errors
in the apportionment of emissions
among various source categories. The
most serious inventory problems center
on VOC and CO, while problems with
NOX inventories appear to be more
modest. Since emissions inventories are
a fundamental input to the process of
choosing pollution reduction measures
and to the modeling used to
demonstrate future attainment of
NAAQS, an inaccurate inventory is
likely to lead to poor policy choices in
terms of cost, effectiveness, or both.
Response: We agree that emissions
inventories are fundamental inputs to
the air quality management process. We
continue to strive to work with State
and local agency partners to develop
emissions inventories that best reflect
the real world and will thus assist in
identifying control strategies to make
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RFP and attain the NAAQS. One should
be aware, however, that it is impossible
to develop an emissions inventory for
an area that is 100 percent accurate. Part
of the problem is that most sources—
including mobile sources—don’t
monitor and report emissions
continuously, and therefore we and the
States must use other methods to
estimate emissions from them. Thus,
emission inventories are by nature
estimates of actual releases to the
atmosphere. The EPA believes that
current emission inventories are
sufficiently accurate to support the air
quality management decisions that are
derived from the application of
emission inventories and air quality
models. The emissions data generated
and used by EPA and State regulatory
agencies for SIP planning and
implementation is the best available.
Although inventories are often criticized
as lacking accuracy, seldom do critics
supply better information.
Comment: One commenter stated that
the Agency proposes that the latest
approved version of the MOBILE model
should be used to estimate emissions
from on-road transportation systems.
The commenter recommended that if
there are other models that meet EPA
performance criteria and are
scientifically peer reviewed, they
should also be acceptable [e.g., the
California mobile model, ‘‘EMission
FACtor’’ (EMFAC)].
Response: We believe that MOBILE is
the best available tool for estimating
emissions from on-road transportation
systems outside of California. We are
working to continually improve
emission factor models and inventory
methods for on-road vehicles. The
EMFAC is not designed to be able to
estimate fleet, activity, fuel, and
environmental characteristics outside of
California and is not a reasonable
substitute for MOBILE in States other
than California.
Comment: One commenter supported
the use of MOBILE6 in the 8-hour
emissions inventory analyses and
believed that EPA should change the
guidance with respect to the use of
MOBILE6 from ‘‘should be used’’ to
‘‘must be used.’’ The commenter
cautioned that MOBILE6 still
significantly over-predicts emissions
from passenger cars and light duty
trucks for many reasons including the
following: (1) The model does not
adequately account for the benefits of
onboard diagnostic regulation in non-I/
M areas; and (2) the model does not
reflect the decline in trips per day
versus vehicle age.
Response: The EPA’s January 18, 2002
SIP and conformity policy guidance
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document (‘‘Policy Guidance on the Use
of MOBILE6 for SIP Development and
Transportation Conformity,’’ memo
from John Seitz and Margo Oge to EPA
Regional Air Division Directors) states,
‘‘In general, EPA believes that MOBILE6
should be used as expeditiously as
possible. The Clean Air Act requires
that SIP inventories and control
measures be based on the most current
information and applicable models that
are available when a SIP is developed.’’
The EPA’s February 14, 2004 SIP and
conformity policy guidance document
(‘‘Policy Guidance on the Use of
MOBILE6.2 and the December 2003 AP–
42 Method for Re-Entrained Road Dust
for SIP Development and Transportation
Conformity’’, memo from Margo Oge
and Steve Page to EPA Regional Air
Division Directors) updates this by
stating that ‘‘All states other than
California should use MOBILE6.2 for
future VOC, NOX, and CO SIP and
conformity analyses in order to take full
advantage of the improvements
incorporated in this version.’’
MOBILE6.2 is the most current
applicable model and is based on the
best information available at the time of
its development and release. Therefore,
EPA has indicated that it should be
used.
We do not believe that more on-board
diagnostic benefits in non-I/M areas was
justified based on available data at the
time of the release of MOBILE6.2.
Likewise, we did not have sufficient
data to develop alternative assumptions
about the relationship between trips per
day and vehicle age. We are working to
continually improve emission factor
models and inventory methods for onroad vehicles and will review these
issues during the development of the
next emission factor model.
L. What guidance should be provided
that is specific to Tribes?
[Section VI.R. of June 2, 2003
proposed rule (68 FR 32854); no draft or
final regulatory text.]
1. Background
As noted in the preamble to the
proposal, the TAR (40 CFR, part 49),
which implements section 301(d) of the
CAA, gives Tribes the option of
developing TIPs which can then be
submitted to EPA for approval. Unlike
States, Tribes are not required to
develop implementation plans. Under
the TAR, eligible Tribes are treated in
the same manner as a State when
implementing the CAA; however, EPA
has determined that Tribes are not
required to meet plan submittal and
implementation deadlines in the CAA,
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e.g., 110(a)(1), 172(a)(2), 182, 187, and
191.88
The TAR provides flexibility for
Tribes in the preparation of a TIP to
address the NAAQS. The ‘‘modular
approach’’ was described in the June 2,
2003 proposal of this rule. The TAR
indicates that EPA ultimately has the
responsibility for implementing CAA
programs in Indian country, as
necessary or appropriate, if Tribes
choose not to implement those
provisions. The EPA may find it
necessary to develop a FIP to reduce
emissions from sources in Indian
country where the Tribe has not
developed a TIP to address an air
quality problem.
Finally, as discussed in the June 2,
2003 proposal, it is important for both
States and Tribes to work together to
coordinate planning efforts since many
nonattainment areas may include both
Tribal land and non-Tribal land.
Coordinated planning will help ensure
that the planning decisions made by the
States and Tribes complement each
other and that the nonattainment area
makes reasonable progress toward
attainment and ultimately attains the
NAAQS. In reviewing and approving
the individual TIPs and SIPs, we will
make certain they do not conflict with
the overall air quality plan for an area.
Section 301(d) of the CAA recognizes
that eligible Indian Tribes are generally
the appropriate non-Federal authority to
implement the CAA in Indian country.
As stated in the TAR, it is appropriate
to treat eligible Tribes in the same
manner as States, except for certain
identified provisions, including
provisions relating to plan submittal
and implementation deadlines, 40 CFR
section 49.3, 49.4. Therefore, when we
discuss the role of the State in
implementing this rule, we are also
generally referring to eligible Tribes,
with the above exception.
As we noted in the June 2, 2003
proposal, States have an obligation to
notify Tribes as well as other States in
advance of any public hearing(s) on
their State plans that will significantly
impact such jurisdictions. Under 40
CFR 51.102(d)(5), States must notify the
88 See 40 CFR part 49.4(a). In addition, EPA
determined it was not appropriate to treat Tribes
similarly to States with respect to provisions of the
CAA requiring as a condition of program approval
the demonstration of criminal enforcement
authority or providing for the delegation of such
criminal enforcement authority. See 40 CFR part
49.4(g). To the extent a Tribe is precluded from
asserting criminal enforcement authority, the
Federal government will exercise primary criminal
enforcement responsibility. See 40 CFR part 49.8.
In such circumstances, Tribes seeking approval for
CAA programs provide potential investigative leads
to an appropriate Federal enforcement agency.
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affected States of hearings on their SIPs;
this requirement extends to Tribes
under 301(d) of the CAA and the TAR.
(40 CFR part 49). Therefore, affected
Tribes that have achieved ‘‘treatment in
the same manner as States’’ status must
be informed of the contents of such
plans and the extent of documentation
to support the plans. In addition to this
mandated process, we encourage States
to extend the same notice to all Tribes
for the reasons noted in the comment
and response below. As a matter of
policy, EPA intends to consult with and
assist all Tribes, regardless of whether a
Tribe has received Treatment in the
same manner as a State (TAS) approval
for the purpose of implementing its own
TIP, and we encourage States to do the
same.
Understanding the content of a SIP
will be important to Tribes located next
to areas that are required to adopt SIPs,
particularly to Tribes who do not choose
or have the capacity to develop a TIP.
Therefore, EPA intends to offer Tribes
the opportunity for consultation on
activities potentially affecting the
achievement and maintenance of the
NAAQS in Indian country. In addition,
we expect States to work with Tribes
with land that is part of the same air
quality area during the SIP development
process and to coordinate with Tribes as
they develop the SIPs. In the case where
the State models projected emissions
and air quality under the SIP, the Tribes
should be made aware of these
modeling analyses. Tribes may wish to
determine if the Tribal area has been
affected by upwind pollution and
whether projected emissions from the
Tribal area have been considered in the
modeling analysis.
Generally, Tribal lands have few
major sources, but in many cases, air
quality in Indian country is affected by
the transport—both long range and
shorter distance transport—of
pollutants. In many cases, Tribal
nonattainment problems caused by
upwind sources will not be solved by
long-range transport policies, as the
Tribes’ geographic areas are small.
Tribes are sovereign entities, and not
political subdivisions of States.
Strategies used for intrastate transport
are not always available. Most of the
strategies and policies used by States in
dealing with short-range transport are
not available to Tribes, e.g., requiring
local governments to work together and
expanding the area to include the
upwind sources. Unlike Tribes, States
can generally require local governments
to work together, or make the
nonattainment area big enough to cover
contributing and affected areas. We
believe that it is also unfair to Tribes to
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require disproportionate local regulatory
efforts to compensate for upwind
emissions. In many cases, attainment
could not be reached even if emissions
from the Tribe were zero.
To address these concerns, in the June
2, 2003 proposal, we took comment on
the following: EPA will review SIPs for
their effectiveness in preventing
significant contributions to
nonattainment in downwind Tribal
areas with the same scrutiny it applies
to reviewing SIPs with respect to
impacts on downwind States. Where a
Tribe has ‘‘treatment in the same
manner as States,’’ EPA will support the
Tribes in reviewing upwind area SIPS
during the State public comment period.
2. Summary of Policy
We intend to take the approach noted
in the proposal.
3. Comments and Responses
Comment: One commenter was
concerned about the transport of
pollutants, including ozone precursors
from urbanized areas into areas of
Indian country. The commenter
expressed strong support for the
proposed 8-hour implementation rule
statement that ‘‘EPA will review SIPS
for their effectiveness in preventing
significant contributions to
nonattainment in downwind Tribal
areas with the same scrutiny it applies
to impacts on downwind States. Where
a Tribe has ‘treatment in the same
manner as States,’ EPA will support the
Tribe in reviewing upwind area SIPs
during the State public comment
period.’’ This commenter asked for
clarification on the nature of EPA’s
support for Tribes without TAS status.
The commenter also asked if EPA would
support Tribes without TAS approval in
reviewing upwind area SIPs and
provide technical assistance in
interpreting SIP documentation.
Response: In the TAR, we stated that
the CAA protections against interstate
pollutant transport apply with equal
force to States and eligible Tribes. We
stated that the prohibitions and
authority contained in sections
110(a)(2)(D) and 126 of the CAA apply
to eligible Tribes in the same manner as
States. (See 63 FR 7254, 7260; February
12, 1998). Section 110(a)(2)(D) requires,
among other things, that States include
provisions in their SIPs that prohibit
any emissions activity within the State
from significantly contributing to
nonattainment, interfering with
maintenance of the NAAQS or PSD or
visibility protection programs in another
State. In addition, section 126
authorizes any State or eligible Tribe to
petition EPA to enforce these
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prohibitions against a State containing
an allegedly offending source or group
of sources.
We intend to consult with and assist
Tribes during the TIP and SIP
development process, regardless of
whether a Tribe has received TAS
approval for the purpose of
implementing its own TIP. Executive
Orders and EPA Indian policy generally
call for EPA to be proactive with the
Tribes. Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ requires
EPA to develop an accountable process
to ensure ‘‘meaningful and timely input
by Tribal officials in the development of
regulatory policies that have Tribal
implications.’’ As part of EPA’s ongoing
efforts to actively involve Tribal officials
in the development of programs which
have Tribal implications, EPA in the
July 18, 2000 ‘‘Guidance on 8-hour
Ozone Designations for Indian Tribes’’
established a consultation process with
each Tribe that EPA used throughout
the designations process regardless of
whether a particular Tribe has received
an eligibility determination to
implement section 107 of the CAA. In
summary, EPA intends, as a matter of
policy, to consult with and assist
interested Tribal governments,
regardless of their TAS status, in
ensuring that the NAAQS are achieved
in Indian country, including working
with those Tribes located downwind
from a polluting area.
Comment: One commenter also asked
us to explain how we envision our role
in maintaining continued consultation
with Tribes throughout the SIP
development process.
Response: We intend to continue to
offer Tribes the opportunity for
consultation on activities potentially
affecting attainment and maintenance of
the NAAQS in Indian country. In
addition, we expect States to work with
Tribes with land that is part of a
nonattainment area in the SIP
development process and to inform
Tribes of the content of these SIPs as
they develop them. States should
coordinate with Tribes when projecting
emissions from counties or other areas
which include areas of Indian country
to ensure that assumptions regarding
demographics, economic activity,
commuting patterns, etc. are accurate
for the Tribal portions. Where the State
models project future emissions under
the SIP and their effect on air quality,
then Tribes should be made aware of
these modeling analyses in order to
determine if their Indian country is
being affected by upwind pollution and
whether this impact has been
considered in the modeling analyses.
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States have an obligation under 40
CFR 51.102(d)(5) to notify other States
in advance of any public hearing(s) on
their State plans which will
significantly impact those other entities.
This CAA requirement for States to
notify other parties extends to Tribes
under section 301(d) and the TAR.
Historically, States have not always
understood their responsibility to
coordinate with other affected entities,
including, where appropriate, Tribes.
States may not know how to contact
Tribes, particularly when Tribal air
programs are not well developed. It may
be difficult for a State to obtain a copy
of the control requirements for Indian
country. We can assist States in
identifying and contacting Tribes. When
developing control strategies and
making policy decisions, States, should
as appropriate, coordinate with Tribes at
the earliest opportunity. Where States
utilize stakeholder-based consensus
processes to develop SIP strategies, we
recommend that Tribes be provided the
opportunity to participate in the
process.
We have begun providing training to
Tribes about how to participate in SIP
development and implementation.
Many Tribes may not possess the
resources to develop a TIP or may
decide not to develop a TIP. Some will
develop robust air quality programs,
which may or may not include a TIP.
We intend to work with Tribes with all
levels of air management programs. In
general, where areas of Indian country
have poor air quality, it is most likely
as a result of transported pollution
sources. We recognize that the manner
in which States construct the SIP and
what sources the SIP controls may
impact Indian country located in
downwind areas.
Comment: One commenter raised
concerns about the practical impacts of
the NSR program on Indian Tribes. The
commenter noted that Tribes have long
traditions of environmental stewardship
and recognize their responsibility to
protect the health of their citizens.
However, the commenter noted that
Tribes have the right to pursue
industrial and economic development.
While that development must comply
with all current environmental
standards, the Tribes should not be
burdened with requirements that in
effect subsidize non-Tribal sources of
pollution.
Under the nonattainment NSR
program, new major sources locating in
a nonattainment area are required to
obtain emissions reductions, referred to
as offsets. The commenter stated that
this requirement poses a hardship on an
Indian reservation located in a larger
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nonattainment area. The new source
wishing to locate on the reservation
must obtain offsets from elsewhere in
the nonattainment area; there are not
usually enough sources on the
reservation to supply the needed
emissions reductions. When a Tribe is
located in such a nonattainment area,
efforts to increase economic
development may be stalled by an
inability of new sources to obtain
offsets. The commenter concluded that
this requirement is unfair to Tribes
because of past barriers to economic
development in Indian country. The
commenter also stated that in many
cases air pollution is transported onto
the reservation.
Response: The EPA acknowledges
that offsets are a concern for Tribes. We
are currently evaluating potential
options for addressing this concern.
M. What are the requirements for OTRs
under the 8-hour ozone standard?
[Section VI.S. of June 2, 2003
proposed rule (68 FR 32855); § 51.916 in
draft and final regulatory text.]
1. Background
Section 176A of the CAA provides
EPA with authority to establish
interstate transport regions where
transport of air pollutants from one or
more States contributes significantly to
a violation of a NAAQS in one or more
other States.
Section 184 of the CAA establishes
additional provisions for OTRs. Section
184(a) specifically established an OTR
comprising 12 Northeast and MidAtlantic States and the District of
Columbia in order to address the
longstanding problem of interstate
ozone pollution in that region. To date,
the existing OTR is the only transport
region for any pollutant that has been
established. The general provisions of
section 176A apply to any OTR
established under section 184.
Section 184(b) sets forth specific VOC
and NOX regulatory requirements to be
applied throughout the entire OTR, in
both attainment and nonattainment
areas, to reduce interstate pollution.
These additional regional regulatory
requirements are NSR (for VOC and
NOX), RACT (for VOC and NOX),
enhanced vehicle I/M, and Stage II
vapor recovery (for vehicle refueling) or
a comparable measure. In general, these
requirements duplicate requirements for
certain ozone nonattainment areas that
are classified under subpart 2. In the
proposal, we indicated that we believed
that under section 184 the current OTR
will remain in place and remain subject
to the section 184 control requirements
for purposes of the 8-hour standard.
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2. Summary of Final Rule
Section 184 continues to apply for
purposes of the 8-hour standard. The
current OTR remains in place and the
section 184 control requirements
continue to apply for purposes of the 8hour standard.
Today’s rule describes RACT
requirements for portions of an OTR
that are not classified moderate or
above. Consistent with the RACT
requirement for areas classified as
moderate and above for the 8-hour
standard, the State must submit a SIP
revision that meets the RACT
requirements of section 184 of the CAA
for each area in the OTR that is
designated as attainment or
unclassifiable or that may be classified
marginal, or that is under § 51.904 of
this subpart. A major stationary source
for these areas is defined as a source
which directly emits, or has the
potential to emit, 100 tpy or more of
NOX or 50 tpy or more of VOC. For any
areas in the OTR, the State is required
to submit the RACT revision no later
than September 16, 2006 (27 months
after designation for the 8-hour NAAQS)
and must provide for implementation of
RACT as expeditiously as practicable
but no later than May 1, 2009 (first day
of the first ozone season that is 30
months after the RACT SIP is due).
We believe that this does not result in
any new regulatory requirements for any
area in the OTR because these
regulatory requirements are not
associated with an area’s designation or
classification and already apply
regionwide under the 1-hour ozone
standard. If a new OTR is established for
purposes of the 8-hour standard
pursuant to section 176A, that area
would also be subject to the provisions
and control requirements of section 184.
3. Comments and Responses
Comments: The EPA received two
comments supporting our interpretation
of section 184 with regard to the 8-hour
standard. One commenter further
asserted that for any areas that might be
added to the OTR, or for any new OTR,
if modeling shows that the control
requirements from section 184 are not
appropriate and should not be required,
then EPA has the discretion to exempt
such areas from those requirements. The
commenter pointed to a portion of the
decision in Alabama Power v. Costle,
636 F. 2d. 323 (D.C. Circuit, 1979).
Response: Regarding the comment
about modeling, we are not prepared to
determine whether the de minimis
doctrine established by the court in
Alabama Power would be available in
the situation the commenter describes.
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As the court in that case explained, such
a determination would first require EPA
to assess whether Congress, in enacting
section 184 of the CAA, was so
prescriptive as to foreclose granting
such waivers. Since that issue of
statutory interpretation for the described
situation is not presently before the
Agency, EPA is not addressing whether
de minimis authority exists under
section 184.
[Section VI.T. of June 2, 2003
proposed rule (68 FR 32855); no draft or
final regulatory text.]
1. Background
In the proposal, we noted that section
172(c)(6) requires nonattainment SIPs to
‘‘include enforceable emission
limitations, and such other control
measures, means or techniques * * * as
well as schedules and timetables for
compliance, as may be necessary or
appropriate to provide for attainment
* * *’’ We also noted that the current
guidance, ‘‘Guidance on Preparing
Enforceable Regulations and
Compliance Programs for the 15 Percent
Rate-of-Progress Plans (EPA–452/R–93–
005, June 1993)’’ is relevant to rules
adopted for SIPs under the 8-hour ozone
NAAQS and should be consulted for
purposes of developing appropriate
nonattainment plan provisions under
section 172(c)(6). We proposed no
specific regulatory provisions related to
compliance and enforcement.
2. Summary of Final Rule
As in the proposal, we are not setting
forth any additional regulatory text
related to compliance and enforcement.
3. Comments and Responses
We received no comments on the
proposed approach of handling
enforcement and compliance provisions
related to SIPs for the 8-hour ozone
standard.
O. What requirements should apply to
emergency episodes?
[Section VI.U. of June 2, 2003
proposed rule (68 FR 32856); no draft or
final regulatory text.]
1. Background
In the June 2, 2003 proposal, we noted
that subpart H of 40 CFR part 51
specifies requirements for SIPs to
address emergency air pollution
episodes and for preventing air
pollutant levels from reaching levels
determined to cause significant harm to
the health of persons. We noted that we
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2. Summary of Final Rule
We have not yet proposed any rule
revision related to emergency episodes,
and the final rule below does not
contain any such rule revision.
3. Comments and Responses
We received no comments on this
aspect of the proposal.
N. Are there any additional
requirements related to enforcement
and compliance?
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anticipate proposing a separate
rulemaking in the future to update
portions of that rule.
P. What ambient monitoring
requirements will apply under the 8hour ozone NAAQS?
[Section VI.V. of June 2, 2003
proposed rule (68 FR 32856); no draft or
final regulatory text.]
1. Background
Ozone monitoring data play an
important role in designations, control
strategy development, and related
implementation activities. We did not
propose any revisions to current
ambient monitoring requirements listed
in 40 CFR part 58.
We indicated in the proposal that we
do plan to modify the existing ozone
monitoring requirements in a separate
rulemaking as part of implementation of
the National Ambient Air Monitoring
Strategy (NAAMS), including adoption
of a national strategy introducing
national core monitoring sites (NCore)
as a replacement for traditional national
air monitoring stations/State and local
air monitoring stations (NAMS/SLAMS)
monitoring currently codified at 40 CFR
part 58. Part of the NCore network
would include the existing ozone
monitoring sites that currently support
the NAAQS-related activities. The
regulatory modifications are expected to
include ozone monitoring requirements
based upon the population of an area
and its historical/forecasted ozone air
quality values.
We indicated in the proposal that as
part of ongoing air quality monitoring
network assessments (outside the scope
of this present rulemaking), each State,
local, and Tribal air monitoring agency
is being asked to assess the adequacy of
its air pollution monitoring networks,
including those sites that measure
ozone. We said we would work with
these agencies to develop network plans
to ensure approval of all network
designs. It is expected that the number
and location of the original sites will be
very similar to the current network.
However, on a local basis, there will be
some relocation, addition, and removal
of ozone sites as a result of regional
network assessments.
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71669
In addition, we stated that we
anticipate that we will include a
requirement for measuring multiple air
pollutants, including ozone precursors
at select locations. The NCore sites are
expected to include high-sensitivity
nitrogen oxide (NO) and total reactive
oxides of nitrogen (NOy) measurements
at locations across the nation to support
the tracking of emission reduction
strategy efforts such as the NOX SIP
Call, the CAIR and, if created, a statute
codifying the Administration’s Clear
Skies Act, which addresses NOX
reductions across the nation.
Section 182(c)(1) of the CAA requires
that enhanced ozone (e.g., precursor)
monitoring be conducted in any ozone
nonattainment area classified as serious,
severe, or extreme. Our regulations
reflecting the statutory requirements are
found at 40 CFR part 58. This is known
as the Photochemical Assessment
Monitoring Stations (PAMS) program.
The proposal noted that the PAMS
monitoring requirements (referred to as
‘‘enhanced monitoring’’ under section
182(c)(1) of the CAA) are retained in
areas designated as 1-hour ozone
serious, severe, and extreme
nonattainment areas. Areas that are
designated serious or above under the 8hour ozone NAAQS are not currently
addressed in 40 CFR part 58 for ozone
precursor monitoring, although such
areas are subject to the section 182(c)(1)
provision. We anticipated that the
revisions to the monitoring regulations
would also cover all areas that are
classified as serious or above for the 8hour NAAQS, including any area that is
bumped up to serious or above for the
8-hour NAAQS.
2. Summary of Final Rule
There is no change from the proposal.
No monitoring requirements are being
promulgated as part of this rulemaking.
EPA still expects to separately propose
a number of amendments to the
monitoring requirements, along the
lines described above, in December
2005.
3. Comments and Responses
Comment: One commenter noted that
the NAAMS, which will likely influence
the future of the ozone monitoring
network, is based on the presumption
that less criteria pollutant monitoring is
needed and that resources must be
shifted into measures that support other
analyses. The commenter pointed out
that many States have already curtailed
their criteria pollutant monitoring
networks in order to meet program
requirements. The commenter argued
that we should support and maintain
the ozone monitoring network since the
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data is used as the basis of attainment
determinations and the tracking of
progress.
Response: While we did discuss some
aspects of the NAAMS in the proposed
rule, this rulemaking effort does not
affect the ambient monitoring
requirements listed in 40 CFR part 58.
As such, comments on the NAAMS are
not germane to this action. As noted
above, we are working on a separate
rulemaking effort to amend the ambient
monitoring requirements. Commenters
should raise any concerns they have
regarding the NAAMS during the
comment period on that action.
We recognize that ozone continues to
pose a significant environmental threat.
The NAAMS does not recommend
curtailing ozone monitoring, but rather
recommends that State and local
agencies perform assessments of their
ozone networks to assure that the
available resources are used to
maximum benefit. We do not foresee
significant changes to the existing ozone
network as a result of these assessments.
The NAAMS does recommend that
resources be shifted from criteria
pollutant monitoring to other
monitoring initiatives (e.g., air toxics)
for those criteria pollutants whose
ambient concentrations are well below
their respective NAAQS. Specifically,
the strategy recommends significant
reductions in total suspended
particulate (TSP), PM10, SO2, CO and
NO2 monitoring.
Comment: Two commenters
questioned the appropriateness of
making high sensitivity NOX and CO
measurements at NCore Level 2 sites
which may be in urban areas.
Response: This rulemaking effort does
not affect the ambient monitoring
requirements listed in 40 CFR part 58.
As such, comments on the
appropriateness of making high
sensitivity NOX and CO measurements
in urban areas are not germane to this
action.
Comment: One commenter urged the
continued support of the PAMS
program. The commenter points out that
the PAMS’ data has been used to
evaluate (and improve) emissions
inventories, apply observation-based
models, evaluate photochemical gridbased models, and assess effectiveness
of control programs. The commenter
argues that while fine-tuning the PAMS
requirements may be appropriate, the
program should be maintained.
Response: As part of the antibacksliding provisions of the Phase 1
rule, the PAMS monitoring
requirements are retained in areas
designated as 1-hour ozone serious,
severe, and extreme nonattainment
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areas at the time of a designation of
nonattainment for the 8-hour standard.
[See 40 CFR 51.900(f)(9)]. In addition,
areas that are designated serious or
above under the 8-hour ozone NAAQS
will also be required to comply with the
PAMS monitoring requirements. Also, if
an area is bumped up to serious or
above for the 8-hour NAAQS, it would
be required to conduct the appropriate
PAMS monitoring.
Currently, 40 CFR part 58 does not
specifically apply to areas for purposes
of the 8-hour standard. As discussed
above, we are working on a separate
rulemaking effort to amend the ambient
monitoring requirements. We expect
these revisions to ensure that all areas
that are classified as serious or above for
the 8-hour NAAQS are covered by the
PAMS regulations. However, even in the
absence of the applicability of these
regulations, the enhanced monitoring
requirement of section 182(c)(1) applies.
Q. When will EPA require 8-hour
attainment demonstration SIP
submissions?
[Section VI.W. of June 2, 2003
proposed rule (68 FR 32856); § 51.908(e)
in draft regulatory text and § 51.908(d)
of final regulatory text.]
1. Background
In the June 2, 2003 action, we
proposed that required attainment
demonstrations, which will be based on
photochemical grid modeling for all
areas must be submitted within 3 years
after designation. However, we
proposed that a subpart 1 area that
desires an attainment date within 3
years after designation would have to
provide a demonstration within 1 year
after designation.
We noted that the proposed time of
submission is expected to result in as
close as possible a synchronization of
the 8-hour ozone and PM2.5 attainment
demonstration SIP submittal dates.
2. Summary of Final Rule
The final rule provides that
attainment demonstrations—where
required—must be submitted within 3
years after the effective date of the area’s
nonattainment designation. As noted in
section IV.D.1. above, the final rule does
have a separate provision addressing
submission of an early attainment
demonstration.
On June 18, 2004 (69 FR 34076), EPA
announced it was reconsidering the
boundaries of the Las Vegas, NV, 8-hour
ozone nonattainment area. The EPA
deferred the effective date of the
designation until September 13, 2004,
and that this reconsideration would not
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affect the time SIPs would be due for the
Clark County nonattainment area.
3. Comments and Responses
Comment: Several commenters
believed some areas would need longer
than 3 years to submit their attainment
demonstration. At least one of these
commenters noted that section 182(c)(2)
allows up to 4 years (rather than 3 years)
for submission of a modeled attainment
demonstration for serious and above
areas. One commenter recommended
that EPA should consider extending
attainment-modeling deadlines for
nonattainment areas that are not
currently contained within the 1-hour
boundary, but will now be included in
the 8-hour boundary. At least one
commenter agreed with the timing we
proposed.
Response: For the reasons stated in
the proposal, we believe it is
appropriate to require that the modeled
attainment demonstrations be submitted
within 3 years after designation. In
addition, we note the following:
• In general, the CAA requires these
submissions no later than 3 years
following designation. See sections
172(b) and 182(b) of the CAA. At the
time of enactment of the CAA
Amendments of 1990, Congress allowed
areas that used the recently developed
and complex photochemical grid model
an extra year (4 years rather than 3
years) to submit their attainment
demonstration. Photochemical grid
modeling is now a process more familiar
to users for purposes of developing
attainment demonstrations, and all areas
will be using these models for purposes
of their attainment demonstrations and
can be completed with the time frame
established in this rule. There is no
distinction between the tools used for
attainment modeling that would justify
additional time for these areas to submit
attainment demonstrations. Further,
where appropriate, existing modeling
exercises (e.g., regional analyses, RPO
analyses, older 1-hour analyses) may be
leveraged for use in certain cases. In
most cases, it will not be necessary to
conduct a modeling exercise ‘‘from
scratch.’’
• We do not believe it is appropriate
or desirable to require States to submit
attainment demonstrations for areas
designated nonattainment under the 8hour standard at different times for
different areas. We recognize that
photochemical grid modeling—required
by the CAA for interstate moderate
nonattainment areas, as well as serious
and higher—classified areas—will be
performed on large enough scales to
address transport and will in most cases
encompass a number of nonattainment
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areas. These numerous nonattainment
areas may differ by classification (some
areas may be intrastate moderate areas,
some interstate moderate areas, and
others serious and above nonattainment
areas). Some areas that may require
attainment demonstrations may be
subject to subpart 1 while others may be
subject to subpart 2.
• The control strategies that may be
modeled for all the areas in the
modeling domain will likely be
modeled simultaneously, especially if
all the areas are located in a single State.
• We also note that an area’s RFP
plan and the RACM demonstration
under section 172(c)(1) are due within
3 years after designation. For the
reasons stated in sections describing
those requirements, it is appropriate
that the attainment demonstration, the
RFP plan, and the RACM demonstration
be submitted at the same time.
In light of these reasons, we do not
believe it is consistent with the CAA
and reasonable to require submission of
attainment demonstrations no later than
3 years following designation.
Although we proposed that subpart 1
areas requesting an attainment date
within 3 years after designation should
submit their attainment demonstration
within 12 months, the final rule does
not include such a provision (see
section IV.D.1 above for a further
discussion of this).
R. How will the statutory time periods
in the CAA be addressed when we
redesignate areas to nonattainment
following initial designations for the 8hour NAAQS?
[Section VI.B. of June 2, 2003
proposed rule (68 FR 32816); § 51.906 in
draft and final regulatory text.]
1. Background
We noted in the proposal that section
181(b) of the CAA provides that for
areas designated attainment or
unclassifiable for ozone immediately
following enactment of the 1990 CAA
Amendments and subsequently
redesignated to nonattainment, the
period to the maximum statutory
attainment date would run from the date
the area is classified under subpart 2.89
Thus, if an area designated as
attainment for the 1-hour ozone
standard in 1990 was redesignated to
nonattainment for the 1-hour ozone
89 Section 181(b) provides that ‘‘any absolute,
fixed date applicable in connection with any such
requirement is extended by operation of law by a
period equal to the length of time between the date
of enactment of the CAAA of 1990 and the date the
area is classified under this paragraph.’’ Under
section 181(b), the date of classification is the same
as the date of redesignation to nonattainment.
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standard in January 2002 and classified
as moderate, the area’s 1-hour
attainment date would be no later than
6 years following January 2002, i.e.,
January 2008. Section 172(a)(2) of the
CAA provides for attainment dates to be
calculated from the time the area is
designated nonattainment.
We also noted in the proposal that
most of the SIP submittal dates in
subpart 2 are set as a fixed period from
the date of enactment of the 1990 CAA
Amendments, which was also the date
of designation and classification by
operation of law for most subpart 2
areas. Section 181(b)(1) of the CAA
provides that any fixed dates applicable
in connection with any such
requirements under section 110, subpart
1 and subpart 2 will be extended by
operation of law to a period equal to the
length of time between the date of
enactment of the 1990 CAA
Amendments and the date that an area
is subsequently designated and
classified.
2. Final Rule
We are adopting the approach set
forth in the proposed rule. For any area
that is initially designated attainment or
unclassifiable for the 8-hour NAAQS
and subsequently redesignated to
nonattainment for the 8-hour ozone
NAAQS, the periods for the attainment
date and dates for submittal of any
applicable requirements under subpart 1
or subpart 2 would run from the date of
redesignation to nonattainment of the 8hour NAAQS. This is consistent with
section 181(b), which gives areas
redesignated to nonattainment the same
amount of time to submit plans and to
attain the standard as areas initially
designated nonattainment.
3. Comments and Responses
Comment: One commenter asked
what the reasoning was behind the time
period extension and if this is an
attempt to provide equity, based on the
wording of the draft regulatory text.
Response: As stated above, section
181(b)(1) of the CAA provides for
extending by operation of law any
absolute, fixed date applicable in
connection with a nonattainment
requirement by a period equal to the
length of time between the date of
enactment of the CAA Amendments of
1990 and the date the area is classified
and redesignated as nonattainment.
Thus, an area redesignated to
nonattainment for the 1-hour standard
and classified as moderate would have
been given 3 years to submit an
attainment demonstration and up to 6
years to attain, which are the same time
periods given to an area designated
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71671
nonattainment and classified by
operation of law at the time of the 1990
CAA Amendments. Since it does not
make sense to run deadlines from the
date of the CAA Amendments of 1990,
we have adopted an approach consistent
with the intent of that section—that the
statutory time periods run from the date
of redesignation to nonattainment.
V. EPA’s Final Rule for New Source
Review
A. Background
1. The Major NSR Program
The major NSR program contained in
parts C and D of title I of the CAA is
a preconstruction review and permitting
program applicable to new and
modified major stationary sources of air
pollutants regulated under the CAA. In
areas not meeting health-based NAAQS
and in OTRs, the program is
implemented under the requirements of
section 110(a)(2)(C) and part D of title I
of the CAA. We call this program the
‘‘nonattainment’’ major NSR program.
Subpart 1 of part D of title I contains
general requirements for nonattainment
areas for any criteria pollutant and
subpart 2 contains provisions
specifically for ozone nonattainment
areas. Subparts 3 and 4 contain
provisions specifically for CO monoxide
and PM10, respectively. In Whitman v.
American Trucking Associations, [531
U.S. 457, 482–86 (2001)], the Supreme
Court reviewed EPA’s implementation
strategy for the revised 8-hour ozone
NAAQS, and remanded it to EPA to
develop a reasonable resolution of the
roles of subparts 1 and 2 in classifying
areas for and implementing the revised
ozone standard.90
In areas meeting the NAAQS
(‘‘attainment’’ areas) or for which there
is insufficient information to determine
whether they meet the NAAQS
(‘‘unclassifiable’’ areas), the NSR
requirements under part C of title I of
the CAA apply. We call this program the
PSD program. Collectively, we also
commonly refer to the attainment and
nonattainment programs as the major
NSR program. These regulations are
contained in 40 CFR 51.165, 51.166,
52.21, 52.24, and part 51, appendix S.
Of these, the nonattainment area
regulations are contained in 40 CFR
51.165, 52.24, and part 51, appendix S.
The major NSR provisions of the CAA
are implemented primarily through SIPapproved State preconstruction
permitting programs. As provided in
section 172(c)(5) of the CAA, the SIP
90 For a more complete discussion of this decision
and its implications, see 69 FR 23956; April 30,
2004.
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must require permits for the
construction and operation of new or
modified major stationary sources in
accordance with section 173 of the
CAA. Subpart 2 of title I of the CAA sets
forth additional SIP requirements for
ozone nonattainment areas, including
preconstruction permitting
requirements.91
The minimum permitting
requirements States must meet before
EPA can approve a State’s
nonattainment major NSR program into
a SIP are found in part D of title I and
40 CFR 51.165. However, some States
are lacking a SIP-approved major NSR
program for the 8-hour ozone NAAQS.
This may be because the State has never
had a nonattainment area in which it
needed to apply a nonattainment NSR
program or because the approved
program does not apply to an 8-hour
ozone nonattainment area. As discussed
in section V.D of this preamble, EPA is
providing States 3 years to develop and
submit an approvable nonattainment
major NSR program for the 8-hour
NAAQS. The regulations at 40 CFR
52.24(k) specify that appendix S governs
permits to construct and operate in a
nonattainment area or in any area
designated under section 107(d) of the
CAA as attainment or unclassifiable for
ozone that is located in an OTR that a
source applies for during this SIP
development period (the interim period
between the effective date of
designations and the date that EPA
approves a nonattainment major NSR
program).
Appendix S is an interpretation of 40
CFR subpart I (including § 51.165), and
has historically reflected substantially
the same requirements as those in
§ 51.165, subject to a limited exemption
in section VI. This includes the
requirement that a source comply with
LAER and obtain offsetting emissions
reductions. Pursuant to section 52.24(k),
where necessary, appendix S governs
nonattainment major NSR permitting of
ozone precursors in 8-hour ozone
nonattainment areas and all areas
within the OTR, including areas
designated attainment/unclassifiable,
during the SIP development period.
Thus, consistent with section
110(a)(2)(C), permitting of new and
modified stationary sources in the area
will be regulated as necessary to ensure
that the NAAQS are achieved.
As we describe further in section
V.A.2 of this preamble, today’s final
regulations were proposed as part of two
91 In some cases, subpart 1 and subpart 2
requirements are inconsistent or overlap. To the
extent that subpart 2 addresses a specific obligation,
the provisions in subpart 2 control (68 FR 32811;
June 2, 2003).
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different regulatory packages. On July
23, 1996 (61 FR 38250), we proposed
changes to the major NSR program,
including codification of the
requirements of part D of title I of the
1990 CAA Amendments.92 On June 2,
2003 (68 FR 32802), we proposed a rule
to implement the 8-hour ozone NAAQS.
On April 30, 2004, we promulgated the
Phase 1 final rule and you will find a
summary of the regulatory development
process and stakeholder development
for that rulemaking at 69 FR 23951.
2. What We Proposed
a. Proposed Changes to Incorporate the
1990 CAA Amendments
On July 23, 1996 (61 FR 38250), we
proposed changes to § 51.165 and
appendix S to incorporate requirements
in part D of title I of the 1990 CAA
Amendments for ozone, CO, and PM10
nonattainment areas. Concerning ozone,
we proposed (among other things) to
codify the following provisions from
section 182 of the CAA:
• Major stationary source thresholds
(ranging from 10 to 100 tpy, depending
on classification),
• Significant emission rates (ranging
from 0 to 25 tpy),
• Offset ratios (ranging from 1.1:1 to
1.5:1), and
• Special modification provisions
implementing CAA sections 182(c), (d),
and (e) for serious, severe, and extreme
ozone nonattainment areas.
In the 1996 proposal, we proposed
that the major stationary source
thresholds and offset ratios of CAA
section 182 (subpart 2 of part D) would
apply to all major stationary sources of
VOC and NOX to implement major NSR
under the 1-hour ozone NAAQS. This
proposal is consistent with the 1991 and
1992 Transition Policy Memos
explaining major NSR requirements
under the 1990 CAA Amendments.93
These memos also explained that
permits must comply with the new
statutory requirements for major NSR
under the 1-hour NAAQS after the
deadlines set by Congress, regardless of
92 On December 31, 2002, we finalized five
actions from that proposal related to the
applicability of the NSR regulations. For a summary
of the regulatory development process and
stakeholder development for that rulemaking, see
67 FR 80188.
93 John S. Seitz, ‘‘New Source Review (NSR)
Program Transitional Guidance,’’ March 11, 1991.
We provided additional transitional guidance for
nonattainment areas in our September 3, 1992
memorandum, New Source Review (NSR) Program
Supplemental Transitional Guidance on
Applicability of New Part D NSR Permit
Requirements, from John S. Seitz, Director, Office
of Air Quality Planning and Standards.
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the delay in incorporating them into
SIPs.
Our 1996 proposal predated
promulgation of the 8-hour ozone
NAAQS and thus did not explain the
details of implementation of these
standards under § 51.165 or appendix S.
For a discussion of implementation of
the 1-hour and 8-hour ozone NAAQS
under § 51.165 and appendix S, see
section V.D. of this preamble.
Also, in our 1996 action, and then
again in our June 2, 2003 action, we
proposed to amend our nonattainment
NSR provisions to expressly include
NOX as an ozone precursor in
nonattainment major NSR programs (61
FR 38297, 68 FR 32847). We also
proposed that, as provided under CAA
section 182(f), a waiver from
nonattainment NSR for NOX as an ozone
precursor would be available for both
subpart 1 and subpart 2 areas (68 FR
32846).
On June 2, 2003, we proposed a rule
to identify the statutory requirements
that apply for purposes of developing
SIPs under the CAA to implement the
8-hour ozone NAAQS (68 FR 32802).
Specifically, we proposed two optionsone in which all nonattainment areas
would be classified and regulated under
subpart 2 of part D of title I, and one in
which some nonattainment areas would
be regulated under the less restrictive
requirements of subpart 1 and some
would be classified and regulated under
subpart 2. For areas classified under
subpart 2—those with a 1-hour ozone
design value at or above 0.121 ppm—the
classifications set forth in subpart 2
(marginal, moderate, etc.) would govern
part D SIPs for the 8-hour ozone
standard, with each area’s classification
determined by a modified version of the
subpart 2 classification table containing
1-hour design values and translated 8hour design values for each
classification. The NSR permitting
requirements for the 8-hour ozone
standard necessarily follow from the
classification scheme chosen under the
terms of subpart 1 and subpart 2. We
did not propose specific regulatory
language for implementation of NSR
under the 8-hour NAAQS. However, we
indicated that we intended to revise the
nonattainment NSR regulations to be
consistent with the rule for
implementing the 8-hour ozone NAAQS
(68 FR 32844).
Concerning CO, in 1996 we proposed
the following:
• Major stationary source threshold of
50 tpy for serious nonattainment areas
in which the Administrator has
determined that stationary sources are
significant contributors to CO levels,
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• Significant emission rate of 50 tpy
for serious nonattainment areas in
which the Administrator has
determined that stationary sources are
significant contributors to CO levels.
Concerning PM10, in 1996, we
proposed to amend our nonattainment
NSR regulations to incorporate
requirements of the 1990 CAA
Amendments and establish significant
emission rates. Specifically, we
proposed the following:
• Major stationary source threshold of
100 tpy PM10 or any specific PM10
precursor in moderate PM10
nonattainment areas,
• Major stationary source threshold of
70 tpy PM10 or any specific PM10
precursor in serious PM10
nonattainment areas, and
• Significant emission rate of 15 tpy
PM10 and 40 tpy PM10 precursors.
b. Proposed Changes To Criteria for
Emission Reduction Credits From
Shutdowns and Curtailments
In 1996 we proposed to revise the
regulations limiting offsets from
emissions reductions due to shutting
down an existing source or curtailing
production or operating hours below
baseline levels (‘‘shutdowns/
curtailments’’). The prior regulations at
§ 51.165(a)(3)(ii)(C) provided that such
emissions reductions could be used as
offsets if the State lacked an approved
attainment demonstration, unless the
shutdown/curtailment occurred after
the date the new source permit
application was filed or the applicant
could establish that the proposed new
source is a replacement for the
shutdown/curtailed source. We
proposed to revise the existing
provisions for crediting emissions
reductions by restructuring existing
§ 51.165(a)(3)(ii)(C)(1) and (2) for clarity
without changing the current
requirements therein. [See proposed
§ 51.165 (a)(3)(ii)(C)(1) through (4)]. We
also proposed substantive revisions in
two alternatives that would ease, under
certain circumstances, the existing
restrictions on the use of emission
reduction credits from source
shutdowns and curtailments as offsets.
We explained that easing the
restrictions may be warranted by the
1990 CAA Amendments, in which
Congress significantly reworked the
attainment planning requirements of
part D of title I of the CAA such that an
approved attainment demonstration is
unnecessary.
The revised CAA emphasizes the
emission inventory as the first
requirement in planning, includes new
provisions keyed to the inventory
requirements, and mandates several
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adverse consequences for States that fail
to meet the planning or emissions
reductions requirements related to
inventories.94 In 1993, we issued a
policy memorandum addressing the use
of shutdown credits for offsets in ozone
nonattainment areas and areas in the
OTR in light of the new statutory
requirements.95 According to our
longstanding policy, we emphasized
that sources may use emission reduction
credits generated from shutdowns and
curtailments as offsets if the State
continues to include the emissions in
the emissions inventory for attainment
demonstration and RFP milestone
purposes. We proposed two alternatives
to revise the regulations that limit a
source’s use of emissions reductions as
offsets if the reductions were achieved
by shutting down an existing emissions
unit or curtailing production or
operating hours of a unit (shutdowns/
curtailments).
Under Alternative 1, we proposed to
allow emissions reductions from
shutdowns and curtailments from
sources located in ozone nonattainment
areas that lack an EPA-approved
attainment demonstration to be used as
offsets or netting credits, if the
emissions reductions occur after
November 15, 1990 and the area is
current with part D ozone
nonattainment planning requirements.
See proposed § 51.165(a)(3)(ii)(C)(5) and
(6) [Alternative 1]. Proposed Alternative
2 generally would have allowed
emissions reductions from source
shutdowns and source curtailments in
all nonattainment areas and for all
pollutants to be used as offsets or
netting credits when such reductions
occur after the base year of the
emissions inventory for that pollutant.
See proposed § 51.165(a)(3)(ii)(C)(5)
[Alternative 2]. The 1996 proposal
retained the provision that the
permitting authority may consider the
shutdown or curtailment to have
occurred after the date of its most recent
emissions inventory if the inventory
explicitly includes as current existing
emissions the emissions from such
previously shutdown or curtailed
sources.
c. Proposed Changes to Revise the
Construction Ban Provisions
On July 23, 1996, we proposed to
revise § 52.24(a) to incorporate changes
made by the 1990 CAA Amendments
94 For a complete discussion of how the 1990
CAA Amendments attainment planning
requirements relate to shutdown/curtailment
credits (61 FR 38311; July 23, 1996).
95 Use of Shutdoen Credits for Offsets, July 21,
1993, John S. Seitz, Director, Office of Air Quality
Planning and Standards.
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71673
related to the applicability of
construction bans. Under the 1977
Amendments, section 110(a)(2)(I) of the
CAA required EPA to place certain areas
under a federally imposed construction
moratorium (ban) that prohibited the
construction of new or modified major
stationary sources in nonattainment
areas where the State failed to have an
implementation plan meeting all of the
requirements of part D. The 1990 CAA
Amendments removed these provisions
from the CAA. However, in section
110(n)(3) of the CAA (Savings Clause),
the 1990 CAA Amendments retained the
prohibition in cases where it was
applied prior to the 1990 CAA
Amendments based upon a finding by
the Administrator that the area: (1)
Lacked an adequate NSR permitting
program (as required by section
172(b)(6) of the 1977 CAA); or (2) the
State plan failed to achieve the timely
attainment of the NAAQS for SO2 by
December 31, 1982. All other
construction bans pursuant to section
110(a)(2)(I) are lifted as a result of the
new statutory provision. This includes
previously imposed construction bans
based upon a finding that the plan for
the area did not demonstrate timely
attainment and maintenance of the
ozone or CO NAAQS. In accordance
with the amended section 110(n)(3) of
the CAA, any remaining construction
ban continues in effect until the
Administrator determines that the SIP
meets either the amended part D permit
requirements, or the requirements under
subpart 5 of part D for attainment of the
NAAQS for SO2, as applicable.
We note that § 52.24(k) was not
retained in our proposed rule text.
However, the preamble did not in any
manner indicate that EPA believed that
NSR permits complying with appendix
S were not required during the SIP
development period where necessary.
To clarify our intent, our proposed 8hour ozone NAAQS implementation
rule explained that § 52.24(k) remained
in effect and would be retained. In that
action, we also proposed that we would
revise § 52.24(k) to reflect the changes in
the 1990 CAA Amendments (68 FR
32846). The prior language at section
52.24(k) allowed States to issue permits
under appendix S for a maximum
period of 18 months after designation.
After this time, if the nonattainment
area did not have an approved part D
NSR permit program, the construction
ban would apply. However, the 1990
CAA Amendments to the construction
ban provisions altered the provisions of
the construction ban such that it would
not apply when a State lacked an
approved part D NSR program in the
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future. Thus, the 1990 CAA
Amendments supersede that portion of
prior § 52.24 dealing with the
construction ban but leave unaltered the
requirement that appendix S continues
to apply through § 52.24(k). We
explained that we have interpreted this
language to allow States or EPA to issue
permits under appendix S from
designation to approval even if the time
period between designation and
approval exceeds 18 months, and
proposed to revise § 52.24(k) to properly
reflect this interpretation.
We also proposed regulatory text to
reflect the revisions to CAA section
173(a)(4). Before the State can issue a
nonattainment major NSR permit, the
reviewing authority must first find
pursuant to section 173(a)(4) that the
‘‘Administrator has not determined that
the applicable implementation plan is
not being adequately implemented for
the nonattainment area’’ in accordance
with the requirements of part D. We
stated our intent to make this
determination by sending a letter to the
permitting authority, and publishing a
subsequent action in the Federal
Register, but we solicited comment on
the need to undertake notice-andcomment procedures before taking final
action.
Section 113(a)(5) of the CAA provides
that EPA may issue an order prohibiting
the construction or modification of any
major stationary source in any area,
including an attainment area, where the
Administrator finds that the State is not
in compliance with the NSR
requirements. Specifically, EPA may
issue an order under section 113(a)(5)
banning construction in an area
whenever the Administrator finds that a
State is not acting in compliance with
any requirement or prohibition of the
CAA relating to construction of new
sources or the modification of existing
sources. To codify the requirements of
section 113(a)(5), we proposed new
language in § 52.24(c).
We proposed to remove the transition
provisions under existing § 52.24(c) and
(g). These paragraphs were proposed to
be removed because they were
originally designed to clarify the
applicable requirements for permits
issued prior to the initial SIP revisions
required by the 1977 CAA
Amendments.
In addition to the significant changes
already discussed, we proposed several
minor changes to § 52.24. These minor
changes included: (1) The addition of
requirements applicable to transport
regions; (2) the inclusion of
requirements applicable to criteria
pollutant precursors; (3) incorporation
of the definitions proposed in
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§ 51.165(a); (4) revisions to the language
at § 52.24(h)(2); and (5) revisions to
§ 52.24(j).
d. Proposed Changes on Applicability of
Appendix S and the Transitional NSR
Program
On June 2, 2003 (68 FR 32802), we
explained implementation of the major
NSR program under the 8-hour ozone
NAAQS during the SIP development
period, and proposed flexible NSR
requirements for areas that expected to
attain the 8-hour NAAQS within 3 years
after designation. We stated that the
existing regulation codified at 40 CFR
§ 52.24(k) requires that permits be
issued in compliance with appendix S
during this time, and that a State would
have to continue implementing part D
nonattainment requirements under
appendix S unless the source was
eligible for flexibility under section VI
of the appendix (68 FR 32846–48).
Our June 2, 2003 proposal would
limit the circumstances under which
section VI of appendix S applies (68 FR
32844). Under the existing regulatory
structure of section VI, major new
sources and major modifications located
in nonattainment areas for which the
attainment date has not yet passed may
avoid the requirement to comply with
LAER and obtain source-specific offsets
if the new emissions will not interfere
with an area’s ability to reach
attainment by its attainment date.
Because we believed that most new
emissions in 8-hour nonattainment
areas would generally not meet this
criteria of non-interference, we
proposed to apply section VI only in
areas that qualify for a ‘‘transitional
classification’’ (68 FR 32846).
Accordingly, we called this revised
section VI the Transitional NSR
Program. We proposed that the program
would apply only in nonattainment
areas that: (1) Are attaining the 1-hour
NAAQS; (2) are subject to subpart 1
(rather than subpart 2) of part D of title
I; (3) for which the State submitted an
attainment plan by April 15, 2004 that
demonstrates attainment within 3 years
after designation; (4) and for which the
State submitted an attainment plan
containing any additional local control
measures needed for attainment of the
8-hour standard (68 FR 32847). We also
proposed that the sources using section
VI would be required to comply with
BACT.
On August 6, 2003 (68 FR 46536), we
solicited comment on additional options
for implementing major NSR under the
8-hour NAAQS, including a major
rewrite of appendix S that would
include the proposed changes to section
VI. We also solicited comment on two
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alternatives to appendix S for
implementing NSR in newly designated
nonattainment areas during the
transitional SIP development period.
One alternative was a Federal part D
NSR regulatory program for major new
and modified sources, to be codified at
40 CFR 52.10, under which EPA would
be responsible for permitting unless a
State took delegation of the program.
The other alternative was application of
the Federal PSD program at 40 CFR
52.21 in such newly designated
nonattainment areas. Commenters stated
that neither of those alternatives was
sufficiently developed for public
comment, and we have not pursued
them further.
One other proposal affects appendix S
applicability. In 1978 (43 FR 26408;
June 19, 1978) and 1979 (44 FR 3276;
January 16, 1979), we proposed that
applicability under PSD and appendix S
respectively be based on uncontrolled
emissions, but sources would be exempt
from control requirements unless the
increase in allowable emissions was at
least 50 tpy, 1,000 pounds per day, or
100 pounds per hour. The U.S. Court of
Appeals for the District of Columbia
Circuit, however, ruled that major
source applicability should be based on
potential to emit, rather than
uncontrolled emissions. Alabama Power
Co. v. Costle, 606 F.2d 1068 (D.C.
Circuit, 1979), amended 636 F. 3d 323,
356–57 (D.C. Circuit, 1980). The court
also ruled that EPA had exceeded its
authority in establishing the 50 tpy
exemption and remanded the exemption
for reconsideration. In response, we
proposed removing the 50 tpy
exemption from the PSD rules and
appendix S in the 1979 Notice of
Proposed Rulemaking (NPRM) (44 FR
51930). We finalized these changes in
1980, but we inadvertently did not
remove the change in all the places in
appendix S where it was located,
specifically footnotes 5 and 8 to IV.D.
e. Proposed Changes To Identify NOX as
an Ozone Precursor in Attainment and
Unclassifiable Areas
Currently, only VOCs are expressly
regulated as ozone precursors under the
PSD regulations. Recognizing the role of
NOX in ozone formation and transport,
we proposed to amend our PSD
regulations to expressly include NOX as
an ozone precursor in attainment and
unclassifiable areas. Moreover, we
proposed to require States to modify
their existing programs to include NOX
as an ozone precursor in these areas (68
FR 32846).
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B. Summary of Final Rule and Legal
Basis
1. Final Action and Legal Basis for
Changes to Incorporate the 1990 CAA
Amendments
a. Final Changes to Incorporate the 1990
CAA Amendments
In today’s final action, we revised
§ 51.165 and appendix S to incorporate
the major stationary source thresholds,
significant emission rates, and offset
ratios for sources of ozone precursors
pursuant to part D, subpart 1 and
subpart 2 of title I of the 1990 CAA
Amendments. [See § 51.165(a)(1)(iv),
(a)(1)(v), (a)(1)(x), (a)(8), (a)(9) and
section II. A. 4, 5, and 10 and section
IV.G and H of appendix S.] Accordingly,
consistent with statutory requirements
and the final rules in 40 CFR part 51,
subpart X (Provisions for
Implementation of 8-hour Ozone
NAAQS), today’s final rules in § 51.165
require States’ part D NSR SIPs
implementing the 8-hour ozone
standard to include provisions meeting
subpart 1 of part D of the CAA, and
subpart 2 as applicable, based on the
area’s classification. (We note 40 CFR
part 51, subpart X includes the specific
provisions for determining whether an
area is designated and classified under
subpart 1 or subpart 2 and these rules
are explained in the preamble to those
final rules at 69 FR 23954.) Also,
appendix S requires States or EPA to
issue permits during the SIP
development period consistent with
these requirements. Specifically, under
subpart 1, the major stationary source
threshold is 100 tpy, and an offset ratio
of at least 1:1 applies. Under subpart 2,
the major stationary source threshold
ranges from 10 to 100 tpy, depending on
the classification of the nonattainment
area in which the source is located. The
applicable offset ratios range from 1:1 to
1:5, also depending on the classification
of the nonattainment area in which the
source is located.
We also finalized as proposed in 1996
and 2003 that the NSR requirements
applicable to major stationary sources of
VOC (including provisions regarding
major modifications, significant
emission rates, and offsets) apply to
NOX emissions. These requirements
apply in all 8-hour ozone nonattainment
areas, including subpart 1 and subpart
2 areas. These requirements apply
except where the Administrator
determines, according to the standards
set forth in section 182(f), that NOX
requirements for major stationary
sources, including nonattainment major
NSR requirements, would not apply or
would be limited (‘‘NOX waiver’’). [See
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§ 51.165(a)(8) and appendix S.]
According to § 51.913(c), a section
182(f) NOX exemption granted under the
1-hour ozone standard does not relieve
the area from any requirements under
the 8-hour ozone standard, including
nonattainment major NSR for major
stationary sources of NOX. We discuss
whether a NOX waiver under section
182(f) applies in a particular area and
the effects of NOX waivers on RACT in
section IV.H. of this preamble.
We are not taking final action to
implement the special modification
provisions at CAA sections 182(c), (d),
and (e) for serious, severe, and extreme
ozone nonattainment areas at this time.
We are evaluating additional issues
related to implementation of these
requirements and anticipate taking final
action in the future.
As proposed on July 23, 1996 (61 FR
38250), we have incorporated
requirements in part D of title I of the
1990 CAA Amendments for CO. [See
§ 51.165(a)(1)(iv)(A)(1)(v) and
(a)(1)(x)(D) and appendix S.]
We have also made final changes to
incorporate the requirements of the
1990 CAA Amendments concerning
PM10 nonattainment areas. Specifically,
we have promulgated as proposed in
1996 the major stationary source
thresholds and significant emission
rates for PM10 in PM10 nonattainment
areas. [See § 51.165(a)(1)(iv)(A)(1)(vi)
and (a)(1)(x). See also appendix S at
II.A.4.(i)(a)(6) and II.A.4.(i).] We have
not taken final action on our 1996
proposed rules for PM10 precursors.
Instead, we plan to propose regulations
concerning PM precursors as part of the
PM2.5 NAAQS implementation rule. We
also plan to address requirements for
stationary sources of PM in that action.
b. Legal Basis for Changes To
Incorporate the 1990 CAA Amendments
In areas not meeting health-based
NAAQS and in the OTR, the major NSR
program is implemented under the
requirements of section 110(a)(2)(C) and
part D of title I of the CAA. Subpart 1
of part D of title I contains general
requirements for nonattainment areas
for any criteria pollutant. Subpart 2
contains provisions specifically for
ozone nonattainment areas. Subpart 3
contains provisions specifically for CO
nonattainment areas. Subpart 4 contains
provisions specifically for PM10
nonattainment areas. On July 23, 1996
(61 FR 38250), we proposed changes to
§ 51.165 and appendix S to incorporate
requirements in part D of title I of the
1990 CAA Amendments for ozone, CO,
and PM10 nonattainment areas.
We promulgated a new 8-hour ozone
NAAQS on July 18, 1997. We indicated
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71675
that we anticipated that States would
implement the 8-hour ozone NAAQS
under the less prescriptive subpart 1
requirements. In February 2001, the
Supreme Court ruled that the statute
was ambiguous as to the relationship of
subparts 1 and 2 for purposes of
implementing the 8-hour ozone
NAAQS. In Whitman v. American
Trucking Associations, [531 U.S. 457,
482–86 (2001)], the Supreme Court
reviewed EPA’s implementation strategy
for the revised 8-hour ozone NAAQS,
and remanded it to EPA to develop a
reasonable resolution of the roles of
subparts 1 and 2 in classifying areas for
and implementing the revised ozone
standard. On April 30, 2004, we
promulgated a final rule to implement
the 8-hour ozone NAAQS (69 FR
23951), in which some nonattainment
areas would be regulated under the less
restrictive requirements of subpart 1 and
some would be classified and regulated
under subpart 2. All ozone
nonattainment areas have now been
categorized subpart 1 or subpart 2 areas
in 40 CFR part 81. Now that we have
designated and classified nonattainment
areas, the NSR program requirements
(including the specific major stationary
source thresholds, significant emission
rates, and offset ratios associated with
each classification) are determined by
reference to subpart 1 and subpart 2, as
codified in § 51.165 and appendix S
through this rulemaking. Thus, as
described in further detail in section
V.A.2 of this preamble, we have
incorporated the requirements of the
1990 CAA Amendments for major
stationary sources of ozone precursors
in ozone nonattainment areas as
proposed in 1996, and codified those
requirements for the 8-hour standard
consistent with the designation and
classification scheme finalized in the 8hour ozone implementation rule (69 FR
23951) promulgated in response to
Whitman v. American Trucking
Associations, 531 U.S. 457 (2001).
Concerning CO, section 187(c) of the
CAA unambiguously establishes the
major stationary source threshold of 50
tpy codified today for serious
nonattainment areas where the
Administrator has determined that
stationary sources contribute
significantly. It is also reasonable to set
the significant emission rate at 50 tpy in
those serious nonattainment areas
where 50 tpy is the major stationary
source threshold. The regulations at
§ 51.165(a)(1)(iv)(A)(2) require that if a
modification itself would constitute a
major stationary source, the
modification is subject to major NSR.
Concerning PM10, section 189 of the
CAA unambiguously establishes the
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major stationary source threshold as 70
tpy in serious nonattainment areas.
Also, EPA has the authority to exempt
de minimis emissions from the reach of
a rule. See Alabama Power, 636 F.2d at
360–61. Previously, EPA has defined the
PM10 significant emission rate (that is,
de minimis cut-off level) as at or above
15 tpy for purposes of determining
which modifications are insignificant
and thus exempt from PSD review (52
FR 24672, 24694–96; July 1, 1987). We
believe it is reasonable to use the same
significant emission rate in the
nonattainment NSR program. This is
consistent with our past practice of
applying the same significant emissions
rates for each pollutant in the PSD and
nonattainment NSR programs.
We also revised appendix S to
incorporate the requirements of the
1990 CAA Amendments to part D of
title I of the CAA. These changes are
necessary to make appendix S
consistent with part D. As we discuss in
section V.B.3.b of this preamble, we
have determined that Congress intended
for permitting equivalent to the part D
NSR provisions to apply during the SIP
development period through the use of
appendix S (subject to the limited
section VI exemption). In light of this
determination, there is no reasonable
basis for declining to implement the
NSR requirements in the 1990 CAA
Amendments during that period.96
Additionally, appendix S provides on
its face that it is an interpretation of the
NSR permitting rules in 40 CFR subpart
I, including § 51.165. Therefore, it is
necessary to have appendix S reflect
substantially the same requirements as
are in § 51.165.97 Thus, we proposed to
amend appendix S in this manner in the
1996 NSR proposal. We also are mindful
of the Supreme Court’s decision in
American Trucking Associations.
Although the decision did not directly
96 The 1991 NSR transitional guidance issued to
address implementation of the 1990 CAA
Amendments acknowledged that appendix S did
not contain at that time the newly enacted part D
provisions, and further provided that the new
requirements of part D to title I did not apply until
November 15, 1992 for the ozone nonattainment
areas; June 30, 1992, for the PM10 nonattainment
areas; and 3 years from designation for most CO
nonattainment areas. NSR Program Transitional
Guidance, at A5 (March 11, 1991). We later clarified
that the 1990 CAA Amendments did apply to all
permits after those deadlines passed. NSR
Supplemental Program Transitional Guidance on
Applicability of New Part D NSR Requirements at
3 (September 3, 1992).
97 Thus, EPA has typically conformed appendix S
to the part D nonattainment NSR permitting
provisions governing SIPs at 40 CFR § 51.165
(originally codified at § 51.18) whenever those
regulations were revised. See, for example, 45 FR
52676 (August 7, 1980); 47 FR 27554 (June 25,
1982); 49 FR 43210 (October 26, 1984); 54 FR 27274
(June 28, 1989); 57 FR 3941 (February 3, 1992).
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address NSR implementation during the
SIP development period, the Court
emphasized the importance of creating
a role for subpart 2 in implementation
of the 8-hour ozone NAAQS. We believe
this suggests the need to create a role for
subpart 2 in appendix S, in contrast to
the exclusive subpart 1 scheme
currently embodied in appendix S.
2. Final Action and Legal Basis for
Changes to Criteria for Emission
Reduction Credits From Shutdowns and
Curtailments
a. Final Changes to Criteria for Emission
Reduction Credits From Shutdowns and
Curtailments
The final revisions lift the
requirement to have an approved
attainment plan before using
preapplication credits from shutdowns
or curtailments as offsets. They also
facilitate the availability of creditable
offsets, consistent with the requirements
of section 173 of the CAA. We revised
the provisions at § 51.165(a)(3)(ii)(C)
and appendix S concerning emission
reduction credits generated from
shutdowns and curtailments as
proposed in Alternative 2 of the 1996
proposal, with one exception. We agree
with the commenter who found the
regulatory term ‘‘most recent emissions
inventory’’ confusing. We have revised
§ 51.165(a)(3)(C)(1) accordingly,
specifying that the shutdown or
curtailment must have occurred after
‘‘the last day of the base year for the SIP
planning process.’’ For the 8-hour ozone
NAAQS, the base year is 2002.98
Additionally, today’s final provisions
allow a reviewing authority to consider
a prior shutdown or curtailment to have
occurred ‘‘after the last day of the base
year if the projected emission inventory
used to develop the attainment
demonstration explicitly includes the
emissions from such previously
shutdown or curtailed emissions unit.’’
This provision is consistent with the
previous regulation which also allowed
the reviewing authority to treat prior
shutdowns or curtailments as occurring
after the date of the most recent
emissions inventory, but we have
modified the regulatory language to
clarify the appropriate emissions
inventory. This regulatory language is
consistent with our previous guidance
on how emission reduction credits from
shutdowns and curtailments are used in
attainment planning.99 The base year
98 68 FR 32833. See also ‘‘2002 Base Year
Emission Inventory SIP Planning: 8-hr Ozone,
PM2.5 and Regional Haze Programs,’’ U.S. EPA, pg.
1 (November 18, 2002).
99 See 57 FR 13553. After the 1990 CAA
Amendments were enacted, 1990 was the base year
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inventory includes actual emissions
from existing sources and would not
reflect emissions from units that were
shutdown or curtailed before the base
year, as these emissions are not ‘‘in the
air.’’ To the extent that these emission
reduction credits are considered
available for use as offsets and are thus
‘‘in the air’’ for purposes of
demonstrating attainment, they must be
included in the projected emissions
inventory used in the attainment
demonstration along with other growth
in emissions over the base year
inventory. This step assures that
emissions from shutdown and curtailed
units are accounted for in attainment
planning.100 As with the prior rules,
reviewing authorities thus retain the
ability to consider a prior shutdown or
curtailment to have occurred after the
last day of the base year if emissions
from the shutdown or curtailment are
accounted for in the attainment
demonstration. However, in no event
may credit be given for shutdowns that
occurred before August 7, 1977, a
provision carried over from the previous
regulation.
The other changes to the proposed
rule text also are nonsubstantive and
instead clarify the restrictions on credits
from shutdowns or curtailments.
Specifically, the proposed rule retained
the requirement for an approved
attainment demonstration, but made
that requirement inapplicable where the
credits occurred after the last day of the
base year for the SIP planning process
or where they were included in the most
recent emissions inventory. The final
rule recognizes there is no requirement
for an approved attainment
demonstration in those circumstances,
and thus deletes the reference to that
former requirement.
We note that the requirements for
emissions reductions used as offsets and
for netting differ from those for emission
reduction credits used for RFP and ROP.
for 1-hour ozone NAAQS attainment planning
purposes. See 57 FR 13502. The EPA encouraged
States to allow sources to use pre-enactment banked
emissions reductions credits for offsetting purposes.
States have been allowed to do so if the restored
credits meet all other offset creditability criteria,
and States consider such credits as part of the
attainment emissions inventory when developing
their post-enactment attainment demonstration.
100 For a discussion of emission inventories for
the 8-hour ozone standard, see our emission
inventory guidance, ‘‘Emissions Inventory
Guidance for Implementation of Ozone and
Particulate Matter National Ambient Air Quality
Standards (NAAQS) and Regional Haze
Regulations—Final,’’ at https://www.epa.gov/ttn/
chief/eidocs/eiguid/. For a discussion of
emission projections used in attainment
demonstrations, see Emission Inventory
Improvement Program, Volume X, Emission
Projections, December 1999, available at https://
www.epa.gov/ttn/chief/eiip/techreport/.
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Section IV.E.14. of this preamble
discusses requirements for emission
reduction credits used for RFP and ROP.
For a more detailed discussion of
emission reduction credits for offsets
and netting under the 8-hour ozone
NAAQS, see section V.D.5. of this
preamble.
b. Legal Basis for Changes to Criteria for
Emission Reduction Credits From
Shutdowns and Curtailments
The revisions to the rules governing
use of emissions reductions from
shutdowns/curtailments as offsets are
warranted by the more detailed
attainment planning and sanction
provisions of the 1990 CAA
Amendments. These provisions
specifically address air quality concerns
in nonattainment areas lacking EPAapproved attainment demonstrations.
As a threshold matter, we note that CAA
section 173 does not mandate the prior
restrictions on shutdown credits,
specifically, the requirement to have an
approved attainment demonstration.
(See 48 FR 38742, 38751; August 25,
1983). Rather, in promulgating these
restrictions in 1989, EPA recognized
that it had a large degree of discretion
under the CAA to shape implementing
regulations, as well as the need to
exercise that discretion such that offsets
are consistent with RFP as required in
CAA section 173. (See 54 FR 27286,
27292; June 28, 1989). Originally, EPA
believed that areas without approved
attainment demonstrations lacked
adequate safeguards to ensure that
shutdown/curtailment credits would be
consistent with RFP. We thus subjected
those areas to more restrictive
requirements to ensure a link between
the new source and the source being
shutdown/curtailed (that is, shutdown/
curtailment must occur after application
for a new or modified major source is
filed).
The 1990 CAA Amendments changed
the considerations involved. As
discussed above, for areas subject to
subpart 2, Congress emphasized the
emission inventory requirement in
section 172(c)(3) as a fundamental tool
in air quality planning. Congress also
added new provisions keyed to the
inventory requirement, including
specific reduction strategies and
Amilestones@ that measure progress
toward attainment from the base year
emissions inventory or subsequent
revised inventories. Where the emission
reduction credits pre-date the base year,
State and local agencies must include
the credits from the shutdown/
curtailment in the projected emissions
inventory used to develop the
attainment demonstration. Subpart 4
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sets forth specific reduction strategies
and milestones for attainment of the
PM10 standards. Additionally, there are
now several adverse consequences
where States fail to meet the planning
or emissions reductions requirements of
the CAA. For example, the CAA
contains mandatory increased new
source offset sanctions at a 2:1 ratio
where the Administrator finds that a
State failed to submit a required
attainment demonstration. In areas that
are subject to subpart 2 and subpart 4,
failure to attain the air quality standard
by the attainment deadline results in the
area being bumped up to a higher
classification. Additional regulatory
requirements are imposed as a result of
the higher classification. These statutory
changes justify shifting the focus of the
current regulations from individual
offset transactions between a specific
new source and shutdown source and
towards a systemic approach.
Considering the changes to the 1990
CAA Amendments, we now believe that
continuing the prohibition on the use of
shutdown/curtailment credits generated
where there is no approved attainment
demonstration is not warranted. We
believe that use of emission reduction
credits from shutdowns/curtailments
will be consistent with RFP towards
attainment under CAA section 173, even
in the absence of an approved
attainment demonstration, if they occur
after the last day of the base year for the
SIP planning process or are included in
the projected emissions inventory used
to develop the attainment
demonstration. From an air quality
planning perspective, emissions from
the shutdown source actually impacted
the measurements of air quality used in
determining the nonattainment status of
an area. Subsequently, emissions
reductions from such source
shutdowns/curtailments are actual
emissions reductions, and their use as
emission offsets at a ratio of 1:1 or
greater is consistent with RFP towards
improved air quality as set forth in CAA
section 173(a)(1)(A).
3. Final Action and Legal Basis for
Changes to the Construction Ban
Provisions
a. Final Action for Changes to the
Construction Ban Provisions
We are promulgating final changes to
§ 52.24 to implement the construction
ban provisions and other changes, as
proposed in 1996 and 2003.101 We
101 We note that we are changing the crossreference in § 52.24(f) to ‘‘§ 51.165’’ instead of the
definitions section at § 51.165(a), to ensure that all
of the provisions of ‘‘51.165 apply in interpreting
the terms of § 52.24.
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71677
believe these changes are beneficial to
conform the regulatory text with the
requirements that apply under the 1990
CAA Amendments.
As noted in our June 2003 proposal,
we are retaining the provision in
§ 52.24(k) that specifies that appendix S
governs permits to construct and
operate applied for during the SIP
development period. Although the
regulatory text proposed in 1996
omitted § 52.24(k), the 1996 preamble
also explained that the changes to
§ 52.24 were intended only to update
and clarify the regulation with regard to
the changes to the construction ban
made by the 1990 CAA Amendments.
(61 FR 38250, 38305). The preamble did
not in any manner indicate that EPA
believed that NSR permits complying
with appendix S were not required
during the SIP development period
where necessary. Additionally, it did
not contemplate nonattainment major
NSR permitting in light of the situation
that today’s final action addresses,
which is the need to permit
nonattainment area sources during a
transition period in which a substantial
number of new nonattainment areas are
being created. Therefore, we are
retaining § 52.24(k).
As we proposed in the 8-hour ozone
NAAQS implementation rule (68 FR
32846), we made one change to the
regulatory language in § 52.24(k). The
previous language at § 52.24(k) only
allowed States to issue permits under
appendix S for a maximum period of 18
months after designation. This language
was consistent with the previous SIP
development period and construction
ban under the 1977 CAA, which no
longer apply under the 1990 CAA
Amendments. We have revised
§ 52.24(k) to allow States to issue
permits under appendix S from
designation until the SIP is approved,
even if this exceeds 18 months. As we
noted in our proposal, this change
implements the removal of the
construction ban from the 1990 CAA
Amendments and is consistent with our
1991 policy memo, ‘‘New Source
Review (NSR) Program Transitional
Guidance,’’ John S. Seitz, March 11,
1991.
b. Legal Basis for Changes to the
Construction Ban Provisions
Section 110(a)(2)(c) of the CAA
establishes a general duty on States to
include a program in their SIP that
regulates the modification and
construction of any stationary source as
necessary to assure that the NAAQS are
achieved. This general duty, often
referred to as ‘‘minor NSR,’’ exists
during all periods, including before a
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State has an approved part D NSR
permit program.
Section 110(a)(2)(c) of the CAA does
not define specific requirements States
must follow for issuing major source
permits during the interim period
between nonattainment designation and
EPA approval of a part D nonattainment
NSR SIP (‘‘interim period’’). However,
EPA’s regulations at § 52.24(k) require
States to follow EPA’s Emission Offset
Interpretative Ruling, 40 CFR part 51,
appendix S, during this time.
This approach is consistent with
Congressional intent, as indicated in the
1977 CAA Amendments providing for
major NSR permitting during the SIP
development period in accordance with
appendix S. [See Public Law No. 95–95,
section 129(a), 91 Statute 685 (1977)].
Specifically, Congress enacted a
moratorium on construction in any area
lacking an approved part D NSR SIP,
with a delayed effective date of July 1,
1979. Congress also provided that
appendix S, as modified by rule of the
Administrator, govern permitting of
sources constructing in such areas
before that date, subject to a limited
waiver by the Administrator. Id. 108(b),
129(a). We subsequently codified the
use of appendix S as the interim major
NSR program in 40 CFR § 52.24(k),
reasoning (in the context of
implementing a delay in the
construction ban for then-recently
designated nonattainment areas) that
Congress had provided that appendix S
should remain in effect to protect air
quality while State plans were being
designed (45 FR 65209). When Congress
removed the construction ban [(except
as provided in section 110(n)(3)), it left
in place 40 CFR § 52.24(k)],
implementing the interim major NSR
program under appendix S.
Accordingly, we have historically
recognized that the SIP development
period provided for in section 172(b)
leaves a gap in part D major NSR
permitting and have determined that
this gap is to be filled with an interim
major NSR program that is substantially
similar to the requirements of part D.
This includes the LAER and offset
requirements from part D (57 FR 18070,
18076). Appendix S has been used by
EPA and the States as this interim major
NSR program.102
102 Appendix S was originally promulgated in
1976 to address whether, and to what extent, new
and modified sources would be allowed to
construct in nonattainment areas whose attainment
deadlines had already passed, in light of the
regulatory requirement that new or modified
sources be disapproved where the source would
interfere with attainment of the NAAQS (41 FR
55524; December 21, 1976). It required, inter alia,
compliance with the LAER and offsetting emissions
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Our regulations at 40 CFR 52.24(k)
require permits issued during this
period to be consistent with the
requirements in appendix S. The
continued application of appendix S
through § 52.24(k) is also supported by
the purpose of the CAA, specifically,
section 101(b)(1), ‘‘to protect and
enhance the quality of the Nation’s air
resources so as to promote the public
health and welfare and the productive
capacity of its population.’’ This
provision was the basis for the original
judicial finding that the CAA imposed
an obligation to prevent significant
deterioration in areas that meet the
NAAQS, prior to Congress’ enactment of
the PSD program at part C of the
CAA.103 This policy of non-degradation
applies with even greater force in areas
that fail to meet the NAAQS. Thus, we
believe that an interim major NSR
program for the SIP development
period—as codified at appendix S and
updated to reflect CAA amendments—is
supported by section 110(a)(2)(C),
section 101(b)(1), Congressional intent,
and our gapfilling authority under
section 301(a).
4. Final Action and Legal Basis for
Changes on Applicability of Appendix S
and the Transitional NSR Program
a. Final Changes on Applicability of
Appendix S and the Transitional NSR
Program
We are not finalizing the transitional
NSR program under section VI of
appendix S as proposed, which would
have established limited criteria for
determining in which nonattainment
areas section VI could apply. Upon
consideration of public comments, we
decided to retain the original eligibility
conditions, but added a procedural
requirement that the Administrator
determine whether section VI applies
for a specific situation.
As we noted at 68 FR 32848, on its
surface section VI could apply in any
reductions in excess of the new source’s emissions.
At that time, part D NSR was not part of the CAA.
When the part D NSR provisions were added in
the 1977 CAA Amendments, Congress added the
requirement that SIPs contain nonattainment NSR
provisions as set forth in CAA section 173,
including LAER and the requirement to either offset
the increase in new source emissions or ensure that
emissions fell within a growth allowance. (The
growth allowance provision was repealed in 1990).
Additionally, Congress provided that appendix S,
as modified by rule of the Administrator, would
govern preconstruction permitting in areas lacking
approved part D SIPs before a construction ban
went into effect, as discussed in more detail above.
103 See Alabama Power Co. v. Costle, 636 F. 3d
323, 346–047 (D.C. Circuit, 1980) (discussing Sierra
Club v. Ruckelshaus, 344 F. Supp. 253 (D.D.C.
1972), aff’d per curiam 4 ERC 1815 (D.C. Circuit,
1972), aff’d by an equally divided court, sub nom
Fri v. Sierra Club, 412 U.S. 541 (1973).
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nonattainment area where the dates for
attainment have not passed if the source
meets all applicable SIP emission
limitations and would not interfere with
the area’s ability to meet its attainment
date, without providing any specific
safeguards for such noninterference. We
noted at proposal, however, that States
generally would not be able to show that
a nonattainment area would continue to
meet its attainment date if it does not
apply LAER or offsets to major new
sources and major modifications in the
absence of safeguards (68 FR 32848).
We continue to believe, as stated in
the proposal, that States should not
interpret section VI as allowing a
blanket exemption from LAER and
offsets for all major new sources and
major modifications in a given area
before attainment dates have passed for
that area. However, based on public
comment, we now believe that the
program as proposed at 69 FR 32846 is
not implementable. As many
commenters noted, the April 15, 2004
deadline for submission of attainment
plans and December 31, 2004 deadline
for implementation of all necessary
attainment controls were impracticable.
We agree with the many commenters
who supported flexible NSR
requirements under section VI for some
areas and maintained that attainment
would not be in jeopardy due to such
programs. While we do not identify any
such particular instances in today’s final
rule, we believe that participation in
programs such as the NOX SIP Call and
the CAIR (70 FR 25162, May 12, 2005)
will achieve significant emissions
reductions across broad geographical
areas. Certainly, we want to encourage
development of programs that address
transported air pollution. We recognize
that these and other programs may
prove to be more effective and practical
in assuring that there is no interference
with an area’s ability to meet its
attainment deadline than relying on
offsets from a single source.
For these reasons, we have retained
the original eligibility conditions for
determining when section VI applies,
but added a procedural requirement that
the Administrator provide public notice
that section VI applies for a specific
situation. This requirement will achieve
the proposal’s purpose of assuring that
States do not interpret section VI to
provide a broad exemption to all major
new sources and major modifications in
any nonattainment area for which the
attainment date has not passed.
We also are taking final action to
remove the 50 tpy exemption from
appendix S. As discussed in section
V.A.2.f of this preamble, we proposed
this change in 1979 and finalized it in
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most respects in 1980. However, we
inadvertently did not remove the
exemption in all the places in appendix
S where it was located, specifically
footnotes 5 and 8 to IV.D. We are now
finalizing the 1979 proposal to the
extent it remained incomplete, by
removing these last two references to
the 50 tpy exemption in appendix S.
b. Legal Basis for Changes to
Applicability of Appendix S and the
Transitional NSR Program
The legal basis for appendix S itself,
including section VI, is discussed in
detail in section V.B.3.b. of this
preamble. We have historically
recognized that the SIP development
period provided for in section 172(b)
leaves a gap in part D major NSR
permitting and have determined that
this gap is to be filled with an interim
major NSR program that is substantially
similar to the requirements of part D,
including the LAER and offset
requirements from part D, subject to a
limited exemption where the attainment
deadline will be met (57 FR 18070,
18076). This interim NSR program has
been implemented to date through
appendix S.
We also believe that, contrary to
objections made by some commenters,
appendix S—and in particular, section
VI—has not been superseded by the
1990 CAA Amendments to title I of the
CAA. In short, appendix S only applies
where a NSR permitting program for the
new or revised NAAQS is not otherwise
in effect, and thus does not replace any
part D NSR SIP provisions, as many
commenters erroneously believed. That
is, it applies only in newly designated
or redesignated nonattainment areas
lacking approved part D programs for a
new or revised NAAQS, such as the 8hour ozone NAAQS. Thus, the evasion
of subpart 2 requirements posited by
commenters and the anti-backsliding
concerns they raise are not triggered, as
nothing in the SIP is replaced. Our
detailed response to those comments is
set forth in section V.C.4. of this
preamble.
The section VI exemption, as limited
by this final rule, is consistent with the
section 110(a)(2)(C) requirement that the
preconstruction permitting is
implemented ‘‘as necessary to assure
that the [NAAQS] are achieved.’’ We are
not adopting the eligibility criteria that
were proposed to ensure satisfaction of
the original section VI conditions.
However, we have added a requirement
that the Administrator determine that
sources exempted from LAER and
offsets under section VI will meet those
conditions, in particular,
noninterference with the attainment
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deadline. Section VI also is consistent
with the exercise of our gapfilling
authority under section 301, as
informed by the legislative history. That
is, appendix S reflects Congressional
intent that standards equivalent to part
D govern the issuance of NSR permits,
subject to a limited degree of flexibility
under conditions where attainment of
the NAAQS by the attainment deadline
is assured.
The removal of the 50 tpy exemption
from appendix S is based on Alabama
Power Co. v. Costle, 636 F. 3d 323, 356–
57 (D.C. Circuit, 1980), in which the
court held that EPA had exceeded its
authority to establish the exemption, as
discussed in more detail in section
V.A.2.f. above.
5. Final Action and Legal Basis for
Changes to Identify NOX as an Ozone
Precursor in Attainment and
Unclassifiable Areas
a. Final Changes to Identify NOX as an
Ozone Precursor in Attainment and
Unclassifiable Areas
Our existing PSD regulations in
§ 51.166 and § 52.21 define regulated
NSR pollutants, which includes any
pollutant for which we promulgate a
NAAQS and any constituents or
precursors for such pollutants as
identified by the Administrator. [See
§ 51.166(b)(49)(i) and § 52.21(b)(50)(i)].
Today, the Administrator is identifying
NOX as an ozone precursor in
attainment and unclassifiable areas.
Accordingly, as proposed, we amended
our PSD regulations in § 51.166 and
§ 52.21 to expressly include NOX as an
ozone precursor. Specifically, we have
amended the definitions of major
stationary source, major modification,
significant, and regulated NSR pollutant
to include NOX as an ozone precursor.
[See § 51.166(b)(1)(ii), (b)(2)(ii), (b)(23),
and (b)(49). See also § 52.21(b)(1)(ii),
(b)(2)(ii), (b)(23), and (b)(50)]. We have
also amended the footnote to
§ 51.166(i)(5)(i)(e) and § 52.21(i)(5)(i) to
require sources with a net increase of
100 tpy or more of NOX to perform an
ambient impact analysis.
b. Legal Basis To Identify NOX as an
Ozone Precursor in Attainment and
Unclassifiable Areas
The nonattainment provisions of the
CAA, as amended in 1990, recognize
NOX as an ozone precursor; section
182(f) of the CAA established
nonattainment requirements for NOX.
The definition of air pollutant under
section 302(g) of the CAA includes,
‘‘* * * any precursors to the formation
of any air pollutant * * *’’ Also, the
definition of regulated NSR pollutant in
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§ 51.166 and § 52.21 specifically
recognizes that a regulated NSR
pollutant is ‘‘any pollutant for which a
national ambient air quality standard
has been promulgated and any
constituents or precursors for such
pollutant identified by the
Administrator (e.g., volatile organic
compounds are precursors for ozone).’’
The EPA has recognized NOX as an
ozone precursor in several national
rules because of its contribution to
ozone transport and the ozone
nonattainment problem. The EPA’s
recognition of NOX as an ozone
precursor is supported by scientific
studies, which have long recognized the
role of NOX in ozone formation and
transport.104 Such formation and
transport is not limited to
nonattainment areas. Therefore, we
believe NOX should be treated
consistently as an ozone precursor in
both our PSD and nonattainment NSR
regulations. For these reasons we have
promulgated final regulations providing
that NOX is an ozone precursor in
attainment areas.
6. Final Changes and Legal Basis for
Changes to Emission Offset Provisions
of Appendix S
a. Final Changes to Emission Offset
Provisions of Appendix S
We are revising certain provisions in
appendix S to reflect requirements of
the 1990 CAA Amendments concerning
offsets and RFP. Specifically, we have
conformed appendix S at IV.D. to the
1990 CAA Amendments by replacing
the interim policy on offsetting
emissions with the statutory language at
section 173(c)(1). We also have removed
the language concerning reasonable
progress in section IV.E. of appendix S
and replaced it with the statutory
requirements at 173(a)(1)(A).
Also, we note that the definition of
net emissions increase at
§ 51.165(a)(1)(vi)(E) requires that a
decrease in actual emissions is
creditable only to the extent that the
State has not relied on it in
demonstrating attainment or RFP. This
requirement has never been codified in
appendix S. However, the 1990 CAA
Amendments at sections 172(b)(1) and
182 codifies the requirements
concerning RFP. State and local
agencies should consider the effect of
creditable decreases from permitting
under appendix S in their planning for
demonstrating attainment and RFP.
We are also restating our policy on
offsets from resource recovery facilities
104 See 68 FR 32805–06, 32840, footnote 58
(discussing national rules for controlling VOC and
NOX emissions); and 68 FR 32840 footnote 57.
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under appendix S. Appendix S at
IV.B.(i) exempts resource recovery
facilities from permitting under certain
circumstances. Our 1988 policy memo
indicates that as a matter of policy, EPA
no longer adheres to the offset
exemption for resource recovery
facilities in appendix S.105 As we did
not propose to change this provision, we
are not revising the final rules today
regarding resource recovery facilities.
However, we plan to remove this
exemption in a future rulemaking.
b. Legal Basis for Changes to Emission
Offset Provisions of Appendix S
Because we have not revised the
regulatory text in appendix S since the
latest revision to the statute, the 1990
CAA Amendments provisions limiting
the use of offsets are not explicitly
included in appendix S. Nonetheless,
these requirements apply to sources
permitted using appendix S because
appendix S is intended to reflect the
same offset requirements contained in
part D of the CAA. These provisions
relate to offsets and RFP.
We are revising appendix S to incorporate
the statutory restrictions on offsets and
remove the existing regulatory text that is
outdated. The 1977 CAA is silent concerning
the location of offsetting emissions. As we
noted in footnote 9 to section IV.D. of
appendix S, in the absence of specific
statutory language, we developed an interim
policy on offset locations. The 1990 CAA
Amendments at section 173(c)(1), however,
placed specific limits on the location of
offsets and therefore superceded the interim
policy in appendix S. Accordingly, we
conformed appendix S at IV.D. to the 1990
CAA Amendments by replacing the interim
policy on offsetting emissions with the
statutory language at section 173(c)(1).
Appendix S at section IV.E. contains
provisions regarding the relationship
between offsets, reasonable progress
towards attainment, and RFP. Under the
1990 CAA Amendments, section
173(a)(1)(A) was revised to set forth the
extent to which offsets must represent
RFP, as defined in section 171.
Therefore, we removed the language
concerning reasonable progress in
section IV.E. of appendix S and replaced
it with the statutory requirements at
173(a)(1)(A).
C. Comments and Responses
1. Comments on Proposed Changes to
Incorporate the 1990 CAA Amendments
In today’s final action, we have
revised § 51.165 and appendix S to
incorporate the major stationary source
105 See Emission Offset Exemptions for Resource
Recovery Facilities from Gerald A. Emison, Director,
Office of Air Quality Planning and Standards,
December 28, 1988.
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thresholds, significant emission rates,
and offset ratios pursuant to part D of
title I of the 1990 CAA Amendments for
major stationary sources of ozone
precursors. As we noted in section
V.A.2.a. of this preamble, now that the
designations and classifications have
been made, the provisions of subpart 1
and subpart 2 determine the NSR
program requirements. Those
requirements are codified in this
rulemaking. For a summary of
comments and responses related to
when subpart 1 or subpart 2 applies,
please see the preamble to those final
rules at 69 FR 23961.
Commenters on both the 1996 and
2003 proposals generally supported
applying the nonattainment major NSR
requirements applicable to major
stationary sources of VOC (including
provisions regarding major
modifications, significant emission
rates, and offsets) to NOX emissions,
except where the Administrator
determines pursuant to section 182(f)
that NOX requirements for major
stationary sources, including NSR
requirements, would not apply or would
be limited (‘‘NOX waiver’’). A few
commenters opposed waivers under
section 182(f) for exemptions from NOX
requirements, due to their effect on NOX
emissions in downwind States.
We agree with the commenters
supporting NOX as an ozone precursor
for nonattainment major NSR
applicability, and have retained it in the
final rule. We note that whether a NOX
waiver applies in a particular area and
the effects of NOX waivers on RACT are
discussed in section IV.H. of this
preamble.
2. Comments on Proposed Revisions to
Criteria for Emission Reduction Credits
From Shutdown and Curtailments
Many commenters generally
supported EPA’s conclusion that
emission reduction credits from
shutdowns and curtailments can be
used for NSR offsets. These commenters
believed the safeguards in the 1990 CAA
Amendments justified removing the
previous requirement for an approved
attainment plan before such credits can
be used as offsets. One commenter
opposed lifting the restrictions,
believing that the cited 1990 CAA
Amendment provisions, including
submittal of SIP attainment
demonstrations, have not been
implemented.
While no commenters supported the
adoption of Alternative 1 exclusively, a
few commenters supported both
proposed Alternatives. However, many
commenters strongly supported
Alternative 2. These commenters
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asserted that the safeguards in the 1990
CAA Amendments address progress in
nonattainment areas and that an
approved attainment demonstration is
no longer necessary to ensure
shutdown/curtailment credits are
accounted for in the attainment
demonstration. These commenters also
believed Alternative 2 was more flexible
and would encourage stable banking
programs. Many commenters believed
that State agencies would be unable to
meet the deadlines in Alternative 1.
They also believed that Alternative 1
was unnecessarily restrictive, and
would cause confusion.
We agree with the commenters who
supported Alternative 2. We have
promulgated final regulations that allow
emission reduction credits to be used as
offsets in the absence of an approved
attainment demonstration, provided that
these emission reduction credits were
generated from shutdowns or
curtailments that are included in the
base year emission inventory as current
actual emissions.
One commenter stated that the
regulatory language concerning the
‘‘most recent emissions inventory’’ is
confusing. The commenter believed this
language could be mistaken to mean
that the base year would continue to
shift. The commenter noted that it
would be more accurate to state that the
base year emissions inventory is the
starting point and all creditable
emissions reductions must have been
reported in the base year inventory or a
subsequent emissions inventory. We
agree with the commenter that the
terminology ‘‘most recent emissions
inventory’’ is confusing and have
revised § 51.165(a)(3)(C)(1) accordingly,
specifying the cutoff date as ‘‘the last
day of the base year if the projected
emissions inventory used to develop the
attainment demonstration explicitly
includes the emissions from such
previously shutdown or curtailed
emission units.’’ As we discussed in
section V.B.2.a. of this preamble, this
regulatory language is consistent with
our previous guidance on how emission
reduction credits from shutdowns and
curtailments are used in attainment
planning. Most importantly, it assures
that emissions from shutdown and
curtailed units are accounted for in
attainment planning.
We disagree with the commenter who
opposed the revisions. Since the
submission of this comment in 1997,
States have made substantial progress in
implementing the 1990 CAA
Amendments. This progress includes
submitting the required inventories to
which attainment planning is keyed,
along with the required attainment
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demonstrations.106 We believe that
implementation of the 1990 CAA
Amendments to date supports the
conclusion that emission inventories
have been effective in attainment
planning, and will continue to be
effective in implementing the 8-hour
standard. Therefore, we disagree with
the commenter that the 1990 CAA
Amendments do not justify the
revisions due to inadequate
implementation.
3. Comments on Construction Ban
Provisions
We received comments on the
following procedural issue. In the
proposal, we stated our intent to issue
determinations of inadequate SIP
implementation under section 173(a)(4)
by letter, followed by publication in the
Federal Register, and explained that
such determinations would result in a
prohibition on construction in the area
pursuant to that provision (61 FR
38305). We also solicited comment on
whether an opportunity for public
notice and comment should be
provided. A few State commenters
believed that EPA should provide such
notice and comment, but did not state
a basis for their position.
The text of § 52.24(b) as proposed
tracked the language of section 173(a)(4)
and did not include a provision on the
process to be used for issuing a
determination of inadequate SIP
implementation. We have finalized
§ 52.24(b) in substantially the same form
as we proposed. The Agency is still
considering the appropriate process to
use in issuing a determination under
CAA section 173(a)(4).
4. Comments on Applicability of
Appendix S and the Transitional
Program
Many commenters opposed our
proposed Transitional NSR Program,
stating that it would not be protective of
air quality. Many other commenters
supported the proposed program,
believing that it would provide needed
flexibility and would not interfere with
achieving attainment. Many
commenters, including some who
supported the Transitional Program,
believed the schedule for submitting
attainment plans and control
requirements was impracticable. Some
commenters opposed the Transitional
106 Of the 135 areas designated as nonattainment
for the 1-hour ozone NAAQS in 1991, 69 have been
redesignated as attainment. See hhtp://
www.epa.gov/oar/oaqps/greenbk/onsum2.html. Of
the 55 nonattainment areas with classifications of
moderate and higher that were required to submit
SIPs and attainment demonstrations, all but 4 have
an approved SIP or have requested redesignation to
attainment.
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NSR Program on legal grounds, arguing
that section VI does not authorize any
NSR flexibility or that appendix S has
been superseded in its entirety by
various sections of the CAA.
We agree with commenters that the
schedule in the proposed rule for
submitting attainment plans to be
eligible for Transitional NSR was
impracticable. On the other hand,
however, we do agree with the many
commenters who urged us to provide
flexible NSR requirements for some
areas. While we have not promulgated
specific criteria for when such
flexibility would apply, we have
promulgated final regulations specifying
that section VI applies where the
original conditions are met (that is, the
attainment deadline has not passed, the
source would not interfere with
attainment by the deadline, and the
source meets all applicable SIP
emissions limitations) and the
Administrator has determined and
provided public notice that section VI
applies.
Regarding the objections to our legal
authority to implement flexible NSR
under appendix S, some commenters
argued that the section VI exemption is
potentially applicable only where an
attainment date for the secondary
standards has not yet passed. However,
this comment ignores the plain language
of section VI, which references primary
standards. It states: ‘‘In some cases, the
dates for attainment of primary
standards have not yet passed due to the
delay in the promulgation of a plan
under this section of the Act.’’ It then
goes on to note that the attainment
deadlines for the secondary standards
may also not yet have passed. It then
states: ‘‘In such cases [a reference to
attainment dates that have not passed
for both primary and second standards],
a new source locating in an area
designated in 40 CFR 81.3000 et seq. as
nonattainment may be exempt from the
conditions of Section IV.A’’ 107 where
certain requirements are met. Thus, the
section VI exemption is applicable
where the attainment date for the
primary standard has not passed.
Other commenters argued that
appendix S and 40 CFR 52.24(k) have
been superseded by or prohibited by
various sections of the CAA. (The EPA
will use the term ‘‘appendix S’’ in this
section of the preamble to refer to these
collectively). Although commenters
made this argument in the context of
opposing the proposed revisions to
section VI of appendix S, this comment
applies to any use of appendix S for
107 Designations are in 40 CFR 81.300. This
citation has been corrected in today’s final rule.
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71681
permitting, including the LAER and
offset requirements of section IV, and
the existing version of section VI. First,
the commenter contended that appendix
S has been superseded by section
181(b)(1) within subpart 2 of the CAA,
under which it believes a newly
designated nonattainment area receives
its nonattainment classification by
operation of law and immediately
becomes subject to all of the
requirements—including section 110,
subpart 1, and subpart 2—that apply to
that classification. The EPA disagrees
with the commenter. As a threshold
matter, even if the commenter were
correct that both subpart 1 and subpart
2 applied upon an area’s nonattainment
classification, the statute provides that
the area may have a period of time to
develop and submit a SIP or SIP
revision meeting the preconstruction
permitting requirements of section 173.
See CAA sections 172(b)(5) and
182(a)(2)(C). For the SIP development
period, part D leaves a gap as to the NSR
requirements applicable to the newly
designated nonattainment area (if the
state’s part D NSR SIP does not
automatically cover the area). This gap
exists even if EPA were to accept the
commenter’s contention that subpart 2
applies. Pursuant to 40 CFR 52.24(k),
this gap is filled by appendix S, which
requires NSR permitting that mirrors
part D, subject to the section VI
exemption.
Additionally, EPA disagrees with the
commenter’s contention that subpart 2
must apply to all newly designated
nonattainment areas. As discussed in
more detail in the preamble to the Phase
1 8-hour ozone implementation rule (69
FR 23951), EPA has determined that it
has discretion in determining whether
subpart 2 applies to these areas because
subpart 2 does not dictate whether it
applies where the 1-hour design value
falls below the lowest value in the
subpart 2 classification table. The EPA
has described in that rule the
circumstances in which subpart 2
applies.
The commenter also contends that
section 193 has superseded appendix S.
The EPA disagrees. The commenter
relies on the following language in
section 193: ‘‘No control requirement in
effect, or required to be adopted by a[]
* * * [implementation] plan in effect
before November 15, 1990, in any area
which is a nonattainment area for any
air pollutant may be modified after
November 15, 1990, in any manner
unless the modification insures
equivalent or greater emission
reductions of such air pollutant.’’
However, this part of section 193 is of
no relevance to appendix S because
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appendix S does not replace any
existing SIP requirements. An area is
only required to apply appendix S
where it does not have a part D NSR SIP
covering permitting for the 8-hour
standard. In other words, it covers only
the gap in the SIP caused by the lack of
a part D NSR program for the relevant
NAAQS, and is supplemental to any
existing SIP requirements.108
The commenter also believes that use
of appendix S for permitting would
violate section 110(l), which provides,
in relevant part, that: ‘‘The
Administrator shall not approve a
revision of a plan if the revision would
interfere with any applicable
requirement concerning attainment and
reasonable further progress * * *’’ The
commenter states that nonattainment
preconstruction permitting
requirements ‘‘concern[] attainment and
reasonable further progress,’’ so if a SIP
is already written such that
nonattainment NSR will apply in an
area as soon as it is designated
nonattainment under the 8-hour
standard, then any revision that would
thwart the automatic effectiveness of
those requirements would violate
section 110(l). Again, appendix S is not
an amendment to a SIP, and does not
replace any existing SIP requirements.
Rather, it covers the gap caused by the
lack of a part D NSR SIP for the newly
designated nonattainment area. If a SIP
applies the nonattainment NSR program
to a newly designated nonattainment
area, appendix S does not apply to that
area. [See 40 CFR 52.24(k) and appendix
S, section I.] For these same reasons, the
commenter is incorrect that NSR
permitting under appendix S violates
Congressional intent not to relax
pollution control requirements when
the NAAQS are revised, as expressed in
section 172(e). One commenter stated
that any major revisions to appendix S
should be subject to additional noticeand-comment because such revisions
could not be a logical outgrowth of the
June 2, 2003 proposal. We disagree that
the public lacked adequate notice and
opportunity to comment. The changes to
incorporate the 1990 CAA Amendments
to part D of title I of the CAA (for
example, major stationary source
108 Although EPA did state in the proposal that
States with already applicable part D NSR SIPs may
choose to amend their SIPs to allow them to take
advantage of the proposed revisions to section VI
(68 FR 32844 n.67), the decision not to go forward
with the section VI revisions as proposed makes
that issue moot. New source review under section
VI, as finalized, will involve notification by the
Administrator that it applies for new sources
meeting the section VI criteria in areas lacking
approved part D NSR programs, rather than
replacement of a NSR program in the SIP with an
alternative NSR program.
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thresholds, significant emission rates,
and offset ratios) and the revisions to
the rule governing creditable emissions
reductions from shutdowns and
curtailments were proposed in 1996 for
the major NSR program, including
appendix S (61 FR 38252). The method
for making designations and
classifications specific to the 8-hour
standard under subparts 1 and 2 was
proposed on June 2, 2003 (68 FR 32802).
Although rule language was not
proposed specifically for appendix S,
the rule language could be discerned
from the rule language proposed for
§ 51.165, as appendix S states it is an
interpretation of 40 CFR subpart I,
which includes § 51.165. Additionally,
the CAA does not require that the
Agency provide notice of the exact rule
language that will be finalized, but
rather that the Agency provide a
statement of basis, including, among
other things, the major legal
interpretations and policy
considerations underlying the proposal.
These were provided by the 1996 and
2003 proposals and, in the case of the
removal of the 50 tpy exemption, in the
1979 proposal.
With regard to the changes to section
VI of appendix S, the Agency notes that
because it declined to adopt the
extensive revisions proposed, the
changes are minimal. The additional
condition regarding approval by the
Administrator is a logical outgrowth of
the proposed revisions to section VI,
which explained that the Agency’s goal
was to limit the applicability of section
VI to situations where the new source
would comply with all of the conditions
in section VI, most notably, not
interfering with an area’s ability to meet
its attainment deadline.
5. Comments on Changes To Identify
NOX as an Ozone Precursor in
Attainment and Unclassifiable Areas
Commenters supported our proposal
to amend our PSD regulations to
expressly include NOX as an ozone
precursor. We agree with these
commenters.
6. Comments on Removing the 50-Ton
Exemption
For comments on removing the 50-ton
exemption, see the discussion in the
1980 final rules at 45 FR 52689–90.
D. NSR Implementation Under the 8Hour Ozone NAAQS
As promulgated at 69 FR 23858, the
designation and classifications for the 8hour NAAQS became effective June 15,
2004. The transition to NSR under the
8-hour NAAQS raises multiple
implementation questions, which are
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discussed below. We intend to address
additional issues in the future.
1. Areas That Have Never Been
Nonattainment for Ozone
If an area has never been
nonattainment for ozone and is
nonattainment for the 8-hour ozone
NAAQS, it became subject to
nonattainment major NSR under the 8hour standard on June 15, 2004. Permits
for new or modified major stationary
sources in such areas issued on or after
June 15, 2004 must reflect NSR
requirements under the 8-hour ozone
NAAQS. Some States may already have
in place a part D major source
permitting program applicable to newly
designated 8-hour ozone nonattainment
areas. For nonattainment areas in States
whose SIPs contain a generic
requirement to issue part D major source
NSR permits in areas designated as
nonattainment, the State can continue to
issue nonattainment NSR permits for
new and modified major stationary
sources under the part D NSR SIP on or
after June 15, 2004. For a nonattainment
area in a State with a SIP that
specifically lists the areas in which part
D NSR applies, or in an area that
currently has no nonattainment plan or
otherwise lacks authority to implement
NSR for the 8-hour ozone NAAQS
through a SIP-approved permitting
program, there will be an interim period
between June 15, 2004 and the date that
the State amends its SIP either to list
any new nonattainment area(s) or to
include a part D plan. During this
interim period, pursuant to § 52.24(k),
permits for new and modified major
stationary sources in such areas must be
consistent with the requirements in
appendix S. Where a State or local
agency lacks authority to issue permits
consistent with appendix S, EPA is the
reviewing authority.
States may not issue PSD permits to
address major NSR obligations arising
from nonattainment classifications. As
we stated at 69 FR 23992, PSD permits
may not be issued after June 14, 2004,
to satisfy permitting obligations under
the 8-hour nonattainment designation.
We clarify here that States are not
precluded from issuing PSD permits
based on the 1-hour attainment
classifications, but such actions do not
relieve States or sources from
addressing nonattainment NSR
obligations based on the 8-hour
classification.
2. Areas That Are Nonattainment for the
1-Hour NAAQS and the 8-Hour NAAQS
New source review under the 8-hour
NAAQS became effective in 8-hour
nonattainment areas on June 15, 2004.
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Currently, the 1-hour NAAQS remains
in effect. Thus, there is a period of time
when major NSR requirements for both
the 1-hour and 8-hour NAAQS applies
in an area or parts of an area. During
this period, different major stationary
source thresholds and offset ratios may
apply in a given nonattainment area
under the 1-hour and 8-hour ozone
NAAQS, due to a change in its
classification. Permits issued during this
transition period will assure compliance
with both programs if the permit
requirements are based on the highest
classification that applies to the area. If
the area’s 1-hour classification is higher
than its 8-hour classification, the NSR
SIP program under the 1-hour NAAQS
will satisfy the requirements of both
programs. If the 8-hour classification is
higher, then the NSR program under the
8-hour classification will determine the
NSR requirements. For example,
suppose a source is locating in an area
that is now classified as moderate
nonattainment under the 8-hour ozone
NAAQS but was previously classified as
a serious ozone nonattainment area
under the 1-hour NAAQS. Any permit
the State issues during the transition
would be based on the 50 tpy major
stationary source threshold and at least
1.2:1 offset ratio that apply to serious
ozone nonattainment areas under the 1hour ozone NAAQS.
Pursuant to 40 CFR 50.9(b), EPA
revoked the 1-hour NAAQS effective
June 15, 2005 for areas designated for
the 8-hour ozone standard effective June
15, 2004. We anticipate that, upon
revocation of the 1-hour ozone NAAQS,
States will submit requests for approval
of SIP revisions removing NSR
requirements based on the 1-hour
classifications, where such SIP revisions
are necessary to achieve this result. At
69 FR 23985, we stated that upon
revocation of the 1-hour ozone NAAQS,
for any area that was designated
nonattainment for the 1-hour ozone
NAAQS, the area’s implementation plan
provisions satisfying sections 172(c)(5)
and 173 (including provisions satisfying
section 182) based on the area’s
previous 1-hour ozone NAAQS
classification are no longer required
elements of an approvable
implementation plan. We also indicated
that a State may request approval of a
SIP revision to remove its 1-hour
nonattainment NSR program from its
SIP. We further stated that we will
approve such changes to a state’s SIP
because we have determined based on
110(l) of the CAA that such changes will
not interfere with any state’s ability to
reach attainment of the 8-hour standard
and will be consistent with RFP.
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On June 29, 2004, we received a
Petition for Reconsideration from
Earthjustice concerning these statements
on removing the 1-hour NSR SIP and on
the 110(l) determination related to
removing the 1-hour NSR SIP. You can
find a copy of this Petition for
Reconsideration at https://www.epa.gov/
ttn/naaqs/ozone/o3imp8hr/
materials.html. We have granted
reconsideration on these two narrow
NSR issues in the Phase 1 Ozone
Implementation Rule. We published a
proposed rule on these issues on April
4, 2005 (70 FR 17018). We published a
final rule on these two issues on July 8,
2005 (70 FR 39413).
As we stated at 69 FR 23986 (Column
1), emission limitations and other
requirements in major NSR permits
issued under 1-hour NSR programs will
continue to be in force when the 1-hour
NAAQS is revoked. For example,
suppose an existing source is located in
an area classified as serious
nonattainment under the 1-hour ozone
NAAQS and has a nonattainment major
NSR permit based on its potential to
emit 75 tpy VOC. That major NSR
permit (including emission limitations
and other requirements) remains in
force on and after June 15, 2005 even if
the area that the source is located in is
now classified moderate nonattainment
(with a major stationary source
threshold of 100 tpy) under the 8-hour
ozone NAAQS.
3. Part D NSR SIP Submittals
Today’s final action on the regulations
at § 51.165 establishes the minimum
requirements for part D SIPs
implementing major NSR under the 8hour NAAQS. Some States may find it
unnecessary to revise their SIPs to
implement NSR under the 8-hour
NAAQS. This can happen when the
approved part D NSR and ozone
classification scheme SIP applies to any
areas designated as nonattainment
under section 107 of the CAA or listed
in 40 CFR 81.300 et seq. In States that
do not have authority to implement a
part D program for the 8-hour NAAQS,
a SIP revision for major NSR under the
8-hour NAAQS must be submitted.109
The revised implementation plan must
include requirements to implement the
provisions of sections 172(c)(5) and 173
of the CAA based on the area’s 8-hour
ozone NAAQS classification under 40
CFR part 81, and the provisions of
§ 51.165 as amended in today’s final
action.
109 As noted in section V.D.2 of this preamble, we
will complete our reconsideration on issues related
to NSR SIP submittals and announce our final
action by May 20, 2005.
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States must submit SIP provisions
incorporating today’s final rules at
§ 51.165 no later than June 15, 2007,
which is 3 years after designation. This
schedule is consistent with the schedule
set forth in CAA sections 172(b) and
110(a)(1).110 This date facilitates
coordination of NSR program changes
with the submission of the attainment
plan, which is also due within 3 years.
Part D NSR SIPs to implement the 8hour NAAQS should reflect the
requirements of today’s final action, as
well as the requirements in subpart X of
part 51 promulgated on April 30, 2004
at 69 FR 23951. Before EPA can approve
a program into the SIP to implement a
nonattainment major NSR program for
the 8-hour ozone NAAQS, State and
local agency programs implementing
part D (nonattainment NSR permit
program in § 51.165) must include
today’s changes as minimum program
elements. States must also submit SIP
provisions incorporating today’s final
rules at § 51.166 no later than June 15,
2007.
4. Effective Date for Today’s
Requirements
All of these changes will take effect in
the NSR permitting programs for
nonattainment areas codified at
appendix S of part 51 and § 52.24 on
January 30, 2006. This means that
appendix S as amended in today’s final
action will apply on January 30, 2006 in
any nonattainment area without an
approved part D NSR SIP that applies to
major sources in the nonattainment area
for the nonattainment pollutant. These
changes will take effect in the Federal
PSD program (codified at 40 CFR 52.21)
on January 30, 2006 in any area without
an approved PSD program, for which we
are the reviewing authority, or for which
we have delegated our authority to issue
permits to a State or local reviewing
authority. The provisions of § 51.165
and § 52.24, as amended in today’s final
action, also apply on January 30, 2006.
State and local agency programs
implementing part C (PSD permit
program in § 51.166) and part D
(nonattainment NSR permit program in
§ 51.165) are effective when they are
approved by us.
5. Requirements for Offsets
Offsets under CAA section 173 are
typically based on emissions reductions
110 CAA Section 182(a)(2)(C)(i) requires NSR SIPs
to meet the 1-hour ozone NAAQS to be submitted
within 2 years after the date of the enactment of the
1990 CAA Amendments. This requirement has been
met by the submission of NSR SIPs due on
November 15, 1992, which EPA requested on April
16, 1992 at 57 FR 13499. We have interpreted the
2-year schedule not to apply for the NSR SIPs
implementing the 8-hour ozone NAAQS.
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achieved through installation of control
technology, shutdown of a source, or
curtailment of production or operating
hours below baseline levels. Offsets
must meet several requirements set forth
in section 173 of the CAA, including the
following:
• Offsets must be obtained by the
time the source is to commence
operation [CAA section 173(a)(1)(A)].
• Offsets must be consistent with RFP
[CAA section 173(a)(1)(A)].
• Offsets must be federally
enforceable before permit issuance
[CAA section 173(a)].
• Offsets must be in effect and
enforceable by the time a new or
modified source commences operation
[CAA section 173(c)(1)(B)].
• Emissions reductions that are
otherwise required under the CAA
cannot be creditable as offsets [CAA
section 173(c)(2)].
• Offsets must come from a source in
the same nonattainment area, unless it
comes from an area that has an equal or
higher nonattainment classification and
the emissions from such other area
contribute to a violation of the national
in the nonattainment area in which the
source is located [CAA section
173(c)(1)].
If an emission reduction credit
(including an emission reduction credit
generated from a shutdown or
curtailment) has been used to meet ROP
or RFP milestones, it is not available for
use as an offset or in netting. This is
because section 173(c)(2) of the CAA
prohibits use of emissions reductions as
offsets where the reductions are
‘‘otherwise required by the Act.’’ Thus,
reductions that are used to meet Federal
requirements, including SIP-approved
ROP and RFP obligations under CAA
section 182, are not creditable. Where
emissions reductions pre-dating 2002
have not been used to meet ROP and
RFP obligations, or other Federal
requirements, CAA section 173(c)(2)
does not prohibit their use. Thus, EPA
believes that such credits may be used
as offsets consistent with the CAA. The
EPA encourages States to allow sources
to use pre-2002 banked emissions
reductions credits (that is, those that
were generated before January 1, 2002,
which is the first day of the emissions
inventory base year for the base year
inventory used to develop the
attainment demonstration) for offsetting
purposes. States may do so as long as
the banked credits meet all other offset
creditability criteria and such credits are
included by States as growth in
developing the attainment
demonstration as discussed elsewhere
in this preamble. See also 57 FR 13508–
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09. The credits must be certified and
approved for such purposes.
Additional requirements apply to
credits generated from shutdowns or
curtailments. Pursuant to today’s final
rule, States may revise their SIPs to
remove the requirement for an approved
attainment demonstration as a condition
of using shutdown/curtailment credits
pre-dating the new source application.
Under the revised rule, emissions from
the shutdown/curtailed source can be
creditable if they are included in the
projected emissions inventory used to
develop the attainment demonstration.
For emissions reductions from
shutdowns or curtailments to be
creditable for offset purposes, the State
must also certify that emissions from the
shutdown or curtailed source have not
been used and are not necessary to meet
any other requirement under the CAA,
including RFP or ROP.
Use of emission reduction credits
banked before the base year (that is,
those generated before January 1, 2002)
for netting continues to be available to
the extent allowed under State rules.
However, because these emission
reduction credits represent emissions
that are not included in the 2002 base
year inventory, States should consider
net emission increases occurring on or
after January 1, 2002 as growth even
though, for applicability purposes, the
source does not have a significant net
emissions increase.
VI. Final Rule for RFG
A. Introduction
This portion of the rule addresses
what effect the transition to the 8-hour
NAAQS will have on certain aspects of
the federal RFG program. Under the
CAA, the RFG requirements apply in
certain areas of the country. First, there
are nine areas that Congress identified
pursuant to section 211(k)(10)(D) of the
CAA as mandatory RFG areas. Second,
there are five RFG areas that are
mandatory areas based on their
reclassification to a severe ozone
classification. These areas are typically
called ‘‘bump-up’’ areas. See CAA
section 211(k)(10)(D), 211(k)(6), and
211(k)(5). Finally, there are a number of
areas that have voluntarily opted in to
the RFG program. The purpose of the
RFG program is to improve air quality
through the use in certain areas of
gasoline that is reformulated to reduce
motor vehicle emissions of tropospheric
ozone-forming compounds and toxics,
as set forth in section 211(k)(1) of the
CAA.
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B. Background
In the Phase 1 Rule, EPA addressed
two key issues regarding the transition
from the 1-hour NAAQS to the 8-hour
NAAQS. First, when will the 1-hour
NAAQS no longer apply (i.e., be
‘‘revoked’’)? Second, what protections
are in place to ensure that, once the 1hour NAAQS is revoked, air quality will
not degrade and that progress toward
attainment will continue as areas
transition from implementing the 1-hour
NAAQS to implementing the 8-hour
NAAQS?
On the first issue, EPA decided that
the 1-hour NAAQS will be revoked in
full, including the associated
designations and classifications, 1 year
following the effective date of the
designations for the 8-hour NAAQS.
Most areas were designated effective
June 15, 2004, and for those areas the 1hour NAAQS and the related
designation and classification will no
longer apply as of June 15, 2005.
On the second issue, the antibacksliding portion of the Phase 1 rule
established that all areas designated
nonattainment for the 8-hour ozone
NAAQS, that were designated
nonattainment for the 1-hour NAAQS at
the time of designation for the 8-hour
NAAQS, remain subject to mandatory
control measures that applied by virtue
of the area’s classification for the 1-hour
NAAQS. These control measures are
called ‘‘applicable requirements.’’ 111
Also, EPA decided that areas designated
nonattainment for the 8-hour NAAQS,
that were designated attainment subject
to a section 175A maintenance for the
1-hour NAAQS at the time of
designation for the 8-hour NAAQS,
must continue to implement all
applicable requirements that have been
approved into the SIP.112
In the June 2003 proposal, EPA
identified Federal RFG as an applicable
requirement (68 FR 32867). In the final
rule, however, EPA did not include RFG
in the list of applicable requirements.
The EPA instead clarified that RFG is
required under a Federal program, and
thus differs significantly from the other
programs on the list of applicable
requirements, which are developed and
adopted by States for inclusion in the
111 In the Phase 1 Rule, EPA defined applicable
requirements as those control measures in place as
of the date of signature of the Phase 1 Rule, (i.e.,
April 15, 2004). The EPA recently reconsidered this
issue and changed this date to the effective date of
the 8-hour designations—for most areas this would
be June 15, 2004 (70 FR 30596).
112 While the Phase 1 Rule also addressed the
transition to the 8-hour NAAQS for areas recently
designated as attainment for the 8-hour NAAQS, all
relevant RFG areas are designated as 8-hour
nonattainment areas (69 FR 23858).
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SIP. The EPA recognized that various
issues exist regarding the scope and
applicability of the RFG program during
and after implementation of the 8-hour
NAAQS that need further clarification.
The EPA stated that we were still
considering how to treat RFG and that
we would address these issues in an
action separate from the Phase 1 Rule
(69 FR 23973). Thus, EPA did not
include RFG in the list of applicable
requirements in the Phase 1 Rule, and
EPA made no decision at that time
concerning RFG treatment in the
transition to the 8-hour NAAQS.
C. What action is EPA taking?
As discussed in more detail below,
EPA is clarifying today that the nine
original mandatory RFG areas, as well as
most other areas that have become
mandatory RFG areas by being ‘‘bumped
up’’ to a severe classification, will
continue to be required to use RFG at
least until they are redesignated to
attainment for the 8-hour NAAQS. The
EPA is not deciding at this time what
will happen when the original nine
areas and the bump-up areas covered by
this rule are redesignated to attainment
for the 8-hour NAAQS. The EPA is also
not deciding at this time what RFG
requirements apply for any bump-up
areas that are redesignated to attainment
for the 1-hour NAAQS before the 1-hour
NAAQS is revoked. The only such area
that was redesignated to attainment
prior to revocation of the 1-hour
NAAQS is Atlanta, Georgia. That issue
will be addressed in an action separate
from this final rule.
The RFG areas that opted into the program
will continue to be RFG areas unless they
opt-out pursuant to EPA’s opt-out
regulations. The transition to the 8-hour
NAAQS does not change the terms and
conditions that apply to opting-out of the
RFG program. Likewise, EPA’s current rules
on opting-in to RFG will apply in the same
manner under the 8-hour NAAQS as under
the 1-hour NAAQS—i.e., 8-hour
nonattainment areas that are classified as
marginal or above under subpart 2 will be
able to opt-in to the RFG program.
D. Why is EPA taking this action?
1. RFG Mandatory Areas
Under section 211(k)(5), RFG is
required in any ‘‘’’covered area.’’ The
term ‘‘covered area’’ is defined in
section 211(k)(10)(D) as:
[t]he 9 ozone nonattainment areas having a
1980 population in excess of 250,000 and
having the highest ozone design value during
the period 1987 through 1989 shall be
‘‘covered areas’’ for purposes of this
subsection. Effective one year after the
reclassification of any ozone nonattainment
area as a severe ozone nonattainment area
under section 181(b) of this title, such severe
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area shall also be a ‘‘covered area’’ for
purposes of this subsection.
In the June 2003 proposed Phase 1
Rule, EPA proposed that RFG be
considered an applicable requirement
and treated like the various mandatory
control obligations that States remained
obligated to adopt and implement after
revocation of the 1-hour NAAQS. Under
that proposal, the nine original
mandatory areas and all bump-up areas
would have continued to be covered
areas after revocation of the 1-hour
NAAQS. For the reasons discussed
below, EPA is adopting this basic
approach for the nine original
mandatory areas as well as those bumpup areas covered by this final rule.
a. Nine Original Mandatory Areas
The first sentence of section
211(k)(10)(D) identifies certain covered
areas by reference to their 1980
population and their 1987–1989 ozone
design value. The nine areas that meet
these criteria are Los Angeles, San
Diego, Hartford, New York,
Philadelphia, Chicago, Baltimore,
Houston, and Milwaukee. It is clear that
transition to the 8-hour NAAQS does
not change the historical facts that
define these areas. In addition, all of
these areas are designated as
nonattainment areas under the 8-hour
NAAQS. Thus, they will continue to be
‘‘ozone nonattainment areas’’ until they
are redesignated to attainment for the 8hour NAAQS. Revocation of the 1-hour
NAAQS and transition to the 8-hour
NAAQS does not change the fact that
each of these nine mandatory areas will
continue to meet the definition of
covered area at least until it is
redesignated to attainment for the 8hour NAAQS. As discussed below, EPA
is not deciding at this time whether
these areas will continue to be covered
areas upon redesignation to attainment
for the 8-hour NAAQS. The EPA
reserves any determination on that issue
for a future action.
The EPA believes that this is a
straightforward and clear application of
the plain language of the statute.
However, even if the statutory terms
were considered ambiguous on this
issue, EPA believes that the same
statutory interpretation and policy
considerations described below for the
‘‘bump-up’’ areas covered by this final
rule apply to the nine mandatory areas
and would lead EPA to require
continued use of RFG in the nine areas
at least until they are redesignated to
attainment for the 8-hour NAAQS.
Since EPA regulations at 40 CFR
80.70 currently define the term
‘‘covered area’’ to include the original
nine mandated areas, no change in EPA
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regulations is needed at this time. The
EPA will address in a future action what
RFG requirements, if any, apply to the
original nine RFG covered areas when
they are redesignated to attainment for
the 8-hour NAAQS.
b. Bump-Up Areas
The second sentence of section
211(k)(10)(D) identifies areas that
become covered areas because they have
been reclassified as a severe area under
CAA section 181(b). These are called
‘‘bump-up’’ areas. To date, five areas
have been reclassified to severe for the
1-hour NAAQS. They became RFG
covered areas 1 year after their
reclassification—Baton Rouge, Atlanta,
Sacramento, San Joaquin Valley, and
Washington, DC—which was already an
opt-in area.
The areas that are RFG covered areas
based on the bump-up provision were
designated as ozone nonattainment
areas and classified by operation of law
at the time of the 1990 CAA
Amendments, and their bump-up to
severe occurred by operation of law
based on EPA’s determination under
section 181(b) that the areas failed to
attain the 1-hour NAAQS by the
applicable attainment date. Thus, their
reclassification to severe was not based
on a determination that their air quality
met the severe area design value.
Instead, reclassification was based on
their failure to meet the applicable
attainment date. The bump-up to severe
has two effects—a later attainment date
is set for the area, and a variety of
additional control measures become
mandatory for the area. The Federal
RFG program becomes a mandatory
control measure in an area 1 year after
it is bumped up to a severe
classification.
There are two ways that a bump-up
area classified as severe could lose its
severe classification. First, it could do
so through redesignation to attainment
for the 1-hour NAAQS. (This is no
longer an option for areas where the 1hour NAAQS was revoked on June 15,
2005.) Second, since the 1-hour NAAQS
is revoked, a bump-up area will no
longer be classified as severe under the
1-hour NAAQS and may have a lower
classification (i.e., subpart 1, marginal,
moderate or serious) for the 8-hour
NAAQS. This rule only addresses the
second situation.
The bump-up areas in this second
situation are all designated as 8-hour
ozone nonattainment areas, with
classifications under the 8-hour NAAQS
that are a lower classification than
severe. This raises the issue of whether
the bump-up areas that lose their severe
classification through revocation of the
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1-hour NAAQS should continue to be
covered areas once the 1-hour NAAQS
and the areas’ related severe
classifications are revoked.
The EPA believes that section
211(k)(10)(D) is ambiguous on the issue
of whether a bump-up area continues to
be a covered area when it is no longer
classified as severe. The text of the
provision could be read to set the
defining criteria as the occurrence of
reclassification to severe, a historical
fact that does not change based on
subsequent changes in classification. It
could also be read as identifying areas
that are reclassified to severe, but as
leaving unresolved what happens when
they are no longer so classified. Given
this ambiguity, EPA has discretion to
determine whether section 211(k)(10)(D)
authorizes removal of a bump-up area
from the RFG program when it is no
longer classified as severe, and to set
appropriate criteria for such removal.113
For a bump-up area covered by this
rule, it is instructive to consider what
would happen if EPA had never revised
the 1-hour NAAQS. In that case, the
area would continue to be a covered
area at least until it was redesignated to
attainment for the 1-hour NAAQS.
While section 211(k)(10)(D) does not
directly address whether a bump-up
area would continue to be a covered
area after redesignation, it is clear that
if EPA had never revised the 1-hour
NAAQS, the area would continue to be
a covered area at least as long as it was
a severe area, and it would be a severe
area as long as it was still designated as
an ozone nonattainment area.
The EPA does not believe that
Congress would have intended that
removal of the severe classification
based solely on revocation of the less
protective 1-hour NAAQS should result
in backsliding of the RFG requirement.
For example, as noted above, if EPA had
not adopted a more protective 8-hour
NAAQS, with the related revocation of
the 1-hour NAAQS and removal of the
severe classification, then the bump-up
areas covered by this rule would remain
covered areas at least until they were
redesignated to 1-hour attainment, at
which point they would no longer be
designated as ozone nonattainment
areas. Here, the removal of the severe
classification is through revocation of
the 1-hour NAAQS, not through
113 While this final rule only addresses bump-up
areas that lose their severe classification based upon
revocation of the 1-hour NAAQS, the ambiguity in
section 211(k)(10)(D) extends to all bump-up areas,
including those not covered by this final rule. As
noted above, EPA intends to address and resolve
this ambiguity for any bump-up areas not covered
by this rule in an action separate from this final
rule.
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redesignation to 1-hour attainment.
These bump-up areas are still
designated as ozone nonattainment
areas. The EPA believes the removal of
the severe classification for these areas
as a result of revocation of the 1-hour
standard should not lead to removal of
the RFG requirement. The EPA believes
the RFG requirement should continue
beyond revocation of the 1-hour
NAAQS, and it should continue at least
until the areas are redesignated to
attainment for the 8-hour NAAQS. This
does not change or affect any discretion
EPA may otherwise have under the RFG
provisions to modify or remove RFG
requirements.
This is consistent with the approach
taken in the Phase 1 Rule for the
mandatory obligations that EPA
identified there as ‘‘applicable
requirements.’’ In that rule, EPA
determined that a number of provisions
of the CAA evidence Congress’ intent
that certain obligations that applied to
an area by virtue of the area’s
classification for the 1-hour NAAQS
should continue to apply despite EPA’s
determination the 1-hour NAAQS is no
longer necessary to protect public
health. While some of these various
statutory provisions do not have direct
bearing on Federal RFG and section
211(k), the issues are closely analogous.
For example, the inclusion of a bumpup area in the RFG program is integrally
tied to the subpart 2 provisions that
establish the original classification and
attainment date for an area and its later
reclassification as severe under section
181(b). The Supreme Court cautioned in
Whitman v. American Trucking Assn.,
531 U.S. 457 (2001), against EPA
making subpart 2 ‘‘abruptly obsolete.’’
Although the RFG requirement itself is
not set forth in subpart 2, the
requirement to use it in severe bump-up
areas is tied directly to the
classifications that arise by operation of
subpart 2. Thus, it would appear that
the Supreme Court’s caution should be
as relevant for RFG bump-up areas as it
is for the subpart 2 control obligations.
For further discussion of the reasoning
behind anti-backsliding provisions in
the Phase 1 Rule, see 69 FR 23951,
23972. The reasoning presented there
also supports EPA’s interpretation of
section 211(k)(10)(D) regarding RFG
requirements for bump-up areas covered
by today’s rule.
One issue addressed in the Phase 1
Rule involved setting the trigger date for
determining what 1-hour SIP-related
requirements would continue as
mandatory ‘‘applicable requirements’’
after revocation of the 1-hour NAAQS.
The EPA considered three possible
trigger dates for the Phase 1 Rule—the
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date of signature of the Phase 1 Rule, the
effective date of the 8-hour
nonattainment designation, and the date
of revocation of the 1-hour NAAQS.114
For purposes of this final rule, it is not
necessary to decide on a similar date for
determining the continued applicability
of RFG for these bump-up areas. Under
all potential trigger date options, RFG
would be a requirement on the trigger
date for the bump-up areas covered by
this rule, as they would all be classified
as severe areas on any of the trigger
dates that were considered.
Based on the above, EPA has
determined that bump-up areas that lose
their severe classification based solely
on revocation of the 1-hour NAAQS
should remain RFG covered areas at
least until they are redesignated to
attainment for the 8-hour NAAQS. As
indicated above, this does not change or
affect any discretion EPA may otherwise
have under the RFG provisions to
modify or remove RFG requirements.
2. RFG Opt-In Areas
Under section 211(k)(6) of the CAA,
certain ozone nonattainment areas may
opt-in to the RFG program. That
provision limits opt-ins to areas
‘‘classified under subpart 2 of part D of
title I as a marginal, moderate, serious,
or severe Area.’’ The EPA’s regulation
implementing this provision is at 40
CFR 80.70(j), which states that ‘‘[a]ny
* * * area classified under 40 CFR part
81, subpart C as a marginal, moderate,
serious, or severe ozone nonattainment
area may be included as a covered area
on petition of the Governor of the State
in which the area is located.’’
Some areas designated nonattainment
for the 8-hour NAAQS are subject only
to the planning requirements of subpart
1, while others are also subject to the
planning requirements of subpart 2 of
part D of title I. The 8-hour
nonattainment areas subject to the
planning requirements of subpart 2 were
all classified as marginal, moderate,
serious, or severe (69 FR 23951, 23954;
April 30, 2004). The 8-hour
nonattainment areas subject only to
subpart 1 are not subject to those
classifications. Thus the only 8-hour
nonattainment areas that would be able
to opt-in under the terms of section
80.70(j) are areas classified under
subpart 2 as marginal, moderate,
serious, or severe, consistent with the
terms of section 211(k)(6).
In a prior rulemaking, EPA initially
expanded the scope of this opt-in
provision, interpreting section 211(k)(6)
as authorizing opt-in for any current or
prior 1-hour ozone nonattainment area,
114 May
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including areas that were not classified
marginal or above. In that rulemaking,
EPA reserved judgment on whether it
would apply the same expanded
interpretation to areas designated as
nonattainment for the then recently
adopted 8-hour NAAQS (63 FR 52094,
52101; September 29, 1998). The EPA’s
expanded view of the scope of section
211(k)(6) was subject to judicial review
and was rejected as inconsistent with
the terms of section 211(k)(6), as
‘‘Congress provided for opt-in only for
areas classified as marginal, moderate,
serious, or severe.’’ API and NPRA v.
EPA, 198 F. 3d 275, 281 (D.C. Cir. 2000).
The text of EPA’s current opt-in
regulation is limited as a result, is
consistent with the limitation in section
211(k)(6), and only allows opt-in for
areas classified under subpart 2 as
marginal or above. The EPA interprets
the current opt-in regulation as allowing
opt-in for those 8-hour nonattainment
areas that are classified as marginal or
above under subpart 2. The EPA
believes this is consistent with section
211(k)(6) and with the API and NPRA
case, and therefore sees no need to
revise the current regulation.
E. Future Proceedings
Today, EPA is reserving for future
consideration what RFG requirements, if
any, should apply to the nine
mandatory areas and the bump-up areas
covered by this final rule when they are
redesignated to attainment for the 8hour NAAQS. The Phase 1 Rule
provides that upon redesignation to
attainment for the 8-hour NAAQS, SIP
measures may be moved to the
contingency measure portion of the SIP
if the State demonstrates in accordance
with section 110(l) that doing so will
not interfere with maintenance of the 8hour NAAQS or any other applicable
requirement of the CAA (69 FR 23951,
23998; April 30, 1994)(40 CFR
51.905(b)). This SIP process does not
apply to RFG, since it is not a SIP
measure. However, EPA will need in the
future to consider whether it should
develop a similar scheme for RFG.
Specifically, EPA will consider the
following issues. Should a State be
allowed to drop the RFG requirement
when a covered area is redesignated to
attainment for the ozone NAAQS, or
should the requirement remain in place?
If it can be dropped, under what
conditions? Once dropped, would the
requirement to use it spring back if a
State backslides into nonattainment? If
it springs back, what lead time should
be provided? If it does not spring back
automatically, should EPA nevertheless
reserve the discretion to require a
former covered area to use RFG if it
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slips back into nonattainment? The EPA
anticipates considering these and
related issues in a future notice-andcomment proceeding. The EPA is not
soliciting comment on these issues at
this time.
As noted above, EPA is not deciding
at this time what RFG requirements
apply for any bump-up areas that are
redesignated to attainment for the 1hour NAAQS before the 1-hour NAAQS
is revoked. The only such area that was
redesignated to attainment prior to
revocation of the 1-hour NAAQS is
Atlanta, Georgia. That issue will be
addressed in an action separate from
this final rule.
F. Miscellaneous Administrative
Changes to the RFG Regulations
Today, EPA is making a nonsubstantive formatting change to its RFG
regulations. The regulations are
currently structured to envision a
complete list of all bump-up areas
required to use RFG. However, EPA has
not made timely amendments to these
regulations to keep the list of bump-up
areas up to date, so the regulations may
appear to be misleading. Although EPA
could take the opportunity to revise the
list at this time to include all current
bump-up areas, EPA believes that it
would be best to amend the regulations
to omit the list. The EPA will maintain
a list of bump-up areas on its RFG Web
site: https://www.epa.gov/otaq/rfg/
whereyoulive.htm. This list can more
quickly and easily be amended in the
future to be kept up-to-date.
G. Comments and Responses
Comment: One commenter noted EPA
has proposed that all areas designated 8hour nonattainment remain subject to
control measures that apply by virtue of
the area’s classification for the 1-hour
standard. For control measures that the
State has not adopted, the State remains
obligated to adopt and submit such
controls. The commenter believes that
such a policy may have unintended
negative consequences for the few areas
that recently bumped-up as the result of
EPA’s failed transport policy.
Specifically, most of these areas will
bump-up to either the serious or severe
subpart 2 classification triggering higher
classification controls. Some of these
controls, and in particular VOC controls
and RFG, may not benefit and/or may
even be counterproductive to attaining
the 8-hour standard. The commenter
believes that for these few areas that
recently bumped-up as the result of the
failed transport policy, EPA should
allow those States to evaluate the
relative ozone reduction benefits of the
higher classification controls and, where
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appropriate, substitute for more
effective ozone controls. The commenter
believes this is important to ensure
continued progress towards attainment
in the most cost-effective manner.
Response: Congress specified use of
RFG for areas bumped up to severe
nonattainment status without providing
an opportunity for such areas to
substitute other controls that may be
more effective. Specifying mandated
controls for areas that have failed to
achieve timely attainment is one of the
specific provisions added by Congress
in the 1990 CAA Amendments. The
EPA does not believe that the transition
to a more protective 8-hour standard
should result in less restrictive
requirements for RFG, such as allowing
substitution of other control measures
for RFG, than would apply if EPA had
never revised the 1-hour standard.
Substitution was not allowed under the
1-hour standard.
However, EPA notes that Congress
established a mechanism to address
adverse impacts of the RFG program on
attainment of the NAAQS by
authorizing EPA to waive the RFG
oxygen content requirement where it is
clearly demonstrated that the oxygen
content requirement prevents or
interferes with NAAQS attainment
[section 211(k)(2)(B)]. This provides
additional support for the view that the
transition to the 8-hour standard should
not establish a right to substitute other
measures for RFG as the statute provides
a different way to address potential
concerns over the effectiveness of RFG
in addressing ozone attainment.
Comment: The local experts have
estimated that RFG will cost consumers
in the 5-parish nonattainment area an
additional $48 to $72 million annually.
The Department of Environmental
Quality, using MOBILE6 modeling has
projected that RFG will provide no
measurable benefits for NOX and less
than 2 tons per day of VOC reductions.
Recent UAM–V modeling for the Baton
Rouge area shows an ozone benefit for
RFG of around 0.26 ppb. Earlier UAM–
V sensitivity modeling showed only a 1
ppb reduction in ozone with a 30
percent reduction in local
anthropogenic VOC emissions from all
sources. Thus, for an expenditure of up
to $72 million annually, we can expect
a negligible ozone benefit. Employing
the usual cost-benefit analysis for cost
per ton of pollutant removed, we arrive
at a cost of around $36 million per daily
ton removed or around $100,000 per
annual ton removed. Since the
reduction would be expected to produce
no measurable ozone benefit anyway,
wouldn’t this qualify as an ‘‘absurd
result’’ and be subject to consideration
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for waiver as discussed in the proposed
8-hour implementation rules? (p.3–4).
Response: Baton Rouge has submitted
requests for an RFG waiver and for a
waiver of the RFG oxygen content
requirement, which are currently before
the Agency. With respect to EPA’s
authority to grant a waiver of the entire
RFG requirement for bump-up areas on
the basis of claims of ‘‘absurd results’’
allegedly caused by the oxygen content
requirement of RFG, please see EPA’s
September 30, 2004, response to
Georgia’s request for an RFG waiver,
which is available at: www.epa.gov/
otaq/regs/fuels/rfg/420s04006.pdf. As
noted above, EPA does not believe that
the transition to the more protective 8hour standard should result in less
restrictive requirements for RFG than
would apply if EPA had never revised
the 1-hour standard. The appropriate
mechanism to address Baton Rouge’s
concerns is therefore in the context of
Baton Rouge’s petitions for relief under
the RFG program, and not by
establishing different, less restrictive
RFG requirements as part of the
transition to the 8-hour standard.
Comment: Several commenters
oppose any attempts to liberalize
procedures allowing for voluntary optins to the Federal RFG program. Simply
stated, further fuels restrictions are not
an appropriate local control strategy.
There is little justification for automatic
proliferation of RFG. The industry is
currently working hard to implement
far-reaching fuels regulations that will
result in significant environmental
improvement. It does not need
additional fuel reformulation
requirements while this implementation
work is going forward.
The commenter notes under section
211(k)(6)(A) of the CAA, only areas
classified under subpart 2 of Part D of
Title I as a marginal, moderate, serious
or severe area (without regard to
whether or not the 1980 population of
the area exceeds 250,000) can opt-in to
RFG. Therefore, ‘‘Gap’’ Areas—those
attaining the 1-hour, but not the 8-hour
standard—would be subject to
implementation under subpart 1 of the
CAA. Those areas not attaining the 1hour standard and reclassified as 8-hour
nonattainment areas would be subject to
implementation procedures under
subpart 2.
Response: Section 211(k)(6)(A)
specifies which ozone nonattainment
areas may opt-in to the RFG program.
The EPA’s implementation plan for the
8-hour standard does not change or
liberalize this statutory provision or
EPA’s regulations implementing it, but
rather provides for continued
availability of opt-ins consistent with
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the statutory scheme. After revocation of
the 1-hour standard, opt-ins will be
possible for areas classified under
subpart 2 as marginal, moderate, serious
or severe ozone nonattainment areas
under the 8-hour standard. The EPA
will continue after transition to the 8hour standard to use its existing
regulations at 40 CFR 80.70(j) and 80.72
regarding procedures for opt-ins and
opt-outs.
Comment: The American Road and
Transportation Builders Association
(ARTBA) believes States should be able
to choose their own devices for
improving air quality. As a result,
ARTBA would like EPA to liberalize its
procedures for allowing a voluntary optin for the Federal RFG program. While
ARTBA understands new national fuel
standards are in the developmental
process, the transportation conformity
requirement often mandates short-term
solutions with a limited number of
options. We believe the RFG opt-in
should be one of the tools available for
States.
Response: Section 211(k)(6) of the
CAA specifies which ozone
nonattainment areas are eligible to optin to the RFG program and the
procedures (petition by governor of the
State) for opting in. Opt-in is limited to
areas classified under subpart 2 as
marginal, moderate, serious or severe
ozone nonattainment areas. The EPA
does not have the authority to
‘‘liberalize’’ these provisions in a
manner inconsistent with the statute.
See American Petroleum Institute v.
EPA, 198 F. 3d 275 (D.C. Cir. 2000)(RFG
opt-ins limited to areas classified under
subpart 2 as marginal, moderate, serious
or severe nonattainment areas).
Comment: One commenter believes
EPA’s proposed incentive feature
undercuts controls aimed at reducing
ozone precursor emissions from mobile
sources. For example, areas that are
bumped down from severe to serious
will no longer need to sell less-polluting
reformulated gas.
Response: The EPA’s final rule does
not provide for areas to be ‘‘bumped
down’’ after final designation and
thereby drop the requirement to use
RFG. On the contrary, the original nine
mandated RFG covered areas, and any
other nonattainment area bumped up to
a severe classification, will be required
to use RFG at least until redesignated to
attainment of the 8-hour ozone NAAQS.
Comment: One commenter notes that,
in the proposed rule, EPA includes the
requirement for RFG in severe areas in
its list of applicable requirements that
will remain in effect after full revocation
of the 1-hour standard (68 FR 32802
appendix B). This commenter requests
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that EPA remove the RFG requirement
from appendix B before promulgation of
the final implementation plan.
The commenter notes that within 1
year of reclassification as a ‘‘severe’’
nonattainment area under the 1-hour
standard, gasoline distributors in the 13county Metro Atlanta nonattainment
area will be required to distribute
reformulated gasoline. [42 U.S.C.
7545(k)(10)(D)]. Reformulated gasoline,
however, will not be as beneficial to the
air quality in Atlanta as other types of
fuel. After significant study, the Georgia
Environmental Protection Division
(EPD) has implemented a fuel program
tailored to the atmospheric conditions
and air quality problems in the metro
area that are primarily related to NOX
emissions and not VOC emissions.
House Hearing (July 22, 2003).
Reformulated gasoline, however, is
designed to reduce VOC emissions
rather than NOX emissions. Therefore,
EPD’s fuel program that requires the
distribution of fuel that is specifically
designed to reduce NOX will do more to
clean the air in Atlanta than RFG. If
Atlanta is ‘‘bumped up’’ to a ‘‘severe’’
nonattainment area, it will lose the
benefits of its beneficial fuel program in
place of the less effective RFG.
The commenter requests EPA to
remove RFG as an applicable
requirement that will remain in effect
after implementation of the 8-hour
standard. The requirement for RFG
under the 1-hour standard is flawed in
that it does not address the specific
ozone nonattainment issues of areas
such as Atlanta in which NOX rather
than VOCs is the pollutant of concern.
Therefore, the commenter urges EPA to
allow the revocation of the RFG
requirement associated with areas
classified as severe and higher under the
1-hour standard to allow areas that will
be classified as a lower designation
under the new, more stringent 8-hour
standard the flexibility to utilize a
gasoline formulated specifically to
address the air quality issues in those
particular areas.
Response: The final rule adopted
today specifies that areas bumped up to
a severe classification under the 1-hour
standard that are designated
nonattainment for the 8-hour standard
must continue to use RFG at least until
redesignated as attainment for the 8hour standard. The reasons for this
approach are described in the preamble
and do not change or affect any
discretion EPA may otherwise have
under the RFG provisions to modify or
remove RFG requirements. The EPA did
remove RFG from the list of applicable
requirements identified in the Phase 1
Rule, because the applicable
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requirements provision in the Phase 1
Rule addresses State controls and SIP
requirements. The final rule adopted
today treats RFG, a Federal control, in
basically the same manner as applicable
requirements are treated in the Phase 1
Rule.
With respect to the specific comments
regarding the impact of using RFG in the
Atlanta area, please see EPA’s analysis
of these issues in its September 30,
2004, response to Georgia’s request for
an RFG waiver for Atlanta.
VII. Other Considerations
A. How will EPA’s implementation of
the 8-hour ozone NAAQS affect funding
under the congestion mitigation and air
quality improvement (CMAQ) program?
1. Background
In the proposal, we noted that the
Transportation Equity Act for the 21st
Century (TEA–21) established eligibility
for the use of CMAQ program funds in
certain nonattainment and maintenance
areas, designated under section 107(d)
of the CAA (42 U.S.C. 7407(d)),
provided the area is, or was, also
classified in accordance with CAA
subpart 2, sections 181, 186, and 188.
All areas designated nonattainment after
December 31, 1997 were also eligible,
but without regard to classification.
2. Current Position
Since the proposal, new
transportation legislation was passed by
Congress and signed into law. The
amount of CMAQ funds available to
States is now set at levels authorized by
the Safe, Accountable, Flexible,
Efficient Transportation Equity Act: A
Legacy for Users (SAFETEA–LU). The
funds are still apportioned to States
through the statutory formula contained
in section 104(b) of title 23. The formula
is still based on the designations and
classifications of ozone and CO
nonattainment and maintenance areas,
and the population in such areas.
The formula for determining the
amount of funds apportioned to the
States takes into account the areas that
are designated under both subpart 1 and
subpart 2 of part D of title I, of the CAA.
How funding is affected for any specific
area is determined by the U.S. DOT in
accordance with SAFETEA–LU.
3. Comments and Responses
Comments: The EPA received several
comments expressing concern that
implementation of the 8-hour ozone
standard may negatively impact an
area’s eligibility for CMAQ Program
funds and/or the amount of CMAQ
funding the State would receive. The
comments indicated that projects and
programs to reduce air pollution in their
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area was supported through CMAQ
funding. Some stated that their area was
attaining the 8-hour ozone standard, and
thus would become ineligible for CMAQ
funding when the 1-hour ozone
standard is revoked. Others expressed
concern that any increases to the
number of nonattainment areas or
changes to classifications of
nonattainment areas could reduce the
amount of CMAQ funds available to the
area.
Response: The impact of the
implementation of the 8-hour standard
and enactment of SAFETEA–LU result
in the geographic eligibility and
apportionment of funds for the CMAQ
programs as follows:
affected county. The program is
administered by the U.S. DOT with EPA
in a consultative role. The EPA is only
taking action to implement the 8-hour
ozone standard and has no authority to
make changes to the eligibility criteria
or apportionment formula contained in
SAFETEA–LU. We understand the
importance of CMAQ funding to States
and nonattainment areas and are
prepared to work with the U.S. DOT to
minimize any unintended impact of the
8-hour ozone NAAQS on transportation
programs in those areas.
CMAQ Eligible Areas
• Designated 8-hour nonattainment
and maintenance areas.
• Former 1-hour ozone nonattainment
and maintenance areas, that are
attaining the 8-hour standard, but must
submit a section 110(a)(1) maintenance
plan in compliance with EPA’s antibacksliding provisions.
• CO, PM10 and PM¥2.5
nonattainment and maintenance areas.
Additionally, Nashville, TN;
Greensboro, NC; and Denver, CO are
Early Action Compact areas under the 8hour ozone standard that were excepted
from the revocation of the 1-hour
standard. As a result, their CMAQ
eligibility and apportionment are based
on their status as maintenance areas
under the 1-hour ozone standard.
• If the State does not have, and has
never had, a nonattainment area
designated under the CAA (42 U.S.C.
7401 et seq.), the State may use the
funds for any project in the State that
would otherwise be eligible under the
CMAQ program as if the project were
carried out in a nonattainment or
maintenance area, or is eligible under
section 133 of the surface transportation
program. This flexibility is in reference
to the CMAQ Program’s minimum
apportionment provision.
1. Background
Apportionment (ozone-based)
• Nonattainment areas designated
under subpart 1 receive a weighting
factor of 1.0
• Nonattainment areas designated
and classified under subpart 2 retain the
same apportionment weighting factors
as under TEA–21
• Maintenance areas receive a
weighting factor of 1.0.
Apportionment of CMAQ funds is
carried out yearly and varies according
to the severity of air pollution and
changes in nonattainment and
maintenance area population as
estimated by the U.S. Census for each
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B. What is the relationship between
implementation of the 8-hour standard
and the CAA’s title V permits program?
The interrelationship between
implementation of the 8-hour ozone
standard and the title V permits
program was not discussed in the
proposed rule. However, various
questions have been raised about the
interface between the implementation of
the 8-hour ozone standard and the title
V operating permits program. The
following questions and answers
address these questions.
Question 1: How is title V
applicability affected by the new 8-hour
ozone standard and the revocation of
the 1-hour ozone standard? 115
Response: Section 502(a) of the CAA
and 40 CFR 70.3 and 71.3 establish
specific criteria for determining whether
a source is subject to the title V
operating permits program. A source
that meets one or more of these criteria
is subject to title V: title IV affected
sources, major sources, sources subject
to standards or regulations under
115 The 1-hour standard was revoked for most
areas, including the associated area designations
and classifications, on June 15, 2005, 1 year
following June 15, 2004, the effective date of
designations for the 8-hour standard. The 1-hour
standard was revoked for most areas, including the
associated area designations and classifications, on
June 15, 2005, 1 year following June 15, 2004, the
effective date of designations for the 8-hour
standard. However, for early action compact areas
that were not designated attainment for the 8-hour
standard, the effective date of 8-hour designations
and classifications was deferred, and the 1-hour
standard remains applicable and will not be
revoked until 1 year after the effective date of the
8-hour designations for these areas. As a result,
although this section of the preamble continually
refers to the June 15, 2004, and June 15, 2005, dates,
the title V major source thresholds are currently
determined only by the 1-hour standard in areas
where the 8-hour designations and classifications
are not effective and the 1-hour standard has not
been revoked. The scenarios described in this
preamble section will not begin to be applicable to
these areas until the effective date of the 8-hour
designations in these areas.
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section 111 or 112,116 sources required
to have a permit under part C or D of
title I, or any other stationary source in
a category designated by the
Administrator. Although a source is
required to obtain a title V permit if it
meets one or more of these criteria, only
sources which are brought into title V as
a result of their major source status and/
or the requirement to obtain a part C or
D permit may be directly affected by the
transition from the 1-hour ozone
standard to the 8-hour ozone standard.
For example, a source subject to title
V solely because it was major for VOCs
under a 1-hour ozone classification is no
longer subject to title V after the
revocation of the 1-hour ozone standard
(on June 15, 2005) if its actual and
potential emissions of VOCs under an 8hour ozone designation or classification
are minor. However, if the same source
was also subject to title V for other
reasons, the source would remain
subject to title V. See question 4 for
further information. In addition, the
source’s title V applicability could also
be affected by future changes, such as
becoming subject to PSD or major
nonattainment NSR.
Question 2: When do the 8-hour major
source thresholds apply for determining
major source status under title V?
Response: For purposes of title V,
section 501(2) of the CAA defines
‘‘major source’’ in part as ‘‘a major
stationary source as defined in section
302 or part D of title I.’’ The part 70 and
part 71 regulations incorporate this
definition and the part D major source
thresholds. ‘‘Major source’’ for ozone
nonattainment areas include sources
which emit or which have the potential
to emit 100 tpy or more of VOCs or
oxides of nitrogen in areas classified as
‘‘marginal’’ or ‘‘moderate,’’ 50 tpy or
more of these ozone precursors in areas
classified as ‘‘serious,’’ 25 tpy or more
of these ozone precursors in areas
classified as ‘‘severe,’’ and 10 tpy or
more of these ozone precursors in areas
classified as ‘‘extreme.’’
On or after June 15, 2004, until June
15, 2005, the major source thresholds
for the 1-hour ozone designations and
classifications and the 8-hour ozone
designations and classifications were in
effect under part D of title I, and
therefore under title V as well. Since
revocation of the 1-hour ozone standard
and the corresponding area designations
and classifications on June 15, 2005,
only the major source thresholds for the
8-hour ozone designations and
classifications continue to determine
116 40 CFR 70.3(b) and 71.3(b) provide for certain
area source deferrals and exemptions, which are not
detailed here.
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whether a source is major for ozone
precursors under title V. Our review of
the 1-hour and 8-hour designations and
nonattainment classifications indicates
that no additional sources became
subject to title V on June 15, 2004 (the
effective date of the 8-hour ozone
NAAQS designations and classifications
(40 CFR part 81, subpart C)) based solely
on the 8-hour designations and
classifications and corresponding major
source thresholds. This is because the 8hour designations and classifications
effective on June 15, 2004 did not result
in a lowering of the title V major source
threshold for any area compared to the
1-hour designations and classifications.
Rather, the title V major source
thresholds either stayed the same or
were raised to a higher threshold in all
cases, e.g., 50 tpy to 100 tpy.
Question 3: Are title V permits
required for sources that trigger the
major source applicability cut-offs for
RACT in 40 CFR 51.900(f)(3) due to the
8-hour ozone anti-backsliding
provisions in 40 CFR part 51, subpart X?
Example: An area is classified as
extreme under the 1-hour ozone
standard. In an extreme area, the major
source threshold for ozone precursors is
10 tpy. Under the 8-hour standard in
this example, this same area is classified
as a severe-17 area. In a severe-17 area,
the major source threshold for ozone
precursors is 25 tpy. Under the antibacksliding provisions, this area would
be required to continue its application
of RACT to sources with potential
emissions of 10 or more tpy of ozone
precursors. However, is the title V major
source threshold for ozone precursors in
this area 10 tpy or 25 tpy since June 15,
2005?
Response: Since revocation of the 1hour ozone standard on June 15, 2005,
the title V major source thresholds for
ozone are now based solely on the 8hour designations and classifications
and thus in the above example will be
25 tpy for ozone precursors. As
discussed in Question 1 above, section
502(a) and 40 CFR §§ 70.3 and 71.3
include criteria for determining title V
applicability. These criteria do not
specifically include sources subject to
RACT, but do include major sources. As
discussed in Question 2 above, section
501(2) defines a title V ‘‘major source’’
in part as ‘‘a major stationary source as
defined in section 302 or part D of title
I’’ and 40 CFR 70.2 and 71.2 incorporate
this definition.
In terms of the language in 40 CFR
51.900(f)(3) regarding ‘‘major source
applicability cut-offs for purposes of
RACT,’’ this provision does not apply
for purposes of defining a ‘‘major
source’’ under title V (nor could it, since
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major source is statutorily defined and
cannot be revised by regulation). Rather,
the cut-offs referenced in this antibacksliding provision apply in
determining which 1-hour
nonattainment requirements are
‘‘applicable requirements’’ for an area—
requirements which will be continued
in implementing the 8-hour standard.
Additionally, 40 CFR 51.900 specifies
that the definition of ‘‘applicable
requirements’’ and other definitions in
this section only ‘‘apply for purposes of
this subpart [subpart X].’’ Thus, in short,
the major source applicability cut-offs
for purposes of RACT referenced in 40
CFR 51.900(f)(3) are not relevant in
determining whether a source is a major
source under title V.
Question 4: In many nonattainment
areas, the major stationary source
threshold under the 8-hour ozone
standard is currently higher than the
major stationary source threshold for the
same area under the 1-hour ozone
standard.
Example: Under the 1-hour ozone
standard, an area is classified as serious
with a 50 tpy major stationary source
threshold for ozone precursors. Under
the 8-hour standard, this same area is
classified as moderate with a 100 tpy
major stationary source threshold for
ozone precursors. If a source in this area
has a potential to emit VOCs at 75 tpy,
but also has a part D permit obtained
under the 1-hour standard, is this source
subject to title V since revocation of the
1-hour ozone standard on June 15,
2005? 117
Response: Yes. Under the 1-hour
standard, this source was subject to title
V both because it was a major source
and also because it was required to have
a part D permit. Under the 8-hour
standard, this source remains subject to
title V because it was required to have
a part D permit under the 1-hour
standard even though it is no longer
subject to title V due to its major source
status.
Sources that are, at any time, required
to have a permit under part C or D of
title I must obtain a title V permit. This
interpretation is consistent with the
CAA and EPA’s implementation policy
history. See the Vastar letter discussed
below. Section 502(a) states in part that
‘‘any other source required to have a
permit under part C or D of title I’’ is
required to have a title V permit. We
interpret the phrase ‘‘required to have a
permit under part C or D of title I’’ to
include any source required to obtain a
117 A source with a part D permit obtained under
the 1-hour standard must retain its part D permit
under the 8-hour standard even though it is now in
an area with a higher major stationary source
threshold.
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permit under part C or D of title I
regardless of whether the permit was
actually obtained by the source. This
interpretation is consistent with the
legislative history which indicates
Congress intended that sources ‘‘subject
to * * * requirements’’ from PSD and
NSR be required to have a title V permit.
H.R. Rep. No. 101–490, 101st Congress,
2nd Session, at 344 (May 17, 1990); see
also S. Rep. 101–228, 101st Congress,
1st Session, at 349 (December 20, 1989).
Note that the exemption in 40 CFR
70.3(b)(1) and 71.3(b)(1) for nonmajor
sources does not apply to sources
required to have a part C or D permit.
As EPA has previously stated: ‘‘* * *
section 70.3(b)(1) cannot be
appropriately interpreted as allowing
title V permitting authorities to exempt
nonmajor part C or D sources from title
V, especially in light of the explicit
requirement in sections 71.5(a)(1)(ii)
and 70.5(a)(1)(ii) that these sources
obtain title V permits.’’ See letter from
R. Long, EPA Region 8, to M. Tarrillion,
Vastar Resources, Inc., September 10,
1999. See also 66 FR 59161, 59163;
November 27, 2001 (‘‘A source required
to have a part C or D permit but
considered nonmajor for part 70 would
be subject to part 70 * * *’’)
Title V permit content may be affected
for sources in the above-noted situation
because, pursuant to 40 CFR 70.3(c)(2)
and 71.3(c)(2), for any nonmajor source
subject to title V, the permit is required
at a minimum to include the applicable
requirements for the emissions units
that cause the source to be subject to the
part 70 or part 71 programs. If an
emissions unit at the nonmajor source
did not trigger the requirement to apply
for a title V permit, then none of that
unit’s applicable requirements are
required to be included in the source’s
title V permit. See 66 FR 59163 and
footnote 2. However, nothing in 40 CFR
70.3(c)(2) or 71.3(c)(2) precludes States
from including Federal applicable
requirements for other emissions units
at a nonmajor source in the source’s title
V permit if States require it.
2. Summary of Final Rule
There has been no change in the final
rule as a result of the above
clarifications regarding the interface
between the 8-hour ozone standard and
the title V operating permits program.
3. Comments and Responses
Comment: One commenter stated
support of the anti-backsliding
regulations to maintain the
requirements established under the 1hour standard nonattainment area
classifications when 8-hour
classification requirements would be
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less stringent. However, the commenter
requested that EPA consider using the
major source thresholds as defined by
the 8-hour standard classifications for
title V permitting purposes. The
commenter further suggested that EPA
evaluate whether a lower title V major
source threshold provides sufficient
protections to justify the added costs
involved, especially in areas such as
that of the commenter’s where 75
percent of the reactive organic gases
(ROG) and NOX emissions are from
mobile sources, which are not subject to
control under title V.
Response: We agree that, since
revocation of the 1-hour ozone standard,
the title V major stationary source
thresholds are only determined by the 8hour designations and classifications.
Additionally, as stated in response to
question 3 in the above questions and
answers, the language in 40 CFR
51.900(f)(3) regarding ‘‘major source
applicability cut-offs for purposes of
RACT’’ does not apply for purposes of
defining a ‘‘major source’’ under title V
(nor could it, since major source is
statutorily defined and cannot be
revised by regulation). Rather, the cutoffs referenced in this anti-backsliding
provision apply in determining which
1-hour nonattainment requirements are
‘‘applicable requirements’’ for an area—
requirements which will be continued
in implementing the 8-hour standard.
Additionally, 40 CFR 51.900 specifies
that the definition of ‘‘applicable
requirements’’ and other definitions in
this section only ‘‘apply for purposes of
this subpart [subpart X].’’ Thus, in short,
the major source applicability cut-offs
for purposes of RACT referenced in 40
CFR 51.900(f)(3) are not relevant in
determining whether a source is a major
source under title V.
C. What Action Is EPA Taking on the
Overwhelming Transport Classification
for Subpart 1 Areas?
The Phase 1 Rule created an
overwhelming transport classification
that would be available to subpart 1
areas that demonstrate they are affected
by overwhelming transport of ozone and
its precursors and demonstrate they
meet the definition of a rural transport
area in section 182(h) of the CAA [40
CFR 51.904(a)]. We received a petition
for reconsideration of the overwhelming
transport classification from
Earthjustice,118 who claimed that our
final rule of April 30, 2004, relied on
118 Filed June 29, 2004 by Earthjustice on behalf
of American Lung Association, Environmental
Defense, Natural Resources Defense Council, Sierra
Club, Clean Air Task Force, Conservation Law
Foundation, and Southern Alliance for Clean
Energy.
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guidance that was not publicly available
during the comment period and was
still unavailable at the time of final
rulemaking. In addition, we noted in the
Phase 1 Rule that we were considering
the comments we received on the issue
of applicable requirements for these
subpart 1 areas and that we would
address this issue after we issue
guidance on how areas should assess
whether they are subject to
overwhelming transport. We granted the
Earthjustice petition concerning the
overwhelming transport classification
on January 10, 2005. In a separate
rulemaking action, we are inviting
comment on the overwhelming
transport classification, the draft
overwhelming transport guidance, and
the requirements that would apply to
such areas.
We will address any comments on the
applicable control requirements for an
area that receives an overwhelming
transport classification in the context of
the reconsideration action.
VIII. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), the Agency
must determine whether the regulatory
action is ‘‘significant’’ and, therefore,
subject to the Office of Management and
Budget (OMB) review and the
requirements of the Executive Order.
The Order defines ‘‘significant
regulatory action’’ as one that is likely
to result in a rule that may:
(1) Have an annual effect on the
economy of $100 million or more or
adversely affect in a material way the
economy, a sector of the economy,
productivity, competition, jobs, the
environment, public health or safety, or
State, local, or Tribal governments or
communities;
(2) Create a serious inconsistency or
otherwise interfere with an action taken
or planned by another agency;
(3) Materially alter the budgetary
impact of entitlements, grants, user fees,
or loan programs or the rights and
obligations of recipients thereof; or
(4) Raise novel legal or policy issues
arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
Pursuant to the terms of Executive
Order 12866, it has been determined
that this rule is a ‘‘significant regulatory
action’’ because it raises novel legal or
policy issues arising out of legal
mandates. As such, this action was
submitted to OMB for review. Changes
made in response to OMB suggestions or
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recommendations are documented in
the public record.
B. Paperwork Reduction Act
The information collection
requirements in this rule will be
submitted for approval to OMB under
the Paperwork Reduction Act, 44 U.S.C.
3501 et seq. The information collection
requirements are not enforceable until
OMB approves them other than to the
extent required by statute.
This rule provides the framework for
the States to develop SIPs to achieve a
new or revised NAAQS. This framework
reflects the requirements prescribed in
CAA sections 110 and part D, subparts
1 and 2 of title I. In that sense, the
present final rule does not establish any
new information collection burden on
States. Had this rule not been
developed, States would still have the
legal obligation under law to submit
nonattainment area SIPs under part D of
title I of the CAA within specified
periods after their nonattainment
designation for the 8-hour ozone
standard, and the SIPs would have to
meet the requirements of part D.
A SIP contains rules and other
requirements designed to achieve the
NAAQS by the deadlines established
under the CAA, and also contains a
demonstration that the State’s
requirements will in fact result in
attainment. The SIP must meet the CAA
requirements in subparts 1 or 2 to adopt
RACM, RACT, and provide for RFP
toward attainment for the period prior
to the area’s attainment date. After a
State submits a SIP, the CAA requires
EPA to approve or disapprove the SIP.
If EPA approves the SIP, the rules in the
SIP become federally enforceable. If
EPA disapproves the SIP (or if EPA
finds that a State fails to submit a SIP),
the CAA requires EPA to impose
sanctions (2:1 offsets for major new or
modified sources and restrictions on
Federal highway funding) within
specified timeframes; additionally, EPA
must prepare and publish a FIP within
2 years after a disapproval or finding of
failure to submit. The SIP must be
publicly available. States must maintain
confidentiality of confidential business
information, however, if used to support
SIP analyses. The SIP is a one-time
submission, although the CAA requires
States to revise their SIPs if EPA
requests a revision upon a finding that
the SIP is inadequate to attain or
maintain the NAAQS. The State may
revise its SIP voluntarily as needed, but
in doing so must demonstrate that any
revision will not interfere with
attainment or RFP or any other
applicable requirement under the CAA
(see section 110(l)).
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This rule does not establish
requirements that directly affect the
general public and the public and
private sectors, but, rather, interprets
the statutory requirements that apply to
States in preparing their SIPs. The SIPs
themselves will likely establish
requirements that directly affect the
general public, and the public and
private sectors.
The EPA has not yet projected cost
and hour burden for the statutory SIP
development obligation but has started
that effort and will shortly prepare an
Information Collection Request (ICR)
request. However, EPA did estimate
administrative costs at the time of
promulgation of the 8-hour ozone
standard in 1997. See Chapter 10 of U.S.
EPA 1997, Regulatory Impact Analyses
for the Particulate Matter and Ozone
National Ambient Air Quality
Standards, Innovative Strategies and
Economics Group, Office of Air Quality
Planning and Standards, Research
Triangle Park, N.C., July 16, 1997.
Assessments of some of the
administrative cost categories identified
as a part of the SIP for an 8-hour
standard are already conducted as a
result of other provisions of the CAA
and associated ICRs (e.g. emission
inventory preparation, air quality
monitoring program, conformity
assessments, NSR, I/M program).
The burden estimates in the ICR for
this rule are incremental to what is
required under other provisions of the
CAA and what would be required under
a 1-hour standard. Burden means the
total time, effort, or financial resources
expended by persons to generate,
maintain, retain, or disclose or provide
information to or for a Federal agency.
This includes the time needed to review
instructions; develop, acquire, install,
and utilize technology and systems for
the purposes of collecting, validating,
and verifying information, processing
and maintaining information, and
disclosing and providing information;
adjust the existing ways to comply with
any previously applicable instructions
and requirements; train personnel to be
able to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR part 9. When
this ICR is approved by OMB, the
Agency will publish a technical
amendment to 40 CFR part 9 in the
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Federal Register to display the OMB
control number for the approved
information collection requirements
contained in this final rule. However,
the failure to have an approved ICR for
this rule does not affect the statutory
obligation for the States to submit SIPs
as required under part D of the CAA.
The information collection
requirements associated with NSR
permitting for ozone are covered by
EPA’s request to renew the approval of
the ICR for the NSR program, ICR
1230.17, which was approved by OMB
on January 25, 2005. The information
collection requirements associated with
NSR permitting were previously
covered by ICR 1230.10 and 1230.11.
The OMB previously approved the
information collection requirements
contained in the existing NSR
regulations at 40 CFR parts 51 and 52
under the provisions of the Paperwork
Reduction Act, and assigned OMB
control number 2060–0003. A copy of
the approved ICR may be obtained from
Susan Auby, Collection Strategies
Division; U.S. Environmental Protection
Agency (2822T); 1200 Pennsylvania
Ave., NW., Washington, DC 20460 or by
calling (202) 566–1672.
For the portion of this rulemaking on
RFG, this action does not add any new
requirements under the provisions of
the Paperwork Reduction Act. The OMB
has approved the information collection
requirements contained in the final
RFG/anti-dumping rulemaking (see 59
FR 7716, February 16, 1994) and has
assigned OMB control number 2060–
0277 (EPA ICR No. 1951.08).
C. Regulatory Flexibility Act
The EPA has determined that it is not
necessary to prepare a regulatory
flexibility analysis in connection with
this final rule.
For purposes of assessing the impacts
of today’s rule on small entities, small
entity is defined as: (1) A small business
as defined by the Small Business
Administrations’ regulations at 13 CFR
121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of today’s final Phase 2 Rule for
implementation of the 8-hour ozone
standard on small entities, EPA has
concluded that this action will not have
a significant economic impact on a
substantial number of small entities.
This final rule will not impose any new
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or additional requirements on small
entities.
Concerning the NSR portion of this
rule, a Regulatory Flexibility Act
Screening Analysis (RFASA) was
developed as part of a 1994 draft
Regulatory Impact Analysis (RIA) and
incorporated into the September 1995
ICR renewal. This analysis showed that
the changes to the NSR program due to
the 1990 CAA Amendments would not
have an adverse impact on small
entities. This analysis encompassed the
entire universe of applicable major
sources that were likely to also be small
businesses (approximately 50 ‘‘small
business’’ major sources). Because the
administrative burden of the NSR
program is the primary source of the
NSR program’s regulatory costs, the
analysis estimated a negligible ‘‘cost to
sales’’ (regulatory cost divided by the
business category mean revenue) ratio
for this source group. The incorporation
of the major source thresholds and offset
ratios from the 1990 CAA Amendments
in § 51.165 and appendix S for the
purpose of implementing NSR for the 8hour standard does not change this
conclusion. Under section 110(a)(2)(C),
all States must implement a
preconstruction permitting program ‘‘as
necessary to assure that the [NAAQS]
are achieved,’’ regardless of changes to
today’s regulations. Thus, small
businesses continue to be subject to
regulations for construction and
modification of stationary sources,
whether under State and local agency
minor NSR programs, SIPs to implement
§ 51.165, or appendix S, to ensure that
the 8-hour standard is achieved.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and Tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures to State, local,
and Tribal governments, in the
aggregate, or to the private sector, of
$100 million or more in any 1 year.
Before promulgating an EPA rule for
which a written statement is needed,
section 205 of the UMRA generally
requires EPA to identify and consider a
reasonable number of regulatory
alternatives and adopt the least costly,
most cost-effective or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
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inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
costly, most cost-effective or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including Tribal
governments, it must have developed
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enabling
officials of affected small governments
to have meaningful and timely input in
the development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
The RFG-related portions of this rule
contain no new Federal mandates
(under the regulatory provisions of title
II of the UMRA) for State, local or Tribal
governments or the private sector. The
rule imposes no new enforceable duty,
since it merely clarifies that in the
transition to the 8-hour ozone standard
the pre-existing opt-in rules remain in
place, as does the pre-existing
requirement that RFG be used in
mandatory RFG-covered areas within
the scope of this rule until such areas
are redesignated to attainment for the
ozone standard. Although EPA does not
believe that UMRA imposes
requirements regarding the RFG-related
portions of this rulemaking, EPA notes
that the environmental and economic
impacts of the RFG program were
assessed in EPA’s RIA for the 1994 RFG
rules.
The EPA has determined that all other
portions of this rule do 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. The estimated
administrative burden hour and costs
associated with implementing the 8hour, 0.08 ppm NAAQS were developed
upon promulgation of the NAAQS and
presented in Chapter 10 of U.S. EPA
1997, Regulatory Impact Analyses for
the Particulate Matter and Ozone
National Ambient Air Quality
Standards, Innovative Strategies and
Economics Group, Office of Air Quality
Planning and Standards, Research
Triangle Park, NC, July 16, 1997. The
estimated costs presented there for
States in 1990 dollars totaled $0.9
million. The corresponding estimate in
1997 dollars is $1.1 million. Thus,
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today’s rule is not subject to the
requirements of sections 202 and 205 of
the UMRA. At the time EPA proposed
its Implementation Rule, EPA noted that
if it chose a classification option that
classified all areas under subpart 2 of
part D, these costs may increase
modestly, but would not reach $100
million. However, in promulgating the
Phase 1 Rule, EPA adopted a
classification scheme that resulted in
approximately half of the areas
designated nonattainment being subject
only to the subpart 1 requirements.
The CAA imposes the obligation for
States to submit SIPs to implement the
8-hour ozone NAAQS; in this rule, EPA
is merely fleshing out those
requirements. However, even if this rule
did establish a requirement for States to
submit SIPs, it is questionable whether
a requirement to submit a SIP revision
would constitute a Federal mandate in
any case. The obligation for a State to
submit a SIP that arises out of section
110 and part D of the CAA is not legally
enforceable by a court of law, and at
most is a condition for continued
receipt of highway funds. Therefore, it
is possible to view an action requiring
such a submittal as not creating any
enforceable duty within the meaning of
section 421(5)(9a)(I) of UMRA [2 U.S.C.
658(a)(I)]. Even if it did, the duty could
be viewed as falling within the
exception for a condition of Federal
assistance under section 421(5)(a)(i)(I) of
UMRA [2 U.S.C. 658(5)(a)(i)(I)]. As
noted below under ‘‘L. Petitions for
Judicial Review,’’ this rule is covered
under section 307(d) of the CAA.
The EPA has determined that this rule
contains no regulatory requirements that
may significantly or uniquely affect
small governments, including Tribal
governments. Nonetheless, EPA carried
out consultations with governmental
entities affected by this rule.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that 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.’’
This rule does not have federalism
implications. It will not have substantial
direct effects on the States, on the
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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. The RFG-related
portions of the rule impose
requirements on certain refiners and
other entities in the gasoline
distribution system, and not on States.
In addition, as described in section D,
above (on UMRA), EPA previously
determined the costs to States to
implement the 8-hour ozone NAAQS to
be approximately $1 million. The CAA
establishes the scheme whereby States
take the lead in developing plans to
meet the NAAQS. This rule would not
modify the relationship of the States
and EPA for purposes of developing
programs to implement the NAAQS. In
the non-RFG portions of this rule, EPA
is interpreting the statutory SIP
submission requirements that apply to
areas designated. As described above,
EPA has generally adopted the more
flexible options proposed in the June
2003 proposal. Thus, Executive Order
13132 does not apply to this rule.
Although section 6 of Executive Order
13132 does not apply to this rule, EPA
actively engaged the States in the
development of this rule. The EPA held
regular calls with representatives of
State and local air pollution control
agencies. Also, EPA held three public
meetings at which it described the
approaches it was considering and
provided an opportunity for States and
various other governmental officials to
comment on the options being
considered. Finally, EPA held three
public hearings after the proposed rule
was published to obtain public
comments.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’
The portions of this rulemaking that
relate to RFG do not create a mandate
for any Tribal government. The rule
does not impose any enforceable duties
on these entities. Rather, the rule will
affect only those refiners, importers or
blenders of gasoline that choose to
produce or import RFG for sale in the
nonattainment areas addressed in the
rule, and the gasoline distributors and
retail stations in those areas. The
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following discussion relates to the nonRFG portions of the rule.
This rule concerns the
implementation of the 8-hour ozone
NAAQS in areas designated
nonattainment for that NAAQS. The
CAA provides for States and Tribes to
develop plans to regulate emissions of
air pollutants within their jurisdictions.
The non-RFG portions of this rule flesh
out the statutory obligations of States
and Tribes that develop plans to
implement the 8-hour ozone NAAQS.
The TAR and the CAA give Tribes the
opportunity to develop and implement
CAA programs such as the 8-hour ozone
NAAQS, but it leaves to the discretion
of the Tribe whether to develop these
programs and which programs, or
appropriate elements of a program, they
will adopt.
This rule does not have Tribal
implications as defined by Executive
Order 13175. There are 126 designated
nonattainment areas. Although there are
61 Tribes estimated to be in one or more
of those nonattainment areas, this rule
does not have a substantial direct effect
on one or more Indian Tribes, since no
Tribe is required to implement a CAA
program to attain the 8-hour ozone
NAAQS. See: https://www.epa.gov/oar/
oaqps/glo/designations/tribaldesig.htm
for the list of Tribes included as part of
a designated nonattainment area.
Furthermore, this rule does not affect
the relationship or distribution of power
and responsibilities between the Federal
government and Indian Tribes. The
CAA and the TAR establish the
relationship of the Federal government
and Tribes in developing plans to attain
the NAAQS, and this rule does nothing
to modify that relationship. Because this
rule does not have Tribal implications,
Executive Order 13175 does not apply.
Although Executive Order 13175 does
not apply to this rule, EPA did consult
with Tribal leaders and environmental
staff in developing this rule and
encouraged Tribal input at an early
stage. The EPA supports the national
‘‘Tribal Designations and
Implementation Work Group’’ which
provided an open forum for all Tribes to
voice concerns to EPA about the
designation and implementation process
for the 8-hour ozone NAAQS. These
discussions have given EPA valuable
information about Tribal concerns
regarding implementation of the 8-hour
ozone NAAQS. The work group sent
issue summaries and suggestions for
addressing them to the newly formed
National Tribal Air Association (NTAA),
which in turn sent them to Tribal
leaders. The project lead for this rule
informed interested Tribal leaders about
progress on the rule and invited input.
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The EPA encouraged Tribes to
participate in the national public
meetings held to take comment on early
approaches to the rule. Several Tribes
made public comments at the April
2002 public meeting in Tempe, Arizona.
Furthermore, EPA sent individualized
letters to all federally-recognized Tribes
inviting Tribal leaders to consult with
EPA on the proposed implementation
rule. The EPA received comment from
the NTAA on several questions: (1) the
NTAA asked for clarification on the
nature of EPA’s support for Tribes
without TAS status and asked if EPA
would provide technical assistance in
interpreting SIP documentation to a
Tribe without TAS approval; (2) the
NTAA asked EPA to explain how it
envisions its role in continuing
consultation with Tribes throughout the
execution of SIPs. We respond to these
comments in the technical support
document. The NTAA’s final comment
cited concerns with the impact of NSR
requirements on the Tribes. The EPA
acknowledges that offsets are a concern
for Tribes. We are currently evaluating
potential options for addressing this
concern.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
Executive Order 13045: ‘‘Protection of
Children From Environmental Health
and Safety Risks’’ (62 FR 19885, April
23, 1997) applies to any rule that (1) Is
determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
the Agency must evaluate the
environmental health or safety effects of
the planned rule on children, and
explain why the planned regulation is
preferable to other potentially effective
and reasonably feasible alternatives
considered by the Agency.
This rule is not subject to Executive
Order 13045 because it implements a
previously promulgated health-based
Federal standard—the 8-hour ozone
NAAQS—and contains a non- healthbased determination of the extent to
which the existing RFG program
remains in place under the 8-hour
standard. We have evaluated the
environmental health and safety effects
of the 8-hour ozone NAAQS on children
as part of this previously promulgated
Federal standard. The results of this
evaluation are contained in 40 CFR part
50, National Ambient Air Quality
Standards for Ozone, Final Rule (62 FR
38855–38896, July 18, 1997;
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specifically, 62 FR 38855, 62 FR 38860
and 62 FR 38865).
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions 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.
At the time of proposal, information
on the methodology and data regarding
the assessment of potential energy
impacts regarding implementation of
the 8-hour standard was addressed in
Chapter 6 of U.S. EPA 2003, Cost,
Emission Reduction, Energy, and
Economic Impact Assessment of the
Proposed Rule Establishing the
Implementation Framework for the 8Hour, 0.08 ppm Ozone National
Ambient Air Quality Standard, prepared
by the Innovative Strategies and
Economics Group, Office of Air Quality
Planning and Standards, Research
Triangle Park, NC, April 24, 2003.
Subsequently, EPA issued an
Addendum 1 to that analysis for the
Phase 1 final rule and designated
nonattainment areas. For purposes of
this final rule, EPA has issued
Addendum 2. By adopting the more
flexible approaches while providing for
attainment and maintenance of the 8hour NAAQS as required by the CAA,
additional energy cost associated with
more extensive use of less flexible
approaches would be averted. The
portions of this rule that relate to RFG
merely clarify that the existing program
continues under the 8-hour standard in
the areas addressed by the rule, so the
rule does not have a significant affect on
energy supply, distribution or use. The
EPA evaluated energy impacts of the
RFG program in the RIA for the 1994
rulemaking establishing the RFG
program.
I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer Advancement Act
of 1995 (NTTAA), Public Law No. 104–
113, section 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards (VCS) 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 VCS bodies. The NTTAA
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directs EPA to provide Congress,
through OMB, explanations when the
Agency decides not to use available and
applicable VCS.
This rulemaking does not involve
technical standards. Therefore, EPA is
not considering the use of any VCS.
The EPA will encourage the States
and Tribes to consider the use of such
standards, where appropriate, in the
development of the implementation
plans.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 requires that
each Federal agency make achieving
environmental justice part of its mission
by identifying and addressing, as
appropriate, disproportionately high
and adverse human health or
environmental effects of its programs,
policies, and activities on minorities
and low-income populations.
The EPA believes that this rule does
not raise any environmental justice
concerns. Today’s rule helps establish a
framework for bringing all areas of the
country into attainment with the 8-hour
ozone standards, an important
environmental justice goal. The health
and environmental risks associated with
ozone were considered in the
establishment of the 8-hour, 0.08 ppm
ozone NAAQS, and the standard was set
at a level requisite to protect public
health with an adequate margin of
safety. In setting this standard, EPA
considered the effects on sensitive
subpopulations, such as those with
respiratory problems.
The EPA has designated as
nonattainment these areas of the
country that are not meeting the 8-hour
ozone standard. This rule will assist
States as they develop plans to bring
these nonattainment areas into
attainment in accordance with the CAA
schedule. By establishing guidelines for
bringing these areas into attainment
with the 8-hour ozone standard, the
Phase 2 Rule advances an important
environmental justice goal and will help
make significant progress in providing
for the fair treatment of all people with
respect to air pollution.
In the preamble to the proposed rule,
EPA took comment on the Clean Air
Development Communities (CADC)
concept (regarding possible State
adoption of land use planning as a
pollution reduction strategy) and noted
that it might raise environmental justice
concerns. Public comments were
submitted that raised environmental
justice concerns with this concept. As
noted earlier in the preamble to this
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71695
Phase 2 Rule, EPA is not finalizing the
CADC concept and has therefore not
responded to these (or any other)
comments on the CADC concept.
The RFG program is designed to
reduce vehicle emissions of toxic and
ozone-forming substances. This rule
will not alter the air quality benefits
associated with the RFG program.
K. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. The EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the rule in the Federal
Register. A major rule cannot take effect
until 60 days after it is published in the
Federal Register. This action is not a
‘‘major rule’’ as defined by 5 U.S.C.
804(2). This rule will be effective
January 30, 2006.
L. Petitions for Judicial Review
Under section 307(b)(1) of the CAA,
petitions for judicial review of this
action must be filed in the United States
Court of Appeals for the District of
Columbia Circuit by January 30, 2006.
Filing a petition for reconsideration by
the Administrator of this final rule does
not affect the finality of this rule for the
purposes of judicial review nor does it
extend the time within which a petition
for judicial review may be filed, and
shall not postpone the effectiveness of
such rule or action. This action may not
be challenged later in proceedings to
enforce its requirements. See CAA
section 307(b)(2).
M. 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.’’
While the Administrator did not make
this determination earlier, the
Administrator believes that all of the
procedural requirements, e.g.,
docketing, hearing and comment
periods, of section 307(d) have been
complied with during the course of this
rulemaking.
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Appendix A to Preamble—Methods to
Account for Non-Creditable Reductions
When Calculating ROP Targets for the
2008 and Later ROP Milestone Years
The following methods properly
account for the non-creditable emissions
reductions when calculating ROP targets
for the 2008 and later ROP milestone
years.119 They are consistent with
requirements of sections 182(b)(1)(C)
and (D) and 182(c)(2)(B) of the CAA.
(1) Method 1: For areas that must
meet a 15 percent VOC reduction
requirement by 2008:
(A) Estimate the actual anthropogenic
base year VOC inventory in 2002 with
all 2002 control programs in place for
all sources.
(B) Using the same highway vehicle
activity inputs used to calculate the
actual 2002 inventory, run the
appropriate motor vehicle emissions
model for 2002 and for 2008 with all
post-1990 CAA measures turned off.
Any other local inputs for vehicle
inspection and maintenance (I/M)
programs should be set according to the
program that was required to be in place
in 1990. Fuel Reid Vapor Pressure (RVP)
should be set at 9.0 or 7.8 depending on
the RVP required in the local area as a
result of fuel RVP regulations
promulgated in June, 1990.
(C) Calculate the difference between
the 2002 and 2008 VOC emission factors
calculated in Step B and multiply by
2002 vehicle miles traveled (VMT). The
result is the VOC emissions reductions
that will occur between 2002 and 2008
without the benefits of any post-1990
CAA measures. These are the noncreditable reductions that occur over
this period.
(D) Subtract the non-creditable
reductions calculated in Step C from the
actual anthropogenic 2002 inventory
estimated in Step A. This adjusted VOC
inventory is the basis for calculating the
target level of emissions in 2008.
(E) Reduce the adjusted VOC
inventory calculated in Step D by 15
percent. The result is the target level of
119 These methods assume the use of EPA’s onroad motor vehicle emissions model in all States
other than California. All of the methods given here
require the user to turn off all post-1990 CAA
measures as part of the calculation. In EPA’s current
motor vehicle emissions model, MOBILE6.2, this is
accomplished using the NO CLEAN AIR ACT
command as described in the MOBILE6.2 User’s
Guide (found at https://www.epa.gov/otaq/m6.htm).
Users of future versions of EPA’s motor vehicle
emissions model should consult the appropriate
User’s Guide for the version of the model they are
using for instructions on what model command to
use. For California nonattainment areas, the current
motor vehicle emissions model is EMFAC2002.
Users modeling California nonattainment areas
should consult with the EPA Regional Office for
information on doing equivalent calculations in that
model and in future versions.
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VOC emissions in 2008 in order to meet
the 2008 ROP requirement. The actual
projected 2008 inventory for all sources
with all control measures in place and
including projected 2008 growth in
activity must be at or lower than this
target level of emissions.
(2) Method 2: For areas covered under
40 CFR 51.910(a)(1)(ii)(C) and that meet
an 18 percent VOC emission reduction
requirement by 2008 with NOX
substitution allowed, following EPA’s
NOX Substitution Guidance:
(A) Estimate the actual anthropogenic
base year inventory for both VOC and
NOX in 2002 with all 2002 control
programs in place.
(B) Using the same highway vehicle
activity inputs used to calculate the
actual 2002 inventory, run the
appropriate motor vehicle emissions
model for 2002 and for 2008 with all
post-1990 CAA measures turned off.
Any other local inputs for I/M programs
should be set according to the program
that was required to be in place in 1990.
Fuel RVP should be set at 9.0 or 7.8
depending on the RVP required in the
local area as a result of fuel RVP
regulations promulgated in June, 1990.
(C) Calculate the difference between
2002 and 2008 VOC emissions factors
calculated in Step B and multiply by
2002 VMT. The result is the VOC
emissions reductions that will occur
between 2002 and 2008 without the
benefits of any post-1990 CAA
measures. These are the non-creditable
VOC reductions that occur over this
period. Calculate the difference between
2002 and 2008 NOX emissions factors
calculated in Step B and multiply by
2002 VMT. This result is the NOX
emissions reductions that will occur
between 2002 and 2008 without the
benefits of any post-1990 CAA
measures. These are the non-creditable
NOX reductions that occur over this
period.
(D) Subtract the non-creditable VOC
reductions calculated in Step C from the
actual anthropogenic 2002 VOC
inventory estimated in Step A. Subtract
the non-creditable NOX reductions
calculated in Step C from the actual
anthropogenic 2002 NOX inventory
estimated in Step A. These adjusted
VOC and NOX inventories are the basis
for calculating the target level of
emissions in 2008.
(E) The target level of VOC and NOX
emissions in 2008 needed to meet the
2008 ROP requirement is any
combination of VOC and NOX
reductions from the adjusted inventories
calculated in Step D that total 18
percent. For example, the target level of
VOC emissions in 2008 could be a 10
percent reduction from the adjusted
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VOC inventory in Step D and an 8
percent reduction from the adjusted
NOX inventory in Step D. The actual
projected 2008 VOC and NOX
inventories for all sources with all
control measures in place and including
projected 2008 growth in activity must
be at or lower than the target levels of
VOC and NOX emissions.
(3) Method 3: For all areas that have
used Method 1 above (and therefore do
not have a NOX target level of emissions
for 2008) and must meet an additional
reduction VOC requirement of 9 percent
every 3 years after 2008 with NOX
substitution allowed, following EPA’s
NOX Substitution Guidance. Each
subsequent target level of emissions
should be calculated as an emission
reduction from the previous target.
(A) Estimate the actual anthropogenic
base year NOX inventory in 2002 with
all 2002 control programs in place for
all sources.
(B) Using the same highway vehicle
activity inputs used to calculate the
actual 2002 inventory, run the
appropriate emissions model for VOC
and NOX in 2002 and 2008 (previously
done in Step B in Method 1 for VOC but
not necessarily for NOX) and 2011 with
all post-1990 CAA measures turned off.
Any other local inputs for I/M programs
should be set according to the program
that was required to be in place in 1990.
Fuel RVP should be set at 9.0 or 7.8
depending on the RVP required in the
local area as a result of fuel RVP
regulations promulgated in June, 1990.
(C) Calculate the difference between
2008 and 2011 VOC emission factors
calculated in Step B and multiply by
2002 VMT. The result is the VOC
emissions reductions that will occur
between 2008 and 2011 without the
benefits of any post-1990 CAA
measures. These are the non-creditable
VOC reductions that occur over this
period. Calculate the difference between
2002 and 2011 NOX emission factors
calculated in Step B and multiply by
2002 VMT. The result is the NOX
emissions reductions that will occur
between 2002 and 2011 without the
benefits of any post-1990 CAA
measures. These are the non-creditable
NOX reductions that occur over this
period.
(D) Subtract the non-creditable VOC
reductions calculated in Step C from the
2008 VOC target level of emissions
calculated previously. Subtract the noncreditable NOX reductions calculated in
Step C from the actual 2002 NOX
inventory of emissions calculated in
Step A. These adjusted VOC and NOX
inventories are the basis for calculating
the target level of emissions in 2011.
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(E) The target level of VOC and NOX
emissions in 2011 needed to meet the
2011 ROP requirement is any
combination of VOC and NOX
reductions from the adjusted inventories
calculated in Step E that total 9 percent.
For example, the target level of VOC
emissions in 2011 could be a 4 percent
reduction from the adjusted VOC
inventory in Step C and a 5 percent
reduction from the adjusted NOX
inventory in Step C. The actual
projected 2011 VOC and NOX
inventories for all sources with all
control measures in place and including
projected 2011 growth in activity must
be at or lower than the target levels of
VOC and NOX emissions.
(F) For subsequent 3-year periods
until the attainment date, repeat the
process for VOC. For subsequent 3-year
periods, the adjusted NOX inventory
should be based on the difference in
NOX emissions during that 3-year
period when all post-1990 CAA
measures are turned off, subtracted from
the previous NOX target level of
emissions. For example, for 2014, take
the difference in NOX emissions
reductions that will occur between 2011
and 2014 without the benefits of any
post-1990 CAA measures. This value is
subtracted from the 2011 target level of
NOX emissions calculated in Step D to
get the adjusted NOX inventory to be
used as the basis for calculating the
target level of NOX emissions in 2014.
(4) Method 4: For all areas that have
used Method 2 above (and therefore do
have a NOX target level of emissions for
2008) and must meet an additional
reduction VOC requirement of 9 percent
every 3 years after 2008 with NOX
substitution allowed, following EPA’s
NOX Substitution Guidance. Each
subsequent target level of emissions
should be calculated as an emissions
reductions from the previous target.
(A) Using the same highway vehicle
activity inputs used to calculate the
actual 2002 inventory, run the
appropriate emissions model for VOC
and NOX in 2008 (previously done in
Step B in Method 2) and 2011 with all
post-1990 CAA measures turned off.
Any other local inputs for I/M programs
should be set according to the program
that was required to be in place in 1990.
Fuel RVP should be set at 9.0 or 7.8
depending on the RVP required in the
local area as a result of fuel RVP
regulations promulgated in June 1990.
(B) Calculate the difference between
2008 and 2011 VOC emission factors
calculated in Step A and multiply by
2002 VMT. The result is the VOC
emissions reductions that will occur
between 2008 and 2011 without the
benefits of any post-1990 CAA
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measures. These are the non-creditable
VOC reductions that occur over this
period. Calculate the difference between
2008 and 2011 NOX emission factors
calculated in Step A and multiply by
2002 VMT. The result is the NOX
emissions reductions that will occur
between 2008 and 2011 without the
benefits of any post-1990 CAA
measures. These are the non-creditable
NOX reductions that occur over this
period.
(C) Subtract the non-creditable VOC
reductions calculated in Step B from the
2008 VOC target level of emissions
calculated previously. Subtract the noncreditable NOX reductions calculated in
Step B from the 2008 NOX target level
of emissions calculated previously.
These adjusted VOC and NOX
inventories are the basis for calculating
the target level of emissions in 2011.
(D) The target level of VOC and NOX
emissions in 2011 needed to meet the
2011 ROP requirement is any
combination of VOC and NOX
reductions from the adjusted inventories
calculated in Step E that total 9 percent.
For example, the target level of VOC
emissions in 2011 could be a 4 percent
reduction from the adjusted VOC
inventory in Step C and a 5 percent
reduction from the adjusted NOX
inventory in Step C. The actual
projected 2011 VOC and NOX
inventories for all sources with all
control measures in place and including
projected 2011 growth in activity must
be at or lower than the target levels of
VOC and NOX emissions.
(E) Repeat entire process for
subsequent 3-year periods until the
attainment date.
Appendix B to Preamble—Glossary of Terms
and Acronyms
ACT—Alternative Control Techniques
ARTBA—American Road and Transportation
Builders Association
BACT—Best Available Control Technology
BART—Best Available Retrofit Technology
CAA—Clean Air Act
CAAAC—Clean Air Act Advisory Committee
CADCs—Clean Air Development
Communities
CAIR—Clean Air Interstate Rule
CERR—Consolidated Emissions Reporting
Rule
CFR—Code of Federal Regulations
CMAQ—Congestion Mitigation and Air
Quality
CMSA—Consolidated Metropolitan
Statistical Area
CO—Carbon Monoxide
CTG—Control Technique Guideline
DOT—Department of Transportation
EMFAC—EMissions FACtors (a mobile
emissions model)
ESRP—Emissions Statement Reporting
Program
CTG—Control Technique Guidelines
EGUs—Electricity Generating Units
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EPA—Environmental Protection Agency
FIP—Federal Implementation Plan
FMVCP—Federal Motor Vehicle Control
Program
HON—Hazardous Organic NESHAP
ICR—Information Collection Requirement
I/M—Inspection and Maintenance Area
km—Kilometers
LADCO—Lake Michigan Air Directors
Consortium
LAER—Lowest Achievable Emission Rate
MACT—Maximum Achievable Control
Technology
MCR—Mid-course Review
MPO—Metropolitan Planning Organization
MSA—Metropolitan Statistical Area
NAA—Nonattainment Area
NAAMS—National Ambient Air Modeling
Strategy
NAAQS—National Ambient Air Quality
Standards
NAMS/SLAMS—National Air Monitoring
Stations/State and Local Air Monitoring
Stations
NAS—National Academy of Sciences
NCore—National Core Monitoring Stations
NESHAP—National Emission Standards for
Hazardous Air Pollutants
NOX—Nitrogen Oxides
NOy—Reactive Oxides of Nitrogen
NPRM—Notice of Proposed Rulemaking
NSR—New Source Review
NTAA—National Tribal Air Association
NTTAA—National Technology Transfer
Advancement Act of 1995
OMB—Office of Management and Budget
OTAG—Ozone Transport Assessment Group
OTR—Ozone Transport Region
PAMS—Photochemical Assessment
Monitoring Stations
PM—Particulate Matter
PM2.5—Fine Particulate Matter
PM10—Particulate Matter Having a Nominal
Aerodynamic Diameter Less than or
Equal to 10 Microns
ppb—Parts per Billion
ppm—Parts per Million
PSD—Prevention of Significant Deterioration
psi—Pounds Per Square Inch
RACM—Reasonably Available Control
Measures
RACT—Reasonably Available Control
Technology
RFASA—Regulatory Flexibility Act
Screening Analysis
RFP—Reasonable Further Progress
RIA—Regulatory Impact Analysis
ROG—Reactive Organic Gases
ROP—Rate of Progress
RPOs—Regional Planning Organizations
RVP—Reid Vapor Pressure
SBA—Small Business Administration
SCR—Selective Catalytic Reduction
SIPs—State Implementation Plans
SO2—Sulfur Dioxide
TAR—Tribal Authority Rule
TAS—(Treatment in the Same Manner as a
State ‘‘Treatment as State’’)
TEA–21—Transportation Equity Act for the
Twenty-first Century
TIPs—Tribal Implementation Plans
tpy—Tons Per Year
TSP—Total Suspended Particulates
TTN/SCRAM—Technical Transfer Network/
Support Center for Regulatory Air
Models
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UMRA—Unfunded Mandates Reform Act of
1995
U.S. DOT—United States Department of
Transportation
VCS—Voluntary Consensus Standards
VMT—Vehicle Miles Traveled
VOC—Volatile Organic Compound
List of Subjects
40 CFR Part 51
Air pollution control, Carbon
monoxide, Intergovernmental relations,
Ozone, Particulate matter,
Transportation, Volatile organic
compounds.
40 CFR Part 52
Air pollution control, Carbon
monoxide, Intergovernmental relations,
Ozone, Particulate matter.
40 CFR Part 80
Fuel additives, Gasoline, Motor
vehicle pollution, Ozone.
Authority: 42 U.S.C. 7408; 42 U.S.C. 7410;
42 U.S.C. 7501–7511f; 42 U.S.C. 7601(a)(1);
42 U.S.C. 7401.
Dated: November 9, 2005.
Stephen L. Johnson,
Administrator.
For the reasons stated in the preamble,
title 40, chapter I of the Code of Federal
Regulations is amended as follows:
I
PART 51—REQUIREMENTS FOR
PREPARATION, ADOPTION, AND
SUBMITTAL OF IMPLEMENTATION
PLANS
1. The authority citation for part 51
continues to read as follows:
I
Authority: 23 U.S.C. 101; 42 U.S.C. 7401–
7671q.
Subpart I—[Amended]
2. Section 51.165 is amended as
follows:
I a. By revising paragraphs
(a)(1)(iv)(A)(1) and (2).
I b. By adding paragraph
(a)(1)(iv)(A)(3).
I c. By adding paragraphs (a)(1)(v)(E)
and (F).
I d. By revising paragraph (a)(1)(x).
I e. By revising paragraph (a)(3)(ii)(C).
I f. By adding paragraphs (a)(8), (a)(9),
and (a)(10).
I
§ 51.165
Permit requirements.
(a) * * *
(1) * * *
(iv) * * *
(A) * * *
(1) Any stationary source of air
pollutants that emits, or has the
potential to emit, 100 tons per year or
more of any regulated NSR pollutant,
except that lower emissions thresholds
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shall apply in areas subject to subpart 2,
subpart 3, or subpart 4 of part D, title
I of the Act, according to paragraphs
(a)(1)(iv)(A)(1)(i) through (vi) of this
section.
(i) 50 tons per year of volatile organic
compounds in any serious ozone
nonattainment area.
(ii) 50 tons per year of volatile organic
compounds in an area within an ozone
transport region, except for any severe
or extreme ozone nonattainment area.
(iii) 25 tons per year of volatile
organic compounds in any severe ozone
nonattainment area.
(iv) 10 tons per year of volatile organic
compounds in any extreme ozone
nonattainment area.
(v) 50 tons per year of carbon
monoxide in any serious nonattainment
area for carbon monoxide, where
stationary sources contribute
significantly to carbon monoxide levels
in the area (as determined under rules
issued by the Administrator).
(vi) 70 tons per year of PM–10 in any
serious nonattainment area for PM–10;
(2) For the purposes of applying the
requirements of paragraph (a)(8) of this
section to stationary sources of nitrogen
oxides located in an ozone
nonattainment area or in an ozone
transport region, any stationary source
which emits, or has the potential to
emit, 100 tons per year or more of
nitrogen oxides emissions, except that
the emission thresholds in paragraphs
(a)(1)(iv)(A)(2)(i) through (vi) of this
section shall apply in areas subject to
subpart 2 of part D, title I of the Act.
(i) 100 tons per year or more of
nitrogen oxides in any ozone
nonattainment area classified as
marginal or moderate.
(ii) 100 tons per year or more of
nitrogen oxides in any ozone
nonattainment area classified as a
transitional, submarginal, or incomplete
or no data area, when such area is
located in an ozone transport region.
(iii) 100 tons per year or more of
nitrogen oxides in any area designated
under section 107(d) of the Act as
attainment or unclassifiable for ozone
that is located in an ozone transport
region.
(iv) 50 tons per year or more of
nitrogen oxides in any serious
nonattainment area for ozone.
(v) 25 tons per year or more of
nitrogen oxides in any severe
nonattainment area for ozone.
(vi) 10 tons per year or more of
nitrogen oxides in any extreme
nonattainment area for ozone; or
(3) Any physical change that would
occur at a stationary source not
qualifying under paragraphs
(a)(1)(iv)(A)(1) or (2) of this section as a
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major stationary source, if the change
would constitute a major stationary
source by itself.
*
*
*
*
*
(v) * * *
(E) For the purpose of applying the
requirements of (a)(8) of this section to
modifications at major stationary
sources of nitrogen oxides located in
ozone nonattainment areas or in ozone
transport regions, whether or not subject
to subpart 2, part D, title I of the Act,
any significant net emissions increase of
nitrogen oxides is considered significant
for ozone.
(F) Any physical change in, or change
in the method of operation of, a major
stationary source of volatile organic
compounds that results in any increase
in emissions of volatile organic
compounds from any discrete operation,
emissions unit, or other pollutant
emitting activity at the source shall be
considered a significant net emissions
increase and a major modification for
ozone, if the major stationary source is
located in an extreme ozone
nonattainment area that is subject to
subpart 2, part D, title I of the Act.
*
*
*
*
*
(x)(A) 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:
Pollutant Emission Rate
Carbon monoxide: 100 tons per year (tpy)
Nitrogen oxides: 40 tpy
Sulfur dioxide: 40 tpy
Ozone: 40 tpy of volatile organic compounds
or NOX
Lead: 0.6 tpy
PM–10: 15 tpy PM–10
(B) Notwithstanding the significant
emissions rate for ozone in paragraph
(a)(1)(x)(A) of this section, significant
means, in reference to an emissions
increase or a net emissions increase, any
increase in actual emissions of volatile
organic compounds that would result
from any physical change in, or change
in the method of operation of, a major
stationary source locating in a serious or
severe ozone nonattainment area that is
subject to subpart 2, part D, title I of the
Act, if such emissions increase of
volatile organic compounds exceeds 25
tons per year.
(C) For the purposes of applying the
requirements of paragraph (a)(8) of this
section to modifications at major
stationary sources of nitrogen oxides
located in an ozone nonattainment area
or in an ozone transport region, the
significant emission rates and other
requirements for volatile organic
compounds in paragraphs (a)(1)(x)(A),
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(B), and (E) of this section shall apply
to nitrogen oxides emissions.
(D) Notwithstanding the significant
emissions rate for carbon monoxide
under paragraph (a)(1)(x)(A) of this
section, significant means, in reference
to an emissions increase or a net
emissions increase, any increase in
actual emissions of carbon monoxide
that would result from any physical
change in, or change in the method of
operation of, a major stationary source
in a serious nonattainment area for
carbon monoxide if such increase equals
or exceeds 50 tons per year, provided
the Administrator has determined that
stationary sources contribute
significantly to carbon monoxide levels
in that area.
(E) Notwithstanding the significant
emissions rates for ozone under
paragraphs (a)(1)(x)(A) and (B) of this
section, any increase in actual emissions
of volatile organic compounds from any
emissions unit at a major stationary
source of volatile organic compounds
located in an extreme ozone
nonattainment area that is subject to
subpart 2, part D, title I of the Act shall
be considered a significant net
emissions increase.
*
*
*
*
*
(3) * * *
(i) * * *
(ii) * * *
(C)(1) Emissions reductions achieved
by shutting down an existing emission
unit or curtailing production or
operating hours may be generally
credited for offsets if they meet the
requirements in paragraphs
(a)(3)(ii)(C)(1)(i) through (ii) of this
section.
(i) Such reductions are surplus,
permanent, quantifiable, and federally
enforceable.
(ii) The shutdown or curtailment
occurred after the last day of the base
year for the SIP planning process. For
purposes of this paragraph, a reviewing
authority may choose to consider a prior
shutdown or curtailment to have
occurred after the last day of the base
year if the projected emissions
inventory used to develop the
attainment demonstration explicitly
includes the emissions from such
previously shutdown or curtailed
emission units. However, in no event
may credit be given for shutdowns that
occurred before August 7, 1977.
(2) Emissions reductions achieved by
shutting down an existing emissions
unit or curtailing production or
operating hours and that do not meet
the requirements in paragraph
(a)(3)(ii)(C)(1)(ii) of this section may be
generally credited only if:
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(i) The shutdown or curtailment
occurred on or after the date the
construction permit application is filed;
or
(ii) The applicant can establish that
the proposed new emissions unit is a
replacement for the shutdown or
curtailed emissions unit, and the
emissions reductions achieved by the
shutdown or curtailment met the
requirements of paragraph
(a)(3)(ii)(C)(1)(i) of this section.
*
*
*
*
*
(8) The plan shall provide that the
requirements of this section applicable
to major stationary sources and major
modifications of volatile organic
compounds shall apply to nitrogen
oxides emissions from major stationary
sources and major modifications of
nitrogen oxides in an ozone transport
region or in any ozone nonattainment
area, except in ozone nonattainment
areas or in portions of an ozone
transport region where the
Administrator has granted a NOX waiver
applying the standards set forth under
section 182(f) of the Act and the waiver
continues to apply.
(9)(i) The plan shall require that in
meeting the emissions offset
requirements of paragraph (a)(3) of this
section for ozone nonattainment areas
that are subject to subpart 2, part D, title
I of the Act, the ratio of total actual
emissions reductions of VOC to the
emissions increase of VOC shall be as
follows:
(A) In any marginal nonattainment
area for ozone—at least 1.1:1;
(B) In any moderate nonattainment
area for ozone—at least 1.15:1;
(C) In any serious nonattainment area
for ozone—at least 1.2:1;
(D) In any severe nonattainment area
for ozone—at least 1.3:1 (except that the
ratio may be at least 1.2:1 if the
approved plan also requires all existing
major sources in such nonattainment
area to use BACT for the control of
VOC); and
(E) In any extreme nonattainment area
for ozone—at least 1.5:1 (except that the
ratio may be at least 1.2:1 if the
approved plan also requires all existing
major sources in such nonattainment
area to use BACT for the control of
VOC); and
(ii) Notwithstanding the requirements
of paragraph (a)(9)(i) of this section for
meeting the requirements of paragraph
(a)(3) of this section, the ratio of total
actual emissions reductions of VOC to
the emissions increase of VOC shall be
at least 1.15:1 for all areas within an
ozone transport region that is subject to
subpart 2, part D, title I of the Act,
except for serious, severe, and extreme
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71699
ozone nonattainment areas that are
subject to subpart 2, part D, title I of the
Act.
(iii) The plan shall require that in
meeting the emissions offset
requirements of paragraph (a)(3) of this
section for ozone nonattainment areas
that are subject to subpart 1, part D, title
I of the Act (but are not subject to
subpart 2, part D, title I of the Act,
including 8-hour ozone nonattainment
areas subject to 40 CFR 51.902(b)), the
ratio of total actual emissions reductions
of VOC to the emissions increase of
VOC shall be at least 1:1.
(10) The plan shall require that the
requirements of this section applicable
to major stationary sources and major
modifications of PM–10 shall also apply
to major stationary sources and major
modifications of PM–10 precursors,
except where the Administrator
determines that such sources do not
contribute significantly to PM–10 levels
that exceed the PM–10 ambient
standards in the area.
*
*
*
*
*
I 3. Section 51.166 is amended as
follows:
I a. By revising paragraph (b)(1)(ii).
I b. By revising paragraph (b)(2)(ii).
I c. By revising the entry for ‘‘ozone’’ in
the list in paragraph (b)(23)(i).
I d. By revising paragraph (b)(49)(i).
I e. By revising footnote 1 to paragraph
(i)(5)(i)(e).
§ 51.166 Prevention of significant
deterioration of air quality.
*
*
*
*
*
(b) * * *
(1) * * *
(ii) A major source that is major for
volatile organic compounds or NOX
shall be considered major for ozone.
*
*
*
*
*
(2) * * *
(ii) Any significant emissions increase
(as defined at paragraph (b)(39) of this
section) from any emissions units or net
emissions increase (as defined in
paragraph (b)(3) of this section) at a
major stationary source that is
significant for volatile organic
compounds or NOX shall be considered
significant for ozone.
*
*
*
*
*
(23)(i) * * *
*
*
*
*
*
Ozone: 40 tpy of volatile organic
compounds or NOX
*
*
*
*
*
(49) * * *
(i) Any pollutant for which a national
ambient air quality standard has been
promulgated and any constituents or
precursors for such pollutants identified
by the Administrator (e.g., volatile
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(c) What criteria must the attainment
demonstration meet? An attainment
demonstration due pursuant to
paragraph (a) or (b) of this section must
meet the requirements of § 51.112; the
adequacy of an attainment
demonstration shall be demonstrated by
means of a photochemical grid model or
any other analytical method determined
by the Administrator, in the
Administrator’s discretion, to be at least
as effective.
*
*
*
*
*
I 6. Section 51.910 is added to read as
follows:
organic compounds and NOX are
precursors for ozone);
*
*
*
*
*
(i) * * *
(5) * * *
(i) * * *
(e) * * *
1 No de minimis air quality level is
provided for ozone. However, any net
emissions increase of 100 tons per year or
more of volatile organic compounds or
nitrogen oxides subject to PSD would be
required to perform an ambient impact
analysis, including the gathering of air
quality data.
Subpart X [Amended]
4. Section 51.906 is added to read as
follows:
I
§ 51.906 Redesignation to nonattainment
following initial designations for the 8-hour
NAAQS.
For any area that is initially
designated attainment or unclassifiable
for the 8-hour NAAQS and that is
subsequently redesignated to
nonattainment for the 8-hour ozone
NAAQS, any absolute, fixed date
applicable in connection with the
requirements of this part is extended by
a period of time equal to the length of
time between the effective date of the
initial designation for the 8-hour
NAAQS and the effective date of
redesignation, except as otherwise
provided in this subpart.
I 5. Section 51.908 is amended as
follows:
I a. By revising the section heading.
I b. By designating the existing text as
paragraph (d).
I c. By adding paragraphs (a), (b), and
(c).
§ 51.908 What modeling and attainment
demonstration requirements apply for
purposes of the 8-hour ozone NAAQS?
(a) What is the attainment
demonstration requirement for an area
classified as moderate or higher under
subpart 2 pursuant to § 51.903? An area
classified as moderate or higher under
§ 51.903 shall be subject to the
attainment demonstration requirement
applicable for that classification under
section 182 of the Act, except such
demonstration is due no later than 3
years after the area’s designation for the
8-hour NAAQS.
(b) What is the attainment
demonstration requirement for an area
subject only to subpart 1 in accordance
with § 51.902(b)? An area subject to
§ 51.902(b) shall be subject to the
attainment demonstration under section
172(c)(1) of the Act and shall submit an
attainment demonstration no later than
3 years after the area’s designation for
the 8-hour NAAQS.
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§ 51.910 What requirements for reasonable
further progress (RFP) under sections
172(c)(2) and 182 apply for areas
designated nonattainment for the 8-hour
ozone NAAQS?
(a) What are the general requirements
for RFP for an area classified under
subpart 2 pursuant to § 51.903? For an
area classified under subpart 2 pursuant
to § 51.903, the RFP requirements
specified in section 182 of the Act for
that area’s classification shall apply.
(1) What is the content and timing of
the RFP plan required under sections
182(b)(1) and 182(c)(2)(B) of the Act for
an area classified as moderate or higher
pursuant to § 51.903 (subpart 2
coverage)?
(i) Moderate or Above Area. (A)
Except as provided in paragraph
(a)(1)(ii) of this section, for each area
classified as moderate or higher, the
State shall submit a SIP revision
consistent with section 182(b)(1) of the
Act no later than 3 years after
designation for the 8-hour NAAQS for
the area. The 6-year period referenced in
section 182(b)(1) of the Act shall begin
January 1 of the year following the year
used for the baseline emissions
inventory.
(B) For each area classified as serious
or higher, the State shall submit a SIP
revision consistent with section
182(c)(2)(B) of the Act no later than 3
years after designation for the 8-hour
NAAQS. The final increment of progress
must be achieved no later than the
attainment date for the area.
(ii) Area with Approved 1-hour Ozone
15 Percent VOC ROP Plan. An area
classified as moderate or higher that has
the same boundaries as an area, or is
entirely composed of several areas or
portions of areas, for which EPA fully
approved a 15 percent plan for the 1hour NAAQS is considered to have met
section 182(b)(1) of the Act for the 8hour NAAQS and instead:
(A) If classified as moderate, the area
is subject to RFP under section 172(c)(2)
of the Act and shall submit no later than
3 years after designation for the 8-hour
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NAAQS a SIP revision that meets the
requirements of paragraph (b)(2) of this
section, consistent with the attainment
date established in the attainment
demonstration SIP.
(B) If classified as serious or higher,
the area is subject to RFP under section
182(c)(2)(B) of the Act and shall submit
no later than 3 years after designation
for the 8-hour NAAQS an RFP SIP
providing for an average of 3 percent per
year of VOC and/or NOX emissions
reductions for
(1) the 6-year period beginning
January 1 of the year following the year
used for the baseline emissions
inventory; and
(2) all remaining 3-year periods after
the first 6-year period out to the area’s
attainment date.
(iii) Moderate and Above Area for
Which Only a Portion Has an Approved
1-hour Ozone 15 Percent VOC ROP
Plan. An area classified as moderate or
higher that contains one or more areas,
or portions of areas, for which EPA fully
approved a 15 percent plan for the 1hour NAAQS as well as areas for which
EPA has not fully approved a 15 percent
plan for the 1-hour NAAQS shall meet
the requirements of either paragraph
(a)(1)(iii)(A) or (B) below.
(A) The State shall not distinguish
between the portion of the area that
previously met the 15 percent VOC
reduction requirement and the portion
of the area that did not, and
(1) The State shall submit a SIP
revision consistent with section
182(b)(1) of the Act no later than 3 years
after designation for the 8-hour NAAQS
for the entire area. The 6-year period
referenced in section 182(b)(1) of the
Act shall begin January 1 of the year
following the year used for the baseline
emissions inventory.
(2) For each area classified as serious
or higher, the State shall submit a SIP
revision consistent with section
182(c)(2)(B) of the Act no later than 3
years after designation for the 8-hour
NAAQS. The final increment of progress
must be achieved no later than the
attainment date for the area.
(B) The State shall treat the area as
two parts, each with a separate RFP
target as follows:
(1) For the portion of the area without
an approved 15 percent VOC RFP plan
for the 1-hour standard, the State shall
submit a SIP revision consistent with
section 182(b)(1) of the Act no later than
3 years after designation for the 8-hour
NAAQS for the area. The 6-year period
referenced in section 182(b)(1) of the
Act shall begin January 1 of the year
following the year used for the baseline
emissions inventory. Emissions
reductions to meet this requirement may
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come from anywhere within the 8-hour
nonattainment area.
(2) For the portion of the area with an
approved 15 percent VOC plan for the
1-hour NAAQS, the State shall submit a
SIP as required under paragraph (b)(2)of
this section.
(2) What restrictions apply on the
creditability of emission control
measures for the RFP plans required
under this section? Except as
specifically provided in section
182(b)(1)(C) and (D) and section
182(c)(2)(B) of the Act, all SIP-approved
or federally promulgated emissions
reductions that occur after the baseline
emissions inventory year are creditable
for purposes of the RFP requirements in
this section, provided the reductions
meet the requirements for creditability,
including the need to be enforceable,
permanent, quantifiable and surplus, as
described for purposes of State
economic incentive programs in the
requirements of § 51.493 of this part.
(b) How does the RFP requirement of
section 172(c)(2) of the Act apply to
areas subject to that requirement? (1)
An area subject to the RFP requirement
of subpart 1 pursuant to § 51.902(b) or
a moderate area subject to subpart 2 as
covered in paragraphs (a)(1)(ii)(A) of
this section shall meet the RFP
requirements of section 172(c)(2) of the
Act as provided in paragraph (b)(2) of
this section.
(2) The State shall submit no later
than 3 years following designation for
the 8-hour NAAQS a SIP providing for
RFP consistent with the following:
(i) For each area with an attainment
demonstration requesting an attainment
date of 5 years or less after designation
for the 8-hour NAAQS, the attainment
demonstration SIP shall require that all
emissions reductions needed for
attainment be implemented by the
beginning of the attainment year ozone
season.
(ii) For each area with an attainment
demonstration requesting an attainment
date more than 5 years after designation
for the 8-hour NAAQS, the attainment
demonstration SIP—
(A) Shall provide for a 15 percent
emission reduction from the baseline
year within 6 years after the baseline
year.
(B) May use either NOX or VOC
emissions reductions (or both) to
achieve the 15 percent emission
reduction requirement. Use of NOX
emissions reductions must meet the
criteria in section 182(c)(2)(C) of the
Act.
(C) For each subsequent 3-year period
out to the attainment date, the RFP SIP
must provide for an additional
increment of progress. The increment
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for each 3-year period must be a portion
of the remaining emission reductions
needed for attainment beyond those
reductions achieved for the first
increment of progress (e.g., beyond 2008
for areas designated nonattainment in
June 2004). Specifically, the amount of
reductions needed for attainment is
divided by the number of years needed
for attainment after the first increment
of progress in order to establish an
‘‘annual increment.’’ For each 3-year
period out to the attainment date, the
area must achieve roughly the portion of
reductions equivalent to three annual
increments.
(c) What method should a State use to
calculate RFP targets? In calculating
RFP targets for the initial 6-year period
and the subsequent 3-year periods
pursuant to this section, the State shall
use the methods consistent with the
requirements of sections 182(b)(1)(C)
and (D) and 182(c)(2)(B) to properly
account for non-creditable reductions.
(d) What is the baseline emissions
inventory for RFP plans? For the RFP
plans required under this section, the
baseline emissions inventory shall be
determined at the time of designation of
the area for the 8-hour NAAQS and
shall be the emissions inventory for the
most recent calendar year for which a
complete inventory is required to be
submitted to EPA under the provisions
of subpart A of this part or a more recent
alternative baseline emissions inventory
provided the State demonstrates that the
baseline inventory meets the CAA
provisions for RFP and provides a
rationale for why it is appropriate to use
the alternative baseline year rather than
2002 to comply with the CAA’s RFP
provisions.
I 7. Section 51.912 is added to read as
follows:
§ 51.912 What requirements apply for
reasonably available control technology
(RACT) and reasonably available control
measures (RACM) under the 8-hour
NAAQS?
(a) What is the RACT requirement for
areas subject to subpart 2 in accordance
with § 51.903? (1) For each area subject
to subpart 2 in accordance with § 51.903
of this part and classified moderate or
higher, the State shall submit a SIP
revision that meets the NOX and VOC
RACT requirements in sections
182(b)(2) and 182(f) of the Act.
(2) The State shall submit the RACT
SIP for each area no later than 27
months after designation for the 8-hour
ozone NAAQS.
(3) The State shall provide for
implementation of RACT as
expeditiously as practicable but no later
than the first ozone season or portion
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71701
thereof which occurs 30 months after
the RACT SIP is due.
(b) How do the RACT provisions
apply to a major stationary source?
Volatile organic compounds and NOX
are to be considered separately for
purposes of determining whether a
source is a major stationary source as
defined in section 302 of the Act.
(c) What is the RACT requirement for
areas subject only to subpart 1 pursuant
to § 51.902(b)? Areas subject only to
subpart 1 pursuant to § 51.902(b) are
subject to the RACT requirement
specified in section 172(c)(1) of the Act.
(1) For an area that submits an
attainment demonstration that requests
an attainment date 5 years or less after
designation for the 8-hour NAAQS, the
State shall meet the RACT requirement
by submitting an attainment
demonstration SIP demonstrating that
the area has adopted all control
measures necessary to demonstrate
attainment as expeditiously as
practicable.
(2) For an area that submits an
attainment demonstration that requests
an attainment date more than 5 years
after designation for the 8-hour NAAQS,
the State shall submit a SIP consistent
with the requirements of § 51.912(a) and
(b) except the State shall submit the
RACT SIP for each area with its request
pursuant to Clean Air Act section
172(a)(2)(A) to extend the attainment
date.
(d) What is the Reasonably Available
Control Measures (RACM) requirement
for areas designated nonattainment for
the 8-hour NAAQS? For each
nonattainment area required to submit
an attainment demonstration under
§ 51.908, the State shall submit with the
attainment demonstration a SIP revision
demonstrating that it has adopted all
RACM necessary to demonstrate
attainment as expeditiously as
practicable and to meet any RFP
requirements.
I 8. Section 51.913 is added to read as
follows:
§ 51.913 How do the section 182(f) NOX
exemption provisions apply for the 8-hour
NAAQS?
(a) A person may petition the
Administrator for an exemption from
NOX obligations under section 182(f) for
any area designated nonattainment for
the 8-hour ozone NAAQS and for any
area in a section 184 ozone transport
region.
(b) The petition must contain
adequate documentation that the criteria
in section 182(f) are met.
(c) A section 182(f) NOX exemption
granted for the 1-hour ozone standard
does not relieve the area from any NOX
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obligations under section 182(f) for the
8-hour ozone standard.
I 9. Section 51.914 is added to read as
follows:
§ 51.914 What new source review
requirements apply for 8-hour ozone
nonattainment areas?
The requirements for new source
review for the 8-hour ozone standard are
located in § 51.165 of this part.
I 10. Section 51.915 is added to read as
follows:
§ 51.915 What emissions inventory
requirements apply under the 8-hour
NAAQS?
For each nonattainment area subject
to subpart 2 in accordance with
§ 51.903, the emissions inventory
requirements in sections 182(a)(1) and
182(a)(3) of the Act shall apply, and
such SIP shall be due no later 2 years
after designation. For each
nonattainment area subject only to title
I, part D, subpart 1 of the Act in
accordance with § 51.902(b), the
emissions inventory requirement in
section 172(c)(3) of the Act shall apply,
and an emission inventory SIP shall be
due no later 3 years after designation.
For purposes of defining the data
elements for the emissions inventories
for these areas, the ozone-relevant data
element requirements under 40 CFR
part 51 subpart A apply.
I 11. Section 51.916 is added to read as
follows:
§ 51.916 What are the requirements for an
Ozone Transport Region under the 8-hour
NAAQS?
(a) In General. Sections 176A and 184
of the Act apply for purposes of the 8hour NAAQS.
(b) RACT Requirements for Certain
Portions of an Ozone Transport Region.
(1) The State shall submit a SIP
revision that meets the RACT
requirements of section 184 of the Act
for each area that is located in an ozone
transport region and that is—
(i) Designated as attainment or
unclassifiable for the 8-hour standard;
(ii) Designated nonattainment and
classified as marginal for the 8-hour
standard; or
(iii) Designated nonattainment and
covered solely under subpart 1 of part
D, title I of the CAA for the 8-hour
standard.
(2) The State is required to submit the
RACT revision no later than September
16, 2006 and shall provide for
implementation of RACT as
expeditiously as practicable but no later
than May 1, 2009.
I 12. Section 51.917 is added to read as
follows:
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§ 51.917 What is the effective date of
designation for the Las Vegas, NV, 8-hour
ozone nonattainment area?
The Las Vegas, NV, 8-hour ozone
nonattainment area (designated on
September 17, 2004 (69 FR 55956)) shall
be treated as having an effective date of
designation of June 15, 2004, for
purposes of calculating SIP submission
deadlines, attainment dates, or any
other deadline under this subpart.
I 13. Section 51.918 is added to read as
follows:
§ 51.918 Can any SIP planning
requirements be suspended in 8-hour
ozone nonattainment areas that have air
quality data that meets the NAAQS?
Upon a determination by EPA that an
area designated nonattainment for the 8hour ozone NAAQS has attained the
standard, the requirements for such area
to submit attainment demonstrations
and associated reasonably available
control measures, reasonable further
progress plans, contingency measures,
and other planning SIPs related to
attainment of the 8-hour ozone NAAQS
shall be suspended until such time as:
the area is redesignated to attainment, at
which time the requirements no longer
apply; or EPA determines that the area
has violated the 8-hour ozone NAAQS.
Appendix S to Part 51—[Amended]
Appendix S to part 51 is amended as
follows:
I 1. By revising the second sentence of
paragraph I and the the fourth sentence
of paragraph.
I 2. By revising paragraph II.A.4(i)(a)
and (b).
I 3. By adding paragraph II.A.4(i)(c).
I 4. By revising paragraph II.A.4(ii).
I 5. By revising paragraph II.A.5 (ii).
I 6. By adding paragraphs II.A.5(iv)
through (v).
I 7. By revising paragraph II.A.6(v)(c).
I 8. By revising the table in paragraph
II.A.10(i).
I 9. By adding paragraphs II.A.10(ii)
through (v).
I 10. By amending paragraph IV.A
Condition 1 by removing footnote 5.
I 11. By amending paragraph IV.A
Condition 3 by redesignating footnote 6
as footnote 5 and by redesignating
footnote 7 as footnote 6.
I 12. By amending paragraph IV.A
Condition 4 by removing footnote 8.
I 13. By revising paragraph IV.C.3.
I 14. By revising paragraph IV.D.
I 15. By revising paragraph IV.E.
I 16. By adding paragraphs IV.G
through H.
I 17. By amending paragraph V.A by
redesignating footnote 10 as footnote 7.
I 18. By revising the last sentence of
paragraph VI and adding paragraphs
VI.A, VI.B and VI.C.
I
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The revisions and additions read as
follows:
Appendix S to Part 51—Emission Offset
Interpretative Ruling
I.
* * * A major new source or major
modification which would locate in any area
designated under section 107(d) of the Act as
attainment or unclassifiable for ozone that is
located in an ozone transport region or which
would locate in an area designated in 40 CFR
part 81, subpart C, as nonattainment for a
pollutant for which the source or
modification would be major may be allowed
to construct only if the stringent conditions
set forth below are met. * * *
For each area designated as exceeding a
NAAQS (nonattainment area) under 40 CFR
part 81, subpart C, or for any area designated
under section 107(d) of the Act as attainment
or unclassifiable for ozone that is located in
an ozone transport region, this Interpretative
Ruling will be superseded after June 30, 1979
(a) by preconstruction review provisions of
the revised SIP, if the SIP meets the
requirements of Part D, Title 1, of the Act; or
(b) by a prohibition on construction under
the applicable SIP and section 110(a)(2)(I) of
the Act, if the SIP does not meet the
requirements of Part D. * * *
*
*
*
*
*
II. * * *
A. * * *
4.(i) * * *
(a) Any stationary source of air pollutants
which emits, or has the potential to emit, 100
tons per year or more of any pollutant subject
to regulation under the Act, except that lower
emissions thresholds shall apply in areas
subject to subpart 2, subpart 3, or subpart 4
of part D, title I of the Act, according to
paragraphs II.A.4(i)(a)(1) through (6) of this
Ruling.
(1) 50 tons per year of volatile organic
compounds in any serious ozone
nonattainment area.
(2) 50 tons per year of volatile organic
compounds in an area within an ozone
transport region, except for any severe or
extreme ozone nonattainment area.
(3) 25 tons per year of volatile organic
compounds in any severe ozone
nonattainment area.
(4) 10 tons per year of volatile organic
compounds in any extreme ozone
nonattainment area.
(5) 50 tons per year of carbon monoxide in
any serious nonattainment area for carbon
monoxide, where stationary sources
contribute significantly to carbon monoxide
levels in the area (as determined under rules
issued by the Administrator)
(6) 70 tons per year of PM–10 in any
serious nonattainment area for PM–10;
(b) For the purposes of applying the
requirements of paragraph IV.H of this Ruling
to stationary sources of nitrogen oxides
located in an ozone nonattainment area or in
an ozone transport region, any stationary
source which emits, or has the potential to
emit, 100 tons per year or more of nitrogen
oxides emissions, except that the emission
thresholds in paragraphs II.A.4(i)(b)(1)
through (6) of this Ruling apply in areas
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subject to subpart 2 of part D, title I of the
Act.
(1) 100 tons per year or more of nitrogen
oxides in any ozone nonattainment area
classified as marginal or moderate.
(2) 100 tons per year or more of nitrogen
oxides in any ozone nonattainment area
classified as a transitional, submarginal, or
incomplete or no data area, when such area
is located in an ozone transport region.
(3) 100 tons per year or more of nitrogen
oxides in any area designated under section
107(d) of the Act as attainment or
unclassifiable for ozone that is located in an
ozone transport region.
(4) 50 tons per year or more of nitrogen
oxides in any serious nonattainment area for
ozone.
(5) 25 tons per year or more of nitrogen
oxides in any severe nonattainment area for
ozone.
(6) 10 tons per year or more of nitrogen
oxides in any extreme nonattainment area for
ozone; or
(c) Any physical change that would occur
at a stationary source not qualifying under
paragraph II.A.4(i)(a) or (b) of this Ruling as
a major stationary source, if the change
would constitute a major stationary source by
itself.
(ii) A major stationary source that is major
for volatile organic compounds or nitrogen
oxides is major for ozone.
*
*
*
*
*
5. * * *
(ii) Any net emission increase that is
considered significant for volatile organic
compounds shall be considered significant
for ozone.
*
*
*
*
*
(iv) For the purpose of applying the
requirements of paragraph IV.H of this Ruling
to modifications at major stationary sources
of nitrogen oxides located in ozone
nonattainment areas or in ozone transport
regions, whether or not subject with respect
to ozone to subpart 2, part D, title I of the
Act, any significant net emissions increase of
nitrogen oxides is considered significant for
ozone.
(v) Any physical change in, or change in
the method of operation of, a major stationary
source of volatile organic compounds that
results in any increase in emissions of
volatile organic compounds from any
discrete operation, emissions unit, or other
pollutant emitting activity at the source shall
be considered a significant net emissions
increase and a major modification for ozone,
if the major stationary source is located in an
extreme ozone nonattainment area that is
subject to subpart 2, part D, title I of the Act.
6. * * *
(v) * * *
(c) The reviewing authority has not relied
on it in issuing any permit under regulations
approved pursuant to 40 CFR 51.165;
*
*
*
*
*
10. (i) * * *
Pollutant and Emissions Rate
Carbon monoxide: 100 tons per year (tpy)
Nitrogen oxides: 40 tpy
Sulfur dioxide: 40 tpy
Ozone: 40 tpy of volatile organic compounds
or NOX
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Lead: 0.6 tpy
Particulate matter: 25 tpy of particulate
matter emissions
PM–10: 15 tpy PM–10
(ii) Notwithstanding the significant
emissions rate for ozone in paragraph
II.A.10(i) of this Ruling, significant means, in
reference to an emissions increase or a net
emissions increase, any increase in actual
emissions of volatile organic compounds that
would result from any physical change in, or
change in the method of operation of, a major
stationary source locating in a serious or
severe ozone nonattainment area that is
subject to subpart 2, part D, title I of the Act,
if such emissions increase of volatile organic
compounds exceeds 25 tons per year.
(iii) For the purposes of applying the
requirements of paragraph IV.H of this Ruling
to modifications at major stationary sources
of nitrogen oxides located in an ozone
nonattainment area or in an ozone transport
region, the significant emission rates and
other requirements for volatile organic
compounds in paragraphs II.A.10(i), (ii), and
(v) of this Ruling shall apply to nitrogen
oxides emissions.
(iv) Notwithstanding the significant
emissions rate for carbon monoxide under
paragraph II.A.10(i) of this Ruling, significant
means, in reference to an emissions increase
or a net emissions increase, any increase in
actual emissions of carbon monoxide that
would result from any physical change in, or
change in the method of operation of, a major
stationary source in a serious nonattainment
area for carbon monoxide if such increase
equals or exceeds 50 tons per year, provided
the Administrator has determined that
stationary sources contribute significantly to
carbon monoxide levels in that area.
(v) Notwithstanding the significant
emissions rates for ozone under paragraphs
II.A.10(i) and (ii) of this Ruling, any increase
in actual emissions of volatile organic
compounds from any emissions unit at a
major stationary source of volatile organic
compounds located in an extreme ozone
nonattainment area that is subject to subpart
2, part D, title I of the Act shall be considered
a significant net emissions increase.
*
*
*
*
*
IV. * * *
C. * * *
3. Emission Reduction Credits from
Shutdowns and Curtailments.
(i) Emissions reductions achieved by
shutting down an existing source or
curtailing production or operating hours may
be generally credited for offsets if they meet
the requirements in paragraphs IV.C.3.i.1.
through 2 of this section.
(1) Such reductions are surplus,
permanent, quantifiable, and federally
enforceable.
(2) The shutdown or curtailment occurred
after the last day of the base year for the SIP
planning process. For purposes of this
paragraph, a reviewing authority may choose
to consider a prior shutdown or curtailment
to have occurred after the last day of the base
year if the projected emissions inventory
used to develop the attainment
demonstration explicitly includes the
emissions from such previously shutdown or
curtailed emission units. However, in no
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71703
event may credit be given for shutdowns that
occurred before August 7, 1977.
(ii) Emissions reductions achieved by
shutting down an existing source or
curtailing production or operating hours and
that do not meet the requirements in
paragraphs IV.C.3.i.1. through 2 of this
section may be generally credited only if:
(1) The shutdown or curtailment occurred
on or after the date the new source permit
application is filed; or
(2) The applicant can establish that the
proposed new source is a replacement for the
shutdown or curtailed source, and the
emissions reductions achieved by the
shutdown or curtailment met the
requirements of paragraphs IV.C.3.i.1.
through 2 of this section.
D. Location of offsetting emissions. The
owner or operator of a new or modified major
stationary source may comply with any offset
requirement in effect under this Ruling for
increased emissions of any air pollutant only
by obtaining emissions reductions of such air
pollutant from the same source or other
sources in the same nonattainment area,
except that the reviewing authority may
allow the owner or operator of a source to
obtain such emissions reductions in another
nonattainment area if the conditions in
IV.D.1 and 2 are met.
1. The other area has an equal or higher
nonattainment classification than the area in
which the source is located.
2. Emissions from such other area
contribute to a violation of the national
ambient air quality standard in the
nonattainment area in which the source is
located.
E. Reasonable further progress. Permits to
construct and operate may be issued if the
reviewing authority determines that, by the
time the source is to commence operation,
sufficient offsetting emissions reductions
have been obtained, such that total allowable
emissions from existing sources in the region,
from new or modified sources which are not
major emitting facilities, and from the
proposed source will be sufficiently less than
total emissions from existing sources prior to
the application for such permit to construct
or modify so as to represent (when
considered together with the plan provisions
required under CAA section 172) reasonable
further progress (as defined in CAA section
171).
*
*
*
*
*
G. Offset Ratios. 1. In meeting the
emissions offset requirements of paragraph
IV.A, Condition 3 of this Ruling for ozone
nonattainment areas that are subject to
subpart 2, part D, title I of the Act, the ratio
of total actual emissions reductions of VOC
to the emissions increase of VOC shall be as
follows:
(i) In any marginal nonattainment area for
ozone—at least 1.1:1;
(ii) In any moderate nonattainment area for
ozone—at least 1.15:1;
(iii) In any serious nonattainment area for
ozone—at least 1.2:1;
(iv) In any severe nonattainment area for
ozone—at least 1.3:1 (except that the ratio
may be at least 1.2:1 if the State also requires
all existing major sources in such
nonattainment area to use BACT for the
control of VOC); and
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(v) In any extreme nonattainment area for
ozone—at least 1.5:1 (except that the ratio
may be at least 1.2:1 if the State also requires
all existing major sources in such
nonattainment area to use BACT for the
control of VOC); and
2. Notwithstanding the requirements of
paragraph IV.G.1 of this Ruling for meeting
the requirements of paragraph IV.A,
Condition 3 of this Ruling, the ratio of total
actual emissions reductions of VOC to the
emissions increase of VOC shall be at least
1.15:1 for all areas within an ozone transport
region that is subject to subpart 2, part D, title
I of the Act, except for serious, severe, and
extreme ozone nonattainment areas that are
subject to subpart 2, part D, title I of the Act.
3. In meeting the emissions offset
requirements of paragraph IV.A, Condition 3
of this Ruling for ozone nonattainment areas
that are subject to subpart 1, part D, title I of
the Act (but are not subject to subpart 2, part
D, title I of the Act, including 8-hour ozone
nonattainment areas subject to 40 CFR
51.902(b)), the ratio of total actual emissions
reductions of VOC to the emissions increase
of VOC shall be at least 1:1.
H. Additional provisions for emissions of
nitrogen oxides in ozone transport regions
and nonattainment areas. The requirements
of this Ruling applicable to major stationary
sources and major modifications of volatile
organic compounds shall apply to nitrogen
oxides emissions from major stationary
sources and major modifications of nitrogen
oxides in an ozone transport region or in any
ozone nonattainment area, except in ozone
nonattainment areas where the Administrator
has granted a NOX waiver applying the
standards set forth under 182(f) and the
waiver continues to apply.
*
*
*
*
*
VI. Policy Where Attainment Dates Have Not
Passed
* * * In such cases, a new source locating
in an area designated in 40 CFR 81.300 et
seq. as nonattainment (or, where section III
of this Ruling is applicable, a new source that
would cause or contribute to a NAAQS
violation) may be exempt from the
Conditions of section IV.A if the conditions
in paragraphs VI.A through C are met.
A. The new source meets the applicable
SIP emission limitations.
B. The new source will not interfere with
the attainment date specified in the SIP
under section 110 of the Act.
C. The Administrator has determined that
conditions A and B of this section are
satisfied and such determination is published
in the Federal Register.
PART 52—[Amended]
1. The authority citation for part 52
continues to read as follows:
I
Authority: 42 U.S.C. 7401, et seq.
Subpart A—[Amended]
2. Section 52.21 is amended as
follows:
I a. By revising paragraph (b)(1)(ii).
I b. By revising paragraph (b)(2)(ii).
I
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c. By revising the entry for ‘‘ozone’’ in
list to paragraph (b)(23)(i).
I d. By revising paragraph (b)(50)(i).
I e. By revising the second sentence of
footnote 1 to paragraph (i)(5)(i).
I
§ 52.21 Prevention of significant
deterioration of air quality.
*
*
*
*
*
(b) * * *
(1) * * *
(ii) A major source that is major for
volatile organic compounds or NOX
shall be considered major for ozone.
*
*
*
*
*
(2) * * *
(ii) Any significant emissions increase
(as defined at paragraph (b)(40) of this
section) from any emissions units or net
emissions increase (as defined in
paragraph (b)(3) of this section) at a
major stationary source that is
significant for volatile organic
compounds or NOX shall be considered
significant for ozone.
*
*
*
*
*
(23)(i) * * *
*
*
*
*
*
Ozone: 40 tpy of volatile organic
compounds or NOX
*
*
*
*
*
(50) * * *
(i) Any pollutant for which a national
ambient air quality standard has been
promulgated and any constituents or
precursors for such pollutants identified
by the Administrator (e.g., volatile
organic compounds and NOX are
precursors for ozone);
*
*
*
*
*
(i) * * *
(5) * * *
(i) * * *
1 No de minimis air quality level is
provided for ozone. However, any net
emissions increase of 100 tons per year or
more of volatile organic compounds or
nitrogen oxides subject to PSD would be
required to perform an ambient impact
analysis, including the gathering of ambient
air quality data.
*
*
*
*
*
3. Section 52.24 is revised to read as
follows:
I
§ 52.24 Statutory restriction on new
sources.
(a) Any area designated
nonattainment pursuant to section
107(d) of the Act to which, immediately
prior to the enactment of the
Amendments to the Act of 1990
(November 15, 1990), a prohibition of
construction or modification of major
stationary sources was applied, shall
retain that prohibition if such
prohibition was applied by virtue of a
finding of the Administrator that the
State containing such an area:
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(1) Failed to submit an
implementation plan meeting the
requirements of an approvable new
source review permitting program; or
(2) Failed to submit an
implementation plan that provided for
timely attainment of the national
ambient air quality standard for sulfur
dioxide by December 31, 1982. This
prohibition shall apply until the
Administrator approves a plan for such
area as meeting the applicable
requirements of part D of title I of the
Act as amended (NSR permitting
requirements) or subpart 5 of part D of
title I of the Act as amended (relating to
attainment of the national ambient air
quality standards for sulfur dioxide), as
applicable.
(b) Permits to construct and operate as
required by permit programs under
section 172(c)(5) of the Act may not be
issued for new or modified major
stationary sources proposing to locate in
nonattainment areas or areas in a
transport region where the
Administrator has determined that the
applicable implementation plan is not
being adequately implemented for the
nonattainment area or transport region
in which the proposed source is to be
constructed or modified in accordance
with the requirements of part D of title
I of the Act.
(c) Whenever, on the basis of any
information, the Administrator finds
that a State is not in compliance with
any requirement or prohibition of the
Act relating to the construction of new
sources or the modification of existing
sources, the Administrator may issue an
order under section 113(a)(5) of the Act
prohibiting the construction or
modification of any major stationary
source in any area to which such
requirement applies.
(d) The restrictions in paragraphs (a)
and (b) of this section apply only to
major stationary sources of emissions
that cause or contribute to
concentrations of the pollutant (or
precursors, as applicable) for which the
transport region or nonattainment area
was designated such, and for which the
applicable implementation plan is not
being carried out in accordance with, or
does not meet, the requirements of part
D of title I of the Act.
(e) For any transport region or any
area designated as nonattainment for
any national ambient air quality
standard, the restrictions in paragraphs
(a) and (b) of this section shall apply to
any major stationary source or major
modification that would be major for the
pollutant (or precursors, where
applicable) for which the area is
designated nonattainment or a transport
region, if the stationary source or major
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modification would be constructed
anywhere in the designated
nonattainment area or transport region.
(f) The provisions in § 51.165 of this
chapter shall apply in interpreting the
terms under this section.
(g) At such time that a particular
source or modification becomes a major
stationary source or major modification
solely by virtue of a relaxation in any
enforceable limitation which was
established after August 7, 1980, on the
capacity of the source or modification
otherwise to emit a pollutant, such as a
restriction on hours of operation, then:
(1) If the construction moratorium
imposed pursuant to this section is still
in effect for the nonattainment area or
transport region in which the source or
modification is located, then the permit
may not be so revised; or
(2) If the construction moratorium is
no longer in effect in that area, then the
requirements of § 51.165 of this chapter
shall apply to the source or modification
as though construction had not yet
commenced on the source or
modification.
(h) This section does not apply to
major stationary sources or major
modifications locating in a clearly
defined part of a nonattainment area or
transport region (such as a political
subdivision of a State), where EPA finds
that a plan which meets the
requirements of part D of title I of the
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Act is in effect and is being
implemented in that part.
(i) [Reserved]
(j) [Reserved]
(k) For an area designated as
nonattainment after July 1, 1979, the
Emission Offset Interpretative Ruling,
40 CFR part 51, appendix S shall govern
permits to construct and operate applied
for during the period between the date
of designation as nonattainment and the
date the NSR permit program meeting
the requirements of part D is approved.
The Emission Offset Interpretative
Ruling, 40 CFR part 51, appendix S,
shall also govern permits to construct
and operate applied for in any area
designated under section 107(d) of the
CAA as attainment or unclassifiable for
ozone that is located in an ozone
transport region prior to the date the
NSR permitting program meeting the
requirements of part D is approved.
PART 80—[AMENDED]
1. The authority citation for part 80
continues to read as follows:
I
Authority: 42 U.S.C. 7414, 7545, and
7601(a).
Subpart D—[Amended]
2. Section 80.70 is amended as
follows:
I a. In the second sentence of paragraph
(m) introductory text remove the words
I
PO 00000
Frm 00095
Fmt 4701
Sfmt 4700
71705
‘‘included in’’ and add in their place the
words ‘‘identified pursuant to’’.
I b. In the third sentence of paragraph
(m) introductory text remove the words
‘‘listed in’’ and add in their place the
words ‘‘identified pursuant to’’.
I c. By revising paragraphs (m)(1) and
(2).
§ 80.70
Covered areas.
*
*
*
*
*
(m) * * *
(1) An area identified as a covered
area pursuant to this paragraph (m),
whose classification as a severe
nonattainment area under the 1-hour
ozone NAAQS is removed as a result of
removal of the 1-hour ozone NAAQS,
remains a covered area as follows:
(i) Prior to redesignation as attainment
for the 8-hour ozone NAAQS the area
remains a covered area;
(ii) After redesignation as attainment
for the 8-hour ozone NAAQS—
[RESERVED].
(2) An area identified as a covered
area pursuant to this paragraph (m),
whose classification as a severe
nonattainment area under the 1-hour
ozone NAAQS is removed as a result of
redesignation to attainment for the 1hour ozone NAAQS, remains a covered
area as follows: [RESERVED]
[FR Doc. 05–22698 Filed 11–28–05; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\29NOR2.SGM
29NOR2
Agencies
[Federal Register Volume 70, Number 228 (Tuesday, November 29, 2005)]
[Rules and Regulations]
[Pages 71612-71705]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-22698]
[[Page 71611]]
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Part II
Environmental Protection Agency
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40 CFR Parts 51, 52, and 80
Final Rule To Implement the 8-Hour Ozone National Ambient Air Quality
Standard; Final Rule
Federal Register / Vol. 70, No. 228 / Tuesday, November 29, 2005 /
Rules and Regulations
[[Page 71612]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 51, 52, and 80
[OAR 2003-0079; FRL-7996-8]
RIN 2060-AJ99
Final Rule To Implement the 8-Hour Ozone National Ambient Air
Quality Standard--Phase 2; Final Rule To Implement Certain Aspects of
the 1990 Amendments Relating to New Source Review and Prevention of
Significant Deterioration as They Apply in Carbon Monoxide, Particulate
Matter and Ozone NAAQS; Final Rule for Reformulated Gasoline
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
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SUMMARY: In this document, we are taking final action on most remaining
elements of the program to implement the 8-hour ozone national ambient
air quality standard (NAAQS or standard). This final rule addresses,
among other things, the following control and planning obligations as
they apply to areas designated nonattainment for the 8-hour ozone
NAAQS: reasonably available control technology and measures (RACT and
RACM), reasonable further progress (RFP), modeling and attainment
demonstrations, and new source review (NSR). We are issuing this rule
so that States and Tribes will know how these statutory control and
planning obligations apply and when State implementation plan (SIP)
revisions are due for these obligations so that the States may develop
timely submissions consistent with the statutory obligations and attain
the NAAQS as expeditiously as practicable but no later than their
maximum attainment dates. The intended effect of the rule is to provide
certainty to States and Tribes regarding development of those plans.
In this rule, we are also finalizing several revisions to the
regulations governing the nonattainment NSR programs mandated by
section 110(a)(2)(C) and part D of title I of the Clean Air Act (CAA).
Finally, this rule addresses what effect the transition to the 8-
hour standard will have on certain aspects of the Reformulated Gasoline
(RFG) program. The nine original mandatory RFG areas, as well as most
other areas that have become mandatory RFG areas by being reclassified
as severe areas under section 181(b) of the CAA, will continue to be
required to use RFG at least until they are redesignated to attainment
for the 8-hour NAAQS. The EPA reserves for future consideration what
effect the transition to the 8-hour standard will have on areas
reclassified as severe areas for the 1-hour NAAQS under section 181(b)
of the CAA that were redesignated to attainment for the 1-hour standard
before revocation of that standard.
EFFECTIVE DATE: This rule is effective on January 30, 2006.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. OAR-2003-0079. All documents in the docket are listed in
the EDOCKET index at https://www.epa.gov/edocket. Although listed in the
index, some information is not publicly available, i.e., Confidential
Business Information or other information whose disclosure is
restricted by statute. Certain other material, such as copyrighted
material, is not placed on the Internet and will be publicly available
only in hard copy form. Publicly available docket materials are
available either electronically in EDOCKET or in hard copy at the EPA
Docket Center (Air Docket), EPA/DC, EPA West, Room B102, 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 Office of Air and Radiation
Docket and Information Center is (202) 566-1742.
In addition, we have placed a variety of earlier materials
regarding implementation of the 8-hour ozone NAAQS on the Web site:
https://www.epa.gov/ttn/naaqs/ozone/o3imp8hr.
FOR FURTHER INFORMATION CONTACT: For general information: Mr. John
Silvasi, Office of Air Quality Planning and Standards, U.S.
Environmental Protection Agency, Mail Code C539-02, Research Triangle
Park, NC 27711, phone number (919) 541-5666, fax number (919) 541-0824
or by e-mail at silvasi.john@epa.gov or Ms. Denise Gerth, Office of Air
Quality Planning and Standards, U.S. Environmental Protection Agency,
Mail Code C539-02, Research Triangle Park, NC 27711, phone number (919)
541-5550, fax number (919) 541-0824 or by e-mail at
gerth.denise@epa.gov. For information concerning new source review: Ms.
Janet McDonald, Office of Air Quality Planning and Standards, U.S.
Environmental Protection Agency, Mail Code C539-03, Research Triangle
Park, NC 27711, phone number (919) 541-1450, fax number (919) 541-5509
or by e-mail at mcdonald.janet@epa.gov.
SUPPLEMENTARY INFORMATION:
Outline
I. What is the Background for this Rule?
II. What is Included in this Rule?
III. In Short, What Does this Final Rule Contain?
IV. Final Rule for Phase 2 Elements Other than NSR and RFG
A. Should prescribed requirements of subpart 2 apply in all 8-
hour nonattainment areas classified under subpart 2, or is there
flexibility in application in certain narrowly-defined
circumstances?
B. How will we address long-range transport of ground-level
ozone and its precursors when implementing the 8-hour ozone
standard?
C. How will we address transport of ground-level ozone and its
precursors for rural nonattainment areas, areas affected by
intrastate transport, and areas affected by international transport?
D. How will EPA address requirements for modeling and attainment
demonstration SIPs for areas implementing the 8-hour ozone standard?
E. What requirements for RFP should apply under the 8-hour ozone
standard?
F. Are contingency measures required in the event of failure to
meet a milestone or attain the 8-hour ozone NAAQS?
G. What requirements should apply for RACM and RACT for 8-hour
ozone nonattainment areas?
H. How will the section 182(f) NOX provisions be
handled under the 8-hour ozone standard?
I. Should EPA promulgate a NSR provision to encourage
development patterns that reduce overall emissions?
J. How will EPA ensure that the 8-hour ozone standard will be
implemented in a way which allows an optimal mix of controls for
ozone, PM2.5, and regional haze?
K. What emissions inventory requirements should apply under the
8-hour ozone NAAQS?
L. What guidance should be provided that is specific to Tribes?
M. What are the requirements for Ozone Transport Regions (OTRs)
under the 8-hour ozone standard?
N. Are there any additional requirements related to enforcement
and compliance?
O. What requirements should apply to emergency episodes?
P. What ambient monitoring requirements will apply under the 8-
hour ozone NAAQS?
Q. When will EPA require 8-hour attainment demonstration SIP
submissions?
R. How will the statutory time periods in the CAA be addressed
when we redesignate areas to nonattainment following initial
designations for the 8-hour NAAQS?
V. EPA's Final Rule for New Source Review
A. Background
B. Summary of Final Rule and Legal Basis
[[Page 71613]]
C. Comments and Responses
D. NSR Implementation Under the 8-hour ozone NAAQS
VI. Final Rule for RFG
A. Introduction
B. Background
C. What Action is EPA Taking?
D. Why is EPA Taking This Action?
E. Future Proceedings
F. Miscellaneous Administrative Changes to RFG Regulations
G. Comments and Responses
VII. Other Considerations
A. How will EPA's implementation of the 8-hour ozone NAAQS
affect funding under the Congestion Mitigation and Air Quality
Improvement (CMAQ) Program?
B. What is the relationship between implementation of the 8-hour
standard and the CAA's title V permits program?
C. What action is EPA taking on the Overwhelming Transport
Classification for Subpart 1 Areas?
VIII. 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 and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
L. Petitions for Judicial Review
M. Determination Under Section 307(d)
Appendix A to Preamble--Methods to Account for Non-Creditable
Reductions when Calculating ROP Targets for the 2008 and Later ROP
Milestone Years
Appendix B to Preamble--Glossary Of Terms and Acronyms
I. What Is the Background for This Rule?
On June 2, 2003 (68 FR 32805), we published a proposed rule to
implement the 8-hour ozone NAAQS. The proposal addressed a number of
implementation issues. We proposed one or more options for each issue
addressed in the proposal. Please refer to the proposed rule (68 FR
32802) for a detailed discussion and background information on the 8-
hour ozone NAAQS; the associated litigation; our proposed strategy for
areas to achieve the NAAQS; and the stakeholder process for gathering
input into this effort, among other topics.
On August 6, 2003 (68 FR 46536), we published a notice of
availability of the draft regulatory text for the proposed rule to
implement the 8-hour ozone NAAQS. This notice started a 30-day public
comment period on the draft regulatory text.
On April 30, 2004 (69 FR 23951), we published a final rule that
addressed the following key elements related to implementation of the
8-hour ozone NAAQS: classifications for the 8-hour NAAQS; revocation of
the 1-hour NAAQS (i.e., when the 1-hour NAAQS will no longer apply);
how anti-backsliding principles will ensure continued progress toward
attainment of the 8-hour ozone NAAQS; attainment dates; and the timing
of emissions reductions needed for attainment.
Following publication of the April 30, 2004 final rule, the
Administrator received three petitions, pursuant to section
307(b)(7)(B) of the CAA requesting reconsideration of a number of
aspects of the final rule.\1\ On September 23, 2004, we granted
reconsideration of three issues raised in the Earthjustice Petition. On
February 3, 2005 (70 FR 5593), we published a proposed rule to take
comment on two of these issues: (1) The provision that section 185 fees
would no longer be applicable once the 1-hour NAAQS is revoked and (2)
the timing for determination of what is an ``applicable requirement.''
On May 20, 2005, the final rule on these two issues was signed by the
Administrator of EPA. On April 4, 2005 (70 FR 17018), we published a
proposed rule to take comment on the issue of whether we should
interpret the Act to require areas to retain major NSR requirements
that apply to certain 1-hour ozone nonattainment areas in implementing
the 8-hour standard. We took final action on the NSR issues on June 30,
2005 (70 FR 39413; July 8, 2005).
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\1\ Three petitions for reconsideration of the Phase 1 Rule were
filed by: (1) Earthjustice on behalf of the American Lung
Association, Environmental Defense, Natural Resources Defense
Council, Sierra Club, Clean Air Task Force, Conservation Law
Foundation, and Southern Alliance for Clean Energy; (2) the National
Petrochemical and Refiners Association and the National Association
of Manufacturers; and (3) the American Petroleum Institute, American
Chemistry Council, American Iron and Steel Institute, National
Association of Manufacturers and the U.S. Chamber of Commerce.
---------------------------------------------------------------------------
On January 10, 2005, we granted reconsideration of the overwhelming
transport classification issue raised by Earthjustice in their
Petition. At the same time, we denied reconsideration of the issues
they raised in their Petition dealing with the applicability of RFG
when the 1-hour NAAQS is revoked and future 8-hour ozone redesignations
to nonattainment. We intend to publish a proposed rule on the
overwhelming transport classification shortly. We are continuing to
review the issues raised in the National Petrochemical and Refiners
Association and American Petroleum Institute Petitions. Copies of the
Petitions for Reconsideration and actions EPA has taken regarding the
Petitions may be found at: www.epa.gov/ttn/naaqs/ozone/o3imp8hr.
In addition, in the April 30, 2004 rule, we established a subpart E
in 40 CFR part 81 ``Identification of Area Designations and
Classifications for the 1-Hour Ozone NAAQS as of June 15, 2004
[Reserved].'' We intend to publish that list shortly.
Concerning the major NSR provisions, today's final regulations were
proposed as part of two different regulatory packages. On July 23, 1996
(61 FR 38250), we proposed changes to the major NSR program, including
codification of the requirements of part D of title I of the 1990 CAA
Amendments for major stationary sources of volatile organic compounds
(VOC), NOX, particulate matter having a nominal aerodynamic
diameter less than or equal to 10 microns (PM10), and CO. On
June 2, 2003 (68 FR 32802), we proposed a rule to implement the 8-hour
ozone NAAQS. In the 2003 action, we proposed a rule to identify the
statutory requirements that apply for purposes of developing SIPs under
the CAA to implement the 8-hour ozone NAAQS (68 FR 32802). We did not
propose specific regulatory language for implementation of NSR under
the 8-hour NAAQS. However, we indicated that we intended to revise the
nonattainment NSR regulations to be consistent with the rule for
implementing the 8-hour ozone NAAQS (68 FR 32844). On April 30, 2004
(69 FR 23951), we published a final rule that addressed classifications
for the 8-hour NAAQS. The April 2004 rule also included the NSR
permitting requirements for the 8-hour ozone standard, which
necessarily follow from the classification scheme chosen under the
terms of subpart 1 and subpart 2.
Also, in our 1996 action, and then again in our June 2, 2003
action, we proposed to amend our nonattainment NSR provisions to
expressly include NOX as an ozone precursor in nonattainment
major NSR programs (61 FR 38297 and 68 FR 32847). We also proposed
that, as provided under CAA section 182(f), a waiver from nonattainment
NSR for NOX as an ozone precursor would be available for
both subpart 1 and subpart 2 areas (68 FR 32846). Moreover, we proposed
to require States to modify their existing programs to include
NOX as an ozone
[[Page 71614]]
precursor in attainment areas (68 FR 32846).
In 1996, we proposed to revise the regulations limiting offsets
from emissions reductions due to shutting down an existing source or
curtailing production or operating hours below baseline levels
(``shutdowns/curtailments''). We proposed substantive revisions in two
alternatives that would ease, under certain circumstances, the existing
restrictions on the use of emission reduction credits from source
shutdowns and curtailments as offsets.
On July 23, 1996, we proposed to revise Sec. 52.24 to incorporate
changes made by the 1990 CAA Amendments related to the applicability of
construction bans (61 FR 38305). To clarify our intent, our proposed 8-
hour ozone NAAQS implementation rule in June 2003 explained that Sec.
52.24(k) remained in effect and would be retained. In that action, we
also proposed that we would revise Sec. 52.24(k) to reflect the
changes in the 1990 CAA Amendments (68 FR 32846). On June 2, 2003 (68
FR 32802), we explained implementation of the major NSR program under
the 8-hour ozone NAAQS during the SIP development period, and proposed
flexible NSR requirements for areas that expected to attain the 8-hour
NAAQS within 3 years after designation.
In this rule, we are also finalizing several revisions to the
regulations governing the nonattainment NSR programs mandated by
section 110(a)(2)(C) and part D of title I of the Clean Air Act (CAA).
First, we are codifying requirements added to part D of title I of the
CAA in the 1990 Amendments related to permitting of major stationary
sources in areas that are nonattainment for the ozone, particulate
matter (PM), and carbon monoxide (CO) NAAQS. Second, we are revising
the criteria for crediting emissions reductions credits from shutdowns
and curtailments as offsets. Third, we are revising the regulations for
permitting of major stationary sources in nonattainment areas in
interim periods between designation of new nonattainment areas and
EPA's approval of a revised SIP. Fourth, we are changing the
regulations that impose a moratorium (ban) prohibiting construction of
new or modified major stationary sources in nonattainment areas where
the State fails to have an implementation plan meeting all of the
requirements of part D. In addition to the changes to the nonattainment
NSR regulations, we also are making one change to the Prevention of
Significant Deterioration (PSD) regulations under part C of title I of
the CAA. We are codifying nitrogen oxides (NOX) as an ozone
precursor in attainment and unclassifiable areas.
Today's changes regarding NSR are based on the proposed rule
published on June 2, 2003 to Implement the 8-hour Ozone National
Ambient Air Quality Standard (NAAQS), as well as the proposed rule
published on July 23, 1996 for ``Prevention of Significant
Deterioration (PSD) and Non-attainment New Source Review (NSR).'' These
changes provide a consistent national program for permitting major
stationary sources under section 110(a)(2)(C) and parts C and D of
title I, including major stationary sources of ozone precursors in
ozone nonattainment areas.
For the reader's convenience, a glossary and list of acronyms
appears in Appendix B of this preamble.
II. What Is Included in This Rule?
Today's action, Phase 2 of the implementation rule, addresses
numerous topics, but primarily focuses on the following key
implementation obligations for areas designated nonattainment for the
8-hour NAAQS: RACT and RACM; RFP; modeling and attainment
demonstrations; and NSR. It also addresses what effect the transition
to the 8-hour standard will have on certain aspects of the RFG program.
III. In Short, What Does This Final Rule Contain?
This summary is intended to give only a convenient overview of our
final rule. It should not be relied on for the details of the actual
rule. The final rule (regulatory text) and the discussion of it in the
sections below should be consulted directly.
Summary of Section IV (Below): Final Rule for Phase 2 Elements Other
Than NSR and RFG
A. Should prescribed requirements of subpart 2 apply in all 8-hour
nonattainment areas classified under subpart 2, or is there flexibility
in application in certain narrowly defined circumstances?
There may be a basis for waiving a prescribed requirement on a
case-by-case basis where imposition of the requirement would create an
absurd result. If a State submits a demonstration that application of a
specific requirement in a specific nonattainment area would create an
absurd result, we will consider application of the absurd results
doctrine at that time. We believe that absurd results that might occur
from application of mandatory control measures would happen only in
rare instances, if at all.
B. How will we address long-range transport of ground-level ozone and
its precursors when implementing the 8-hour ozone standard?
The EPA has issued two major rules to address interstate transport
of ozone pollution. The 1998 NOX SIP Call Rule already is
achieving significant reductions in NOX emissions that
contribute to interstate ozone pollution in the eastern United States.
Nineteen States were required to achieve reductions by May 2004, and
additional reductions are required by May 2007.
On May 12, 2005, EPA published the Clean Air Interstate Rule (CAIR)
in the Federal Register (70 FR 25162). It establishes statewide sulfur
dioxide (SO2) and NOX emissions budgets for
upwind States that significantly contribute to nonattainment or
interfere with maintenance of the fine particle or 8-hour ozone air
quality standards in downwind States. For ozone, this action
established summertime NOX budgets for the District of
Columbia and 25 States in the eastern half of the country, with
reductions to be achieved by 2009 and 2015. The CAIR goes beyond the
SIP call by requiring reductions from additional States and by
requiring further emissions reductions in SIP call States.
C. How will we address transport of ground-level ozone and its
precursors for rural nonattainment areas, areas affected by intrastate
transport, and areas affected by international transport?
1. Rural Transport Nonattainment Areas
The final rule does not contain any revisions to current policy on
rural transport areas under section 182(h). We do not believe there are
any 8-hour nonattainment areas covered under subpart 2 that are
``rural'' and therefore eligible for consideration for coverage under
section 182(h).
2. Intrastate Transport
The final rule does not contain any additional provisions for
addressing intrastate transport for the reasons stated in the proposal.
3. How will EPA address transport of ground-level ozone and its
precursors for areas affected by international transport?
We are not setting forth any regulatory provisions related to
international transport in this rule. Section 179B of the CAA applies
for these purposes. We continue to recommend that States confer with
the appropriate EPA
[[Page 71615]]
Regional Office to establish on a case-by-case basis the technical
requirements for these analyses. These analyses will be subject to
public comment during the State and Federal SIP processes.
D. How will EPA address requirements for modeling and attainment
demonstration SIPs for areas implementing the 8-hour ozone standard?
The final rule retains the following three elements that each
attainment demonstration SIP must include: (1) Technical analyses to
locate and identify sources of emissions that are causing violations of
the 8-hour NAAQS within nonattainment areas (i.e., analyses related to
the emissions inventory required for the nonattainment area), (2)
adopted measures with schedules for implementation and other means and
techniques necessary and appropriate for attainment, and (3)
contingency measures required under section 172(c)(9) of the CAA that
can be implemented without further action by the State or the
Administrator to cover failures to meet RFP milestones and/or
attainment.
1. Attainment Demonstration Due Date
Areas required to submit an attainment demonstration must do so no
later than 3 years after the effective date of designation for the 8-
hour ozone NAAQS.
2. Multi-State Nonattainment Areas
State partners involved in a multi-State ozone nonattainment area
must work together to perform the appropriate modeling analyses to
identify control measures that will enable the area to achieve
attainment as expeditiously as practicable. Each State will be
responsible for its portion of the control program and will be held
accountable for controls identified for implementation within its State
boundaries.
3. Role of Modeling Guidance in Attainment Demonstrations
Attainment demonstrations must be consistent with 40 CFR 51.112. We
will generally review the demonstrations for technical merit using
EPA's most recent modeling guidance at the time the modeled attainment
demonstration is performed.
4. Multi-pollutant Assessments (One-Atmosphere Modeling)
There is no regulatory text on this issue, but the preamble makes
several recommendations concerning multi-pollutant assessments.
E. What requirements for RFP should apply under the 8-hour ozone
standard?
1. General Discussion
We are adopting nearly all the approaches set forth in our proposed
rule for the various 1-hour rate-of-progress (ROP) and 8-hour RFP
issues.
2. What is the content and timing of the plan for addressing the RFP
requirements under section 182(b)(1) for areas covered under subpart 2?
Areas that are classified as moderate under the 8-hour standard
that have already implemented their 15 percent plans under their 1-hour
ozone SIPs would be considered to have met the statutory 15 percent
requirement. Reasonable further progress for the first 6 years from the
baseline year would be covered under the more generic RFP requirements
of subpart 1. Serious and above areas would have to meet 3 percent
reductions per year starting in the baseline year averaged over each 3-
year period out to the attainment year.
An 8-hour nonattainment area that is identical, geographically, to
its predecessor 1-hour nonattainment area (which has already done the
15 percent reduction) will not be required to do another 15 percent
VOC-only reduction plan. For an 8-hour moderate or higher nonattainment
area that contains a 1-hour nonattainment area that has an approved 15
percent VOC ROP plan but also contains areas that do not have an
approved 15 percent VOC ROP plan, the final rule allows States the
choice between two options:
Option 1. Develop a new baseline and new 15 percent VOC ROP
emission reduction target for the entire newly expanded area. Determine
that emissions reductions that occur after the 2002 baseline emissions
inventory year are creditable in the combined new area. The reductions
must be of VOC only.
Option 2. Treat the 8-hour nonattainment area as divided between
the old 1-hour area(s) and the newly added 8-hour area. For the newly
added portion (which had not previously implemented a 15 percent plan),
States must establish a separate 15 percent VOC target under subpart 2.
The previous nonattainment area that fell under the 1-hour standard
will now be subject to the subpart 1 provisions of the CAA and will be
able to credit both VOC and NOX toward meeting the RFP
target for this portion of the nonattainment area. VOC reductions to
meet the 15 percent requirement for the portion of the new 8-hour
nonattainment area that has not yet met this requirement may come from
across the entire 8-hour area.
The subpart 1 RFP provisions addressed by the rule below that are
applicable in the former 1-hour portion of the area depend on the
subpart 2 area's attainment date as follows:
In moderate areas that have an attainment date within 5
years after their 8-hour designation, for which portions of the area
have previously met their 15 percent requirements under the 1-hour
standard, the former 1-hour portion will only be subject to subpart 1
RFP requirements, which will be satisfied with the measures that
demonstrate attainment as expeditiously as practicable. These areas
will not be developing RFP plans separate from their attainment plans.
Thus, for these areas, the only motor vehicle emissions budgets that
will be developed will be for the attainment year.
In moderate areas that have an attainment date beyond 5
years after their 8-hour designation, for which portions of the area
have previously met their 15 percent requirements under the 1-hour
standard, the former 1-hour portion will only be subject to subpart 1
RFP requirements, which will be satisfied with a plan to demonstrate 15
percent emissions reductions (which may be either VOC or NOX
or a combination of both) from 2002 to 2008, and any additional
emissions reductions needed for attainment beyond 2008. Thus, these
areas (the entire 8-hour nonattainment area) would establish a motor
vehicle emission budget for 2008 and for their attainment year.
Serious and above areas will be developing both a 15 percent VOC
plan for the new portion of the 8-hour nonattainment area and an 18
percent VOC/NOX plan for the portion of the area that
previously met its 15 percent requirement. Thus, the RFP plan as a
whole will establish total allowable emissions for 2008 for the entire
8-hour nonattainment area. Therefore, the plans for these areas, as
well as moderate areas that choose option one, will establish motor
vehicle emissions budgets for both 2008 and the attainment year.
3. What baseline year should be required for the emissions inventory
for the RFP requirement?
We are using the 2002 inventory as the baseline inventory for the
RFP requirement for areas designated nonattainment in 2004 primarily
because of timing concerns related to attainment dates and when data is
collected and compiled. However, in response to several comments, we
are allowing States the option of justifying the use of an alternative
baseline year inventory year for RFP.
[[Page 71616]]
4. Should moderate and higher classified areas be subject to prescribed
additional RFP requirements prior to their attainment date?
Moderate areas would have to provide additional emissions
reductions (VOC/NOX) needed to provide for attainment by the
beginning of the ozone season prior to the area's attainment date.
Serious and higher classified areas would need to provide in their SIPs
an additional average of three percent per year emission reduction over
each subsequent 3-year period beyond the initial 6-year period through
the attainment year.
5. What is the timing of the submission of the RFP plan?
For moderate and higher classified areas, the first RFP SIP must be
submitted within 3 years after the area's nonattainment designation.
For areas with a June 15, 2004 effective date, for the 8-hour
designations, the SIP would be due by June 15, 2007. This would provide
up to 3 years for States to develop and submit RFP plans, and 1
additional year (until the end of 2008) for control measures to be
implemented. The RFP SIP for any remaining 3-year periods out to the
attainment date beyond the first 6 years would be required to be
submitted with the attainment demonstration, i.e., within 3 years after
designation. We recommend that States complete their RFP plans as soon
as possible after designation to provide more time for sources to
implement the emissions reductions.
6. How should CAA restrictions on creditable measures be interpreted?
Which national measures should count as generating emissions reductions
credit toward RFP requirements?
All emissions reductions that occur after the baseline emissions
inventory year are creditable for purposes of the RFP requirements in
this section except as specifically provided in section 182(b)(1)(C)
and (D) and section 182(c)(2)(B) of the CAA which exclude four
categories of emissions reductions requirements required to be adopted
prior to 1990.
7. For areas covered only by subpart 1, how should the RFP requirement
be structured?
We are finalizing rules for two rather than three categories of
areas based on the CAA's division of attainment dates for subpart 1
areas under section 172(a)(2). The following are the two scenarios and
the RFP requirements for each:
Scenario A: Areas with attainment dates 5 years or less after
designation (i.e., for most areas on or before June 15, 2009).
Reasonable further progress for these areas would be met by ensuring
emissions reductions needed for attainment are implemented, as noted
above, by the beginning of the ozone season prior to the attainment
date. This would be similar to subpart 2 RFP for areas classified as
marginal.
Scenario B: Areas with attainment dates beyond 5 years after
designation (i.e., beyond 2009).
The RFP plan must show increments of progress from the
baseline emissions inventory year out to the attainment date.
The RFP SIP would first have to provide for a 15 percent
emission reduction from the baseline year within 6 years after the
baseline year (i.e., out to 2008).
The 15 percent RFP SIP would have to be submitted within 3
years after designation (i.e., in 2007).
Either NOX or VOC emissions reductions (or
both) could be used to achieve the 15 percent emission reduction
requirement.
For each subsequent 3-year period (after 2008) out to the
attainment date, the RFP SIP would have to provide for an additional
increment of progress no less than the amount of emissions reductions
that would be roughly proportional to the time between the end of the
first increment (in 2008) and the attainment date. This second RFP SIP
would also have to be submitted within 3 years after the effective date
of designation (i.e., in 2007).
8. Where part of an 8-hour nonattainment area was a 1-hour
nonattainment area with a ROP obligation extending past 2002, can
emissions reductions from the area's 1-hour ROP plan be used as credit
toward meeting the area's 8-hour RFP plan?
Where an area has both 1-hour and 8-hour RFP obligations for the
post-2002 period, the State may rely on emissions reductions from the
1-hour plan in achieving RFP for the 8-hour standard. The State could
develop a new baseline and new RFP emission reduction targets for the
entire 8-hour standard nonattainment area (i.e., the old 1-hour
standard nonattainment area and any newly added portion of the 8-hour
standard nonattainment area). Emissions reductions from measures in the
1-hour ozone SIP that are achieved after the 8-hour ozone NAAQS
baseline year could count (subject to creditability restrictions as
discussed above) toward meeting the RFP requirement for the entire 8-
hour area.
This approach would set an RFP target for the entire 8-hour ozone
nonattainment area. Under this approach, the new RFP target for the 8-
hour standard would replace the previous 1-hour ROP target (while
ensuring that, at a minimum, the emissions reductions required to meet
the old target are met; see 40 CFR 51.905(a)(1)(iii)).
9. Will EPA's ``Clean Data Policy'' apply for purposes of 8-hour RFP,
attainment demonstrations and other related requirements?
We intend to apply the Clean Data Policy, which we had applied
under the 1-hour standard, for purposes of the 8-hour standard. In this
action EPA is finalizing the statutory interpretation that is embodied
in the policy. The text of the final rule encapsulates the statutory
interpretation set forth in the policy.
10. How will RFP be addressed in Tribal areas?
We intend to follow the Tribal Authority Rule (TAR), which provides
Tribes with the ability to develop Tribal implementation plans (TIPs)
to address and implement the NAAQS in Indian country. It further
provides the Tribes with flexibility to develop these plans in a
modular way, as long as the elements of their TIPs are reasonably
``severable.''
11. How will RFP targets be calculated?
Appendix A to the preamble to this final rule provides calculation
procedures for determining the RFP targets. These have been revised
from those in the proposal to account for NOX and for
emissions models in addition to the MOBILE model.
12. Should EPA continue the policy of allowing substitution of controls
from outside the nonattainment area within 100 kilometers for VOC and
200 kilometers for NOX?
We intend to continue to rely on this policy at the current time.
The use of emissions reductions outside the nonattainment area must be
shown to be beneficial toward reducing ozone in the nonattainment area
and must ensure that the reductions meet the standard tests of
creditability (permanent, enforceable, surplus, and quantifiable).
13. When must RFP emissions reductions be achieved?
The target level of emissions must be met by the attainment date of
the attainment year. Section 182(c)(2)(B) requires that RFP be
continued out to the attainment date.
[[Page 71617]]
14. Banked emission reduction credits (including shutdown credits): Can
pre-baseline emission reduction credits be used to satisfy the RFP
requirement?
The baseline emissions should not include pre-enactment
banked emission credits since they were not actual emissions during the
calendar year of enactment of the CAA Amendments of 1990.
Banked emissions reductions credits created prior to
enactment of the CAA Amendments of 1990 are not creditable toward the
15 percent progress requirement. However, for purposes of equity, EPA
encourages States to allow sources to use such banked emissions credits
for offsets and netting as authorized.
When States use such banked credits for offsets and
netting to the extent otherwise creditable under the part D NSR
regulations, these pre-enactment emissions credits must be treated as
growth. Prior guidance on this issue is still relevant for banked
emission reduction credits in relation to the RFP requirement for the
8-hour ozone standard. However, because the rule for implementing the
8-hour ozone standard uses a 2002 baseline year, the prior guidance
should be interpreted with that baseline in mind instead of enactment
of the CAA Amendments of 1990.
F. Are contingency measures required in the event of failure to meet a
milestone or attain the 8-hour ozone NAAQS?
Contingency measures are required to be implemented in the event of
failure to meet a milestone or attain the 8-hour ozone NAAQS and must
accompany the attainment demonstration SIP. All subpart 1 and subpart 2
areas other than marginal areas need contingency measures.
G. What requirements should apply for RACM and RACT for 8-hour ozone
nonattainment areas?
1. Reasonably Available Control Technology (RACT)
For subpart 1 areas that submit a demonstration of attainment for 5
or less years after designation (i.e., do not request an attainment
date extension beyond 5 years after designation), the CAA's RACT
requirement is met with the control requirements associated with a
demonstration that the NAAQS is attained as expeditiously as
practicable.
For subpart 1 areas that submit an attainment demonstration that
requests an attainment date extension (i.e., beyond 5 years after
designation), subpart 2 moderate and above areas, and areas within an
Ozone Transport Region (OTR), a RACT SIP is required covering CTG
sources and major non-CTG sources. The RACT submittal date is 27 months
after designation, except a subpart 1 area shall submit the RACT SIP
with its attainment date extension request.\2\ States must require
sources to implement RACT no later than the first ozone season or
portion thereof which occurs 30 months after the required submittal
date.
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\2\ This is generally expected with the submission of the
attainment demonstration.
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Where a RACT SIP is required, State SIPs implementing the 8-hour
standard generally must assure that RACT is met, either through a
certification that previously required RACT controls represent RACT for
8-hour implementation purposes or through a new RACT determination.
States may use existing EPA guidance in making RACT determinations. The
State need not perform a NOX RACT analysis for sources
subject to the State's emission cap-and-trade program where the cap-
and-trade program has been adopted by the State and approved by EPA as
meeting the NOX SIP Call requirements or, in States
achieving CAIR reductions solely from electric generating units (EGUs),
the CAIR NOX requirements.\3\ States are free to conduct
case-by-case RACT determinations, or RACT determinations or
certifications for groups of sources, at their discretion.
---------------------------------------------------------------------------
\3\ Alternatively, a State need not perform a NOX
RACT analysis for sources subject to Federal implementation plan
that implements the emission reductions required by the
NOX SIP call or the CAIR.
---------------------------------------------------------------------------
2. Reasonably Available Control Measures (RACM)
For each nonattainment area required to submit an attainment
demonstration, the State must submit with the attainment demonstration
a SIP revision demonstrating that it has adopted all control measures
necessary to demonstrate attainment as expeditiously as practicable and
to meet any RFP requirements.
H. How will the section 182(f) NOX provisions be handled
under the 8-hour ozone standard?
The final rule allows a person to petition the Administrator for an
exemption from nonattainment major NSR and/or RACT requirements for
major stationary sources of NOX in 8-hour ozone
nonattainment areas and for any area in a section 184 ozone transport
region. The final rule includes an extension of the NOX
waiver provisions to 8-hour ozone nonattainment areas covered under
subpart 1 (as proposed) as well as subpart 2 nonattainment areas. In
addition, the final rule states that a section 182(f) NOX
exemption granted under the 1-hour ozone standard does not relieve the
area from any requirements under the 8-hour ozone standard. A petition
must contain adequate documentation that the exemption provisions in
section 182(f) are met. We recently issued updated guidance on
appropriate documentation regarding section 182(f) for application to
the 8-hour ozone program.\4\
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\4\ Memorandum dated January 14, 2005, ``Guidance on Limiting
Nitrogen Oxides (NOX) Requirements Related to 8-Hour
Ozone Implementation'' from Stephen D. Page, Director, Office of Air
Quality Planning and Standards, to Air Directors, Regions I-X.
---------------------------------------------------------------------------
I. Should EPA promulgate a NSR provision to encourage development
patterns that reduce overall emissions?
Section V of this preamble below addresses rules for NSR for the 8-
hour ozone standard. We are not at this time issuing any rule related
to Clean Air Development Communities (CADCs).
J. How will EPA ensure that the 8-hour ozone standard will be
implemented in a way which allows an optimal mix of controls for ozone,
fine particulate matter PM2.5), and regional haze?
We are continuing our policy of encouraging each State with an
ozone nonattainment area which overlaps or is nearby a PM2.5
nonattainment area to take all reasonable steps to coordinate the
required revisions for these nonattainment areas and meet reasonable
progress goals for regional haze.
K. What emissions inventory requirements should apply under the 8-hour
ozone NAAQS?
Existing ozone-relevant emissions data element requirements under
40 CFR 51 subpart A are sufficient to satisfy the emissions inventory
data requirements under the 8-hour ozone NAAQS.
L. What guidance should be provided that is specific to Tribes?
Section 301(d) of the CAA recognizes that American Indian Tribal
governments are generally the appropriate authority to implement the
CAA in Indian country. As discussed in the TAR, it is appropriate to
treat Tribes in the same manner as States for purposes of implementing
all of the provisions of the CAA, except those provisions for which EPA
has specifically determined that it is not appropriate to treat Tribes
in the same
[[Page 71618]]
manner as States. (The CAA provisions for which EPA has determined it
is not appropriate to treat Tribes in the same manner as States are
listed in section IV.L. of this preamble.) Examples of CAA provisions
for which EPA has determined it is not appropriate to treat Tribes in
the same manner as States include specific plan submittal and
implementation deadlines.
In implementing this rule, it is important for both States and
Tribes to work together to coordinate planning efforts. Other than in
very limited circumstances, State regulations do not apply to Indian
Country, but SIP control measures could impact downwind areas,
including Indian communities. In addition, nonattainment area
boundaries may include a portion of Indian Country. Coordinated
planning will help ensure that the planning decisions made by the
States and Tribes complement each other and achieve progress toward
meeting the NAAQS.
M. What are the requirements for Ozone Transport Regions (OTRs) under
the 8-hour ozone standard?
Section 184 continues to apply for purposes of the 8-hour standard;
therefore, the current OTR remains in place and the section 184 control
requirements continue to apply for purposes of the 8-hour standard. If
a new OTR is established for purposes of the 8-hour standard pursuant
to section 176A, that area would also be subject to the provisions and
additional control requirements of section 184.
N. Are there any additional requirements related to enforcement and
compliance?
We are not setting forth any additional rule related to compliance
and enforcement.
O. What requirements should apply to emergency episodes?
We have not yet proposed any rule revision related to emergency
episodes (at 40 CFR part 51, subpart H), and the final rule below does
not contain any such rule revision.
P. What ambient monitoring requirements will apply under the 8-hour
ozone NAAQS?
No monitoring requirements are being promulgated as part of this
rulemaking. The preamble discusses current relevant requirements (40
CFR part 58) and anticipated activities.
Q. When will EPA require 8-hour attainment demonstration SIP
submissions?
Modeled attainment demonstrations--where required--must be
submitted within 3 years after the effective date of the area's
nonattainment designation.
R. How will the statutory time periods in the CAA be addressed when we
redesignate areas to nonattainment following initial designations for
the 8-hour NAAQS?
For any area that is initially designated attainment or
unclassifiable for the 8-hour NAAQS and subsequently redesignated to
nonattainment for the 8-hour ozone NAAQS, the attainment date and dates
for submittal of any applicable requirements under subpart 1 or subpart
2 and these regulations would run from the date of redesignation to
nonattainment for the 8-hour NAAQS.
Summary of Section V (Below): EPA's Final Rule for New Source Review
In today's action, we are finalizing previously proposed changes to
three regulations that govern major NSR permitting of major stationary
sources in nonattainment areas--40 CFR 51.165, appendix S of 40 CFR
part 51, and 40 CFR 52.24.
The regulations at 40 CFR 51.165 contain the minimum elements that
a State's preconstruction permitting program for major stationary
sources in nonattainment areas must contain in order for EPA to approve
the State's program into the SIP. In Sec. 51.165, we are making
revisions to incorporate the major stationary source thresholds,
significant emission rates, and offset ratios pursuant to part D of
title I of the CAA, as amended in 1990, for the 8-hour ozone NAAQS, the
CO NAAQS, and the PM10 NAAQS. We are also promulgating final
changes to the requirements for emissions reductions achieved from
shutdowns or curtailments at Sec. 51.165(a)(3)(ii)(C). We are not
currently acting on any other proposed changes to 40 CFR 51.165.
Appendix S of 40 CFR part 51 contains the preconstruction
permitting program that applies to major stationary sources in
nonattainment areas lacking an approved part D NSR program. It applies
during the interim period after EPA designates an area as
nonattainment, but before EPA approves a SIP to implement the
nonattainment NSR requirements for that pollutant (SIP development
period). We are making the same changes to appendix S that we are
making to Sec. 51.165 to implement the CAA as revised by the 1990
Amendments. In addition, we are finalizing revisions to section VI of
appendix S to qualify applicability of this section. This revision is
an outgrowth of the proposed revisions to section VI in the 8-hour
NAAQS implementation proposal (68 FR 32802). We also are removing an
outdated exemption for sources increasing emissions less than 50 tons
per year (tpy).
The regulations at 40 CFR 52.24 contain restrictions on the
construction or modification of major stationary sources, including a
construction ban applicable in circumstances enumerated by the 1977
CAA. These regulations also apply if the Administrator determines
pursuant to CAA section 173(a)(4) that the State is not adequately
implementing the SIP for meeting the part D requirements. today's final
rules codify requirements of the 1990 CAA Amendments related to the
applicability of construction bans. The final rules at Sec. 52.24 also
codify that Sec. 51.165 applies in interpreting the terms in Sec.
52.24. The regulations at 40 CFR 52.24(k) retain the requirement that
appendix S governs permits to construct and operate applied for during
the period between the date of designation as nonattainment and the
date the part D plan for NSR is approved, but is updated to remove the
reference to the construction ban.
In addition to the changes to the nonattainment NSR regulations, we
also are making one change to the PSD regulations under part C of title
I of the CAA. We are codifying NOX as an ozone precursor in
attainment and unclassifiable areas.
Summary of Section VI (Below): Final Rule for RFG
Today's rule specifies that the nine original RFG mandatory areas
must continue to use RFG at least until they are redesignated to
attainment for the 8-hour standard. Similarly, areas that have been
reclassified as severe areas under section 181(b) of the CAA for the 1-
hour NAAQS, and which were not redesignated to attainment for the 1-
hour NAAQS prior to its revocation, must continue to use RFG at least
until they are redesignated to attainment for the 8-hour standard. The
EPA is reserving for future consideration what RFG requirements apply
to areas that were reclassified as severe under the 1-hour standard,
but were redesignated to attainment for that standard before its
revocation. The only such area that was redesignated to attainment
prior to revocation of the 1-hour standard is Atlanta, Georgia. The EPA
is also reserving for future consideration whether areas must continue
using RFG
[[Page 71619]]
after they are redesignated to attainment for the 8-hour standard, for
the original nine mandatory areas as well as the areas reclassified to
severe. Finally, EPA clarifies that the current opt-in rules will
remain in place after the 1-hour standard is revoked. Areas classified
under subpart 2 as marginal or above are eligible to opt-in to the RFG
program.
Summary of Section VII (Below): Other Considerations
A. How will EPA's implementation of the 8-hour ozone NAAQS affect
funding under the Congestion Mitigation and Air Quality Improvement
(CMAQ) Program?
This section describes the relationship between the CMAQ program
and the 8-hour ozone NAAQS implementation program.
B. What is the relationship between implementation of the 8-hour
standard and the CAA's title V permits program?
The interrelationship between implementation of the 8-hour ozone
standard and the title V permits program was not discussed in the
proposed rule. However, various questions have been raised about the
interface between the implementation of the 8-hour ozone standard and
the title V operating permits program. The preamble presents several
questions and answers, mainly dealing with how title V applicability is
affected by the new 8-hr ozone standard and the revocation of the 1-
hour ozone standard.
C. What action is EPA taking on the Overwhelming Transport
Classification for subpart 1 areas?
We are not completing rulemaking on the overwhelming transport
classification in this rulemaking. This section discusses the status of
the rulemaking.
IV. Final Rule for Phase 2 Elements Other Than New Source Review and
Reformulated Gasoline
The discussion of many of the regulatory elements below address
timing of required actions, such as submission dates for SIP revisions.
The discussion is primarily directed toward 8-hour ozone nonattainment
areas for which the effective date of the designation was June 15,
2004. However, a number of areas may have later effective dates for
their designations, such as early action compact areas and areas
subsequently redesignated from attainment to nonattainment for the 8-
hour ozone standard. For these situations, the timing will run from the
effective date of those designations. In cases in this preamble where
we have used June 15, 2004 as a substitute for the ``effective date,''
we are using it only for purposes of those areas with an effective date
of June 15, 2004.
A. Should prescribed requirements of subpart 2 apply in all 8-hour
nonattainment areas classified under subpart 2, or is there flexibility
in application in certain narrowly-defined circumstances?
[Section VI.D. of June 2, 2003 proposed rule (68 FR 32825); no
draft or final regulatory text.]
1. Background
The 1990 CAA Amendments overhauled the CAA's requirements for ozone
nonattainment areas and, in doing so, specified new mandatory measures
for many areas. The approach embodied in subpart 2 was to classify
areas according to the severity of their pollution. Areas with more
serious ozone pollution were given a higher classification that did two
things. First, the successively higher classifications provided a
successively longer maximum timeframe for attaining the ozone NAAQS.
Second, each higher classification mandated specific additional and/or
more stringent obligations than the classification immediately below.
Specifying mandatory measures in the statute was necessary because
States and EPA, prior to 1990, had failed to ensure that SIPs achieved
steady reasonable progress in reducing emissions or to require readily
available measures that were cost effective and necessary to meet the
standard. See generally H.R. Rep. No. 101-490 at 144-48 (1990).
For this rule, we examined the issue of mandatory measures from
both a legal and policy standpoint. Our legal view is guided by the
statutory language in part D of title I of the CAA. In addition, we
were guided by the Supreme Court's view of this language. Our policy
view is guided by past precedents and also the principles we set forth
in our proposed rule (June 3, 2003; 68 FR 32802).
We have consistently interpreted the CAA to mean that once an area
is classified under subpart 2, the subpart 2 requirements apply. While
certain requirements allow for some flexibility in how they apply, the
requirements do not allow for broad waivers. For example, all areas
classified as serious or above must meet the requirement for an
enhanced inspection and maintenance (I/M) program, however, there is
some flexibility in determining what type of I/M program meets the
requirement for an enhanced I/M program. The Supreme Court, in
addressing whether the classification provisions in subpart 2 applied
for purposes of the 8-hour ozone NAAQS found that they did and stated
that EPA's implementation scheme, which would have avoided
classifications under subpart 2, was unreasonable because it would
effectively nullify the subpart 2 provisions that Congress created with
the intent to limit State and EPA discretion. Whitman v. American
Trucking Assoc., 531 U.S. 484-85.
In the proposed rule, we recognized that there is case law doctrine
that might allow a case-by-case waiver from mandatory requirements when
sufficient evidence is presented that application of a specific
requirement in a particular area would cause absurd results.
2. Final Rule
We continue to interpret the CAA to mean that the prescribed
requirements for each classification under subpart 2 apply to areas
with such classification for the 8-hour NAAQS. As we noted in the
preamble to the proposed rule, there may be a basis for waiving a
prescribed requirement on a case-by-case basis where imposition of the
requirement would create an absurd result. However, as stated in the
proposed rule, we believe that absurd results that might occur from
application of mandatory control measures would happen only in rare
instances. If a State submits a demonstration that application of a
specific requirement in a specific nonattainment area would create an
absurd result, we will consider application of the absurd results
doctrine at that time.
3. Comment and Responses
Comment: A number of commenters supported the approach that we
discussed in the proposed rule. Other commenters agreed with the
overall concept that we proposed but felt that we should take
additional factors into consideration if we make case-by-case waivers
from subpart 2 requirements. Several commenters suggested that we take
the cost of controls into consideration when determining if there were
an absurd result while others suggested that we look at relative
control strategy effectiveness, e.g., allowing a demonstration that
NOX reductions are more effective and therefore may be
substituted for mandatory VOC emissions reductions.
Several other commenters stated that we should more broadly allow
substitution of subpart 2 mandatory measures. One commenter felt that
substitution of subpart 2 measures should be allowed as long as the
[[Page 71620]]
substituted measures are at least equivalent to the mandatory measures.
Another commenter stated that we should allow areas to adopt substitute
measures in lieu of subpart 2 measures where the subpart 2 measures
would not be as effective as the substitute measures in reaching
attainment. The commenter stated that we have been overly limited in
our characterization of when subpart 2 measures might be waived to
avoid an absurd result. The commenter believed that we should create a
categorical exemption as an exercise of agency power to allow areas to
substitute NOX for VOC measures or more effective control
measures for less effective control measures when doing so would
expedite attainment. Another commenter urged us to limit the strict
application of subpart 2 measures because the imposition of such
measures creates economic disincentives for companies to locate and
expand in nonattainment areas. A number of commenters stated that they
do not support the vehicle I/M or Stage II vapor recovery programs and
recommended that we provide States with flexibility in meeting these
requirements.
Response: Many of the commenters' suggestions go beyond the
application of an absurd results doctrine and instead suggest broad
waiver of subpart 2 requirements based on a determination that an
alternative or substitute is more effective. We do not believe that we
have the authority to broadly waive measures mandated by Congress. As
noted by the Supreme Court, Congress intended to cabin States'
discretion when it mandated the specific controls under subpart 2. See
e.g., Whitman, 531 U.S. 484-85. (``Whereas subpart 1 gives EPA
considerable discretion to shape nonattainment programs, subpart 2
prescribes large parts of them by law'' and ``EPA may not construe the
statute in a way that completely nullifies textually applicable
provisions meant to limit discretion'').
However, as stated in our proposed rule, we believe that case law
may provide EPA with limited flexibility to waive federally mandated
requirements on a case-by-case basis where application of those
requirements would produce an absurd result. We do not need to conclude
here what precise circumstances would create an absurd result. Rather,
that decision would need to be made on a case-by-case basis in the
context of a specific request. In general, we note that to demonstrate
an absurd result, a State would need to demonstrate that application of
the requirement would result in more harm than benefit. For example,
the programs mandated under subpart 2 are generally effective in
reducing emissions of the two ozone precursors--NOX and
VOC--and because reductions of those precursors generally lead to
improved air quality, we believe that such a demonstration could be
made, if at all, only in rare instances.
With regard to the comment relating to Stage II vapor recovery,
section 202(a)(6) of the CAA does provide for revision or waiver of the
Stage II vapor recovery requirement under certain conditions: ``The
requirements of section 182(b)(3) (relating to stage II gasoline vapor
recovery) for areas classified under section 181 as moderate for ozone
shall not apply after promulgation of such standards and the
Administrator may, by rule, revise or waive the application of the
requirements of such section 182(b)(3) for areas classified under
section 181 as Serious, Severe, or Extreme for ozone, as appropriate,
after such time as the Administrator determines that onboard emissions
control systems required under this paragraph are in widespread use
throughout the motor vehicle fleet.'' Currently, EPA is formulating
policy concerning how widespread use will be determined and has been
seeking participation from affected parties. Further information is
available at: https://www.epa.gov/ttn/naaqs/ozone/ozonetech/stage2/.
Comment: A few commenters disagreed with the approach in our
proposed rule. One commenter stated that we do not have the statutory
authority to create new waivers to subpart 2 requirements. Another
commenter stated that the CAA does not allow case-by-case waivers to
avoid ``absurd'' results. The commenter further stated that doing so
would in effect require us to rewrite the statute by regulation.
Response: As stated above, we agree that we do not have broad
authority to waive subpart 2 requirements and that the CAA itself does
not expressly create authority to waive such requirements. However, the
``absurd results'' line of cases provides that where application of a
statute as written would create a result counter to what Congress
intended, an Agency has limited authority to construe that provision in
a manner than would effectuate Congress' intent.\5\
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\5\ See Holy Trinity Church v. United States, 143 U.S. 457
(1892) (``If literal construction of the words of a statute be
absurd, the act must be so construed to avoid the absurdity.'');
Griffin v. Oceanic Contractors, Inc. 458 U.S. 564 (1982)
(recognizing the absurdity exemption, but concluding that a harsh
penalty provision did not produce results counter to Congress'
intent); Mova Pharm. Corp. v. Shalala, 140 F. 3d 1060 (D.C. Cir.
1998) (recognizing the absurdity exemption, but finding that a
``successful defense'' regulation went beyond the statute was not
necessary to meet Congressional intent.)
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B. How will we address long-range transport of ground-level ozone and
its precursors when implementing the 8-hour ozone standard?
[Section VI.F. of June 2, 2003 proposed rule (68 FR 32827); no
draft or final regulatory text.]
1. Background
Interstate transport can make it difficult or impossible for some
States to meet attainment deadlines for areas within their boundaries
solely by regulating sources