Implementation of the 1997 8-Hour Ozone National Ambient Air Quality Standard: Addressing a Portion of the Phase 2 Ozone Implementation Rule Concerning Reasonable Further Progress Emissions Reductions Credits Outside Ozone Nonattainment Areas, 40074-40083 [E9-19190]
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40074
Federal Register / Vol. 74, No. 153 / Tuesday, August 11, 2009 / Rules and Regulations
Periodic means occurring or recurring
at regular intervals. Each lessee must
specify the intervals for periodic
training and periodic assessment of
training needs in their training
programs.
Production safety includes measures,
practices, procedures, and equipment to
ensure safe, accident-free, and
pollution-free production operations, as
well as installation, repair, testing,
maintenance, and operation of surface
and subsurface safety equipment.
Production operations include, but are
not limited to, separation, dehydration,
compression, sweetening, and metering
operations.
*
*
*
*
*
[FR Doc. E9–19204 Filed 8–10–09; 8:45 am]
BILLING CODE 4310–MR–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 50 and 51
[EPA–HQ–OAR–2008–0419, FRL–8943–3]
RIN 2060–AP96
Implementation of the 1997 8-Hour
Ozone National Ambient Air Quality
Standard: Addressing a Portion of the
Phase 2 Ozone Implementation Rule
Concerning Reasonable Further
Progress Emissions Reductions
Credits Outside Ozone Nonattainment
Areas
I. General Information
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Final rule.
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A. Does This Action Apply to Me?
EPA is taking final action to
revise a portion of its Phase 2
implementation rule for the 8-hour
ozone National Ambient Air Quality
Standard (NAAQS or standard) for
which the Agency had sought a
voluntary remand from the U.S. Circuit
Court of Appeals for the District of
Columbia Circuit. The Court granted
EPA’s request by remanding and
vacating that portion of the rule.
Specifically, this rule addresses an
interpretation that allowed certain
credits toward reasonable further
progress (RFP) for the 8-hour standard
from emissions reductions outside the
nonattainment area.
DATES: This rule is effective on October
13, 2009.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2008–0419. All
documents in the docket are listed in
https://www.regulations.gov. Although
listed in the index, some information is
SUMMARY:
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not publicly available, i.e., Confidential
Business Information (CBI) 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 https://
www.regulations.gov or in hard copy at
the Air and Radiation Docket and
Information Center in the EPA
Headquarters Library, Room Number
3334 in the EPA West Building, located
at 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.
FOR FURTHER INFORMATION CONTACT: For
further information on the this final rule
contact: Ms. Denise Gerth, Office of Air
Quality Planning and Standards, (C539–
01), U.S. EPA, Research Triangle Park,
North Carolina 27711, telephone
number (919) 541–5550 or by e-mail at
gerth.denise@epa.gov, fax number (919)
541–0824; or Mr. John Silvasi, Office of
Air Quality Planning and Standards,
U.S. Environmental Protection Agency,
(C539–01), Research Triangle Park, NC
27711, telephone number (919) 541–
5666, fax number (919) 541–0824 or by
e-mail at silvasi.john@epa.gov.
SUPPLEMENTARY INFORMATION:
Entities potentially affected directly
by this action include state, local, and
tribal governments. Entities potentially
affected indirectly by this rule include
owners and operators of sources of
emissions [volatile organic compounds
(VOCs) and nitrogen oxides (NOx)] that
contribute to ground-level ozone
concentrations.
B. Where Can I Get a Copy of This
Document and Other Related
Information?
A copy of this document and other
related information is available from the
docket EPA–HQ–OAR–2008–0419.
C. How Is This Notice Organized?
The information presented in this
notice is organized as follows:
I. General Information
A. Does This Action Apply to Me?
B. Where Can I Get a Copy of This
Document and Other Related
Information?
C. How Is This Notice Organized?
II. What is the Background for This Rule?
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A. Proposed Regulatory Interpretation of
the Phase 2 Rule To Address RFP
Emission Credits Outside Ozone
Nonattainment Areas
III. This Action
A. Background
B. Final Rule
C. Comments and Responses
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act (RFA)
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
L. Determination Under Section 307(d)
II. What Is the Background for This
Rule?
A. Proposed Regulatory Interpretation of
the Phase 2 Rule To Address RFP
Emission Credits Outside Ozone
Nonattainment Areas
On July 21, 2008 (73 FR 42294), EPA
published a proposed rule to revise its
regulatory interpretation of the Phase 2
implementation rule for the 8-hour
ozone NAAQS to address the U.S.
Circuit Court of Appeals for the District
of Columbia Circuit’s vacatur and
remand of that portion of the
interpretation of the Phase 2
implementation rule for which EPA had
asked for a voluntary remand. The
proposal addressed a provision that
allowed credit toward RFP for the 8hour NAAQS from emission reductions
outside the nonattainment area. Readers
should refer to the proposed rule for
additional background on this action,
including the final Phase 2 ozone
implementation rule and the Court’s
vacatur and remand of the provision
allowing credit for emissions reductions
outside a nonattainment area for the
purposes of RFP for the 8-hour NAAQS.
III. This Action
A. Background
In the Phase 2 Rule to implement the
8-hour ozone NAAQS, EPA set forth an
interpretation that stated that credits
could be taken for emissions reductions
from a source outside the nonattainment
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Federal Register / Vol. 74, No. 153 / Tuesday, August 11, 2009 / Rules and Regulations
area provided that emissions from these
sources were included in the baseline
for calculating the percent reduction
needed. 70 FR 71612. However,
emissions from other sources outside
the nonattainment area did not have to
be included in the baseline if they did
not provide RFP credit for the
nonattainment area. The regulatory
interpretation stated that certain
additional conditions must be met for
such reductions to qualify for credit,
including that credit could be taken for
VOCs and NOX emissions reductions
within 100 kilometers (km) and 200 km
respectively, and there must be a
demonstration that the emissions from
outside the nonattainment area had an
impact on air quality levels within the
nonattainment area.
The Natural Resources Defense
Council (NRDC) filed a petition for
review of the Phase 2 Rule including the
implementation of the statutory
provisions regarding RFP. After briefing
had concluded in this case, EPA
published its final rule implementing
the NAAQS for fine particulate matter
(the ‘‘PM2.5 Implementation Rule’’) 72
FR 20586 (April 25, 2007). Because the
PM2.5 Implementation Rule significantly
modified the interpretation regarding
credits for emissions outside the
nonattainment area, EPA requested a
voluntary remand from the Court on
July 17, 2007, to consider whether to
revise the Phase 2 implementation rule
to be consistent with the provisions in
the PM2.5 rule. In response, the U.S.
Court of Appeals for the District of
Columbia Circuit vacated and remanded
that portion of the Phase 2 Rule which
provided credit under the 8-hour ozone
RFP requirement for VOCs and NOX
emission reductions from outside a
nonattainment area. EPA proposed to
revise its regulatory interpretation of the
RFP provisions in the Phase 2 Rule to
be consistent with its regulatory
interpretation of the RFP provisions in
the PM2.5 Implementation Rule. 73 FR
42294 (July 21, 2008).
EPA received seven comments on this
proposed rule. A few commenters
supported the proposal while others
opposed the action we proposed. The
commenters addressed the following
topics: requested clarification on how
the rule affects general conformity and
whether the transportation conformity
determinations are only required within
the nonattainment areas; stated that
nonattainment areas should be
expanded to include areas that
contribute to nonattainment as required
under section 107(d) of the Clean Air
Act (CAA) rather than allowing areas to
take credit outside of their
nonattainment for RFP reductions;
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requested assurance that the rules do
not allow substitution of NOX to meet
the 15 percent VOC reduction
requirement; stated that the rule lacks
mechanisms for addressing
overwhelming transport in State
Implementation Plan (SIP)
requirements; stated that the proposed
rule flouts the language and purpose of
the CAA and is arbitrary and that EPA
fails to offer a lawful or rational
justification for the proposal, etc.
Detailed responses to these comments
are in section C under Comments and
Responses.
B. Final Rule
Following its stated objective in the
request for a voluntary remand, EPA reevaluted its interpretation of the RFP
provision and is taking final action to
revise the earlier interpretation as
proposed on July 21, 2008 (73 FR 42294)
which is consistent with the provisions
in the PM2.5 Implementation Rule (72
FR 20636). Consequently if the state
justifies consideration of precursor
emissions for an area outside the
nonattainment area, EPA will expect
state RFP assessments to reflect
emissions changes from all sources in
this area. The state must include all
sources, not just some selected sources,
for the area providing emission
reductions in the calculation of either
(a) the RFP baseline from which to
calculate the percent reduction needed
for RFP or (b) the reductions obtained
that would be credited toward the RFP
requirement and the analysis of whether
the reductions from areas outside the
nonattainment area would contribute to
decreases in ozone levels in the
nonattainment area. Also, the
justification for considering emissions
outside the nonattainment area will
include justification of the state’s
selection of the area used in the RFP
plan for each pollutant. As is the case
with the PM2.5 rule, if a state justifies
consideration of precursor emissions for
an area outside the nonattainment area,
EPA expects state RFP assessments to
reflect emissions changes from all
sources in the area. The state cannot
include only selected sources providing
emission reductions in the analysis. The
inventories for 2002, 2009, 2012 (where
applicable) and the attainment year
would all reflect the same source
domain, i.e., the same set of sources
except for the addition of any known
new sources or removal of known,
permanently shut down sources.
In cases where the state justifies
consideration of emissions of one or
both of the ozone precursors (i.e.,VOC
and NOX) from outside the
nonattainment area, states must provide
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separate information regarding on-road
mobile source emissions within the
nonattainment area for transportation
conformity purposes.1 However, this
final rule does not change existing
statutory requirements that
transportation conformity
determinations are only required within
the nonattainment area boundary. The
CAA section 176(c)(5) and EPA’s
transportation conformity regulations
(40 CFR 93.102(b)) only require
conformity determinations in
nonattainment and maintenance areas,
and these requirements rely on SIP onroad motor vehicle emission budgets
that address on-road emissions within
the boundary of the designated
nonattainment area. For this reason and
consistent with the PM2.5
Implementation Rule (72 FR 20636), if
the state addresses emissions outside
the nonattainment area for an ozone
precursor, the on-road mobile source
component of the RFP inventory will
not satisfy the requirements for
establishing a SIP budget for
transportation conformity purposes. In
such a case, the state must supplement
the RFP inventory with an inventory of
on-road mobile source emissions to be
used to establish a motor vehicle
emissions budget for transportation
conformity purposes. This inventory
must: (1) Address on-road motor vehicle
emissions that occur only within the
designated nonattainment area, (2)
provide for the same milestone year or
years as the RFP demonstration, and (3)
satisfy other applicable requirements of
the transportation conformity
regulations (40 CFR part 93). As long as
the state provides this separate
emissions budget and conformity is
determined to that budget, EPA believes
that this approach will optimally
address both the RFP and the
transportation conformity provisions of
the CAA.
In addition, we interpret this final
rule to restrict the use of emission
reductions for RFP credit to areas within
the state, except in the case of multistate nonattainment areas, and only then
would allow RFP reductions from
outside the state to be credited from
outside the nonattainment area if the
states involved develop and submit a
coordinated RFP plan. EPA expects
states with multi-state nonattainment
areas to consult with other involved
states, to formulate a list of the measures
that they will adopt and the measures
1 Transportation conformity is required under
CAA section 176(c) to ensure that federally
supported transportation plans, programs, and
highway and transit projects are consistent with the
purpose of the SIP.
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that the other state(s) will adopt, and
then to adopt their list of measures
under the assumption that the other
state(s) will adopt their listed measures.
Each state would be responsible for
adopting and thereby providing for
enforcement of its list of measures, and
then that state and ultimately EPA (at
such time as the plan is approved)
would be responsible for assuring
compliance with the SIP requirements
which is an approach consistent with
the approach for RFP in the PM2.5
Implementation rule. (72 FR 20640).
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C. Comments and Responses
Comments Supporting EPA’s Approach
1. Comment: One commenter noted
that, in the Phase 2 Ozone
Implementation Rule (70 FR 71648,
November 29, 2005), EPA stated that
modeling analyses relating to the NOX
SIP call demonstrate that significant
contribution to nonattainment results
not only from source emissions within
a nonattainment area but also from
source emissions over a much broader
area. The commenter agrees that
allowing states to take credit for
reductions from sources outside of their
nonattainment areas may help reduce
ozone levels in the nonattainment area
and believes that reductions from
outside the nonattainment area are
sometimes necessary to attain the
standard.
EPA Response: The EPA agrees with
commenter. The preamble to the final
Phase 2 rule explains that the rationale
for allowing emission reduction credits
from outside the nonattainment area for
RFP purposes is based on modeling
analyses that showed that emissions
from outside the nonattainment area
could affect the nonattainment area and
that emission reductions from upwind
of a nonattainment area will help the
nonattainment area achieve progress
toward attainment. 70 FR 71648; 61 FR
65758 (December 13, 1996), and
Memorandum of December 29, 1997
from Richard D. Wilson to Regional
Administrators, Regions I–X entitled:
‘‘Guidance for Implementing the 1–Hour
Ozone and Pre-Existing PM10 NAAQS’’
(the 1997 Policy) located at URL: https://
www.epa.gov/ttn/oarpg/t1/memoranda/
iig.pdf.
2. Comment: One commenter
supports the proposal to revise the
interpretation for crediting emissions
reductions from outside a
nonattainment area for RFP to be
analogous with the provision in the
PM2.5 Implementation Rule.
Specifically, the commenter supports
the portion of the proposal that allows
RFP reductions from outside the state to
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be credited from outside the
nonattainment area if states develop a
coordinated RFP plan as part of their
SIPs.
EPA Response: The EPA agrees with
commenter. The EPA by this action
makes the RFP provisions regarding
credits from emission reductions
outside the nonattainment area in the
context of the ozone NAAQS consistent
with the interpretation in the context of
the PM2.5 NAAQS with respect to multistate areas.
Clarification Requested on How This
Rule Affects General Conformity
3. Comment: One commenter
appreciates EPA’s efforts in the proposal
to clarify that a state may no longer
include only selected sources from an
area outside of a nonattainment area for
emissions reduction credit in the SIP.
The commenter also appreciates EPA’s
efforts to address how the proposed rule
affects transportation conformity. The
commenter requests that EPA provide
clarity on how the proposed rule affects
general conformity requirements and
determinations in the final rule.
EPA Response: This regulatory
interpretation does not affect the
requirement for federal agencies to
demonstrate conformity with SIPs.
These requirements stem from section
176(c) of the CAA. Implementing
regulations published by EPA (40 CFR
93.150 -160) provide for when and how
federal agencies can make these
determinations. EPA discussed
transportation conformity in the
proposal only to clarify that it applies
only within nonattainment areas and to
facilitate development of appropriate
budgets for use in areas that take rate of
progress (ROP) credit from outside the
nonattainment area.
Nonattainment Areas Should Be
Expanded To Include Contributing
Sources
4. Comment: One commenter is
opposed to the revision because it is
contrary to the CAA. Section
107(d)(1)(A)(i) of the CAA requires the
designation as nonattainment for ‘‘any
area that does not meet (or that
contributes to ambient air quality in a
nearby area that does not meet) the
national primary or secondary ambient
air quality standard for that pollutant.’’
The CAA requires that instead of
allowing an area that is contributing to
the nonattainment area to be used to
demonstrate RFP goals, the designated
nonattainment area must be expanded
to include that area. A commenter also
feels that the proposal illegally
circumvents the statutory designation
provisions by allowing states to
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selectively claim credit for reductions
from outside areas without subjecting
those areas to the full range of
safeguards mandated by Congress for
such areas.
EPA Response: As a threshold matter,
EPA is not taking any action through
this regulatory interpretation to
establish procedures for designating or
not designating areas. The designations
process for each NAAQS generally
provides guidance on how to determine
nonattainment areas. Under CAA
section 107 (d)(1)(A) an area is
designated ‘‘nonattainment’’ if it does
not meet the NAAQS or is a ‘‘nearby’’
area that contributes to ambient air
quality in an area that is violating the
NAAQS.2
As the Agency explained in the final
preamble to the Phase 2 rule, the CAA
does not specify a distance that is
‘‘nearby’’ or a specific level of emissions
that is deemed to ‘‘contribute to’’
nonattainment (70 FR at 71648). EPA
also did not establish a hard-and-fast set
of rules to determine which areas are
‘‘nearby’’ or ‘‘contribute to’’
nonattainment. Instead, in guidance
EPA listed a broad set of factors for
states and EPA to consider in
determining the boundaries of each
nonattainment area. As for the comment
that EPA is circumventing the statutory
designations provisions by not
subjecting the outside areas to all the
requirements for nonattainment areas,
EPA believes that since these areas are
not necessarily ‘‘nearby’’ for
designations purposes, it is not
appropriate to subject these areas to all
of the requirements for nonattainment
areas. In this rule EPA is allowing
emissions reductions outside a
nonattainment area that benefits the
nonattainment area to be considered for
credit in emission reductions for ROP
purposes. Whether an area is ‘‘nearby’’
for purposes of designations is an issue
that would be considered on a case-bycase basis when the area is initially
designated nonattainment.
Clarification Requested That
Transportation Conformity Only
Applies in the Nonattainment Area
5. Comment: One state transportation
agency requested clarification in the
final rule that transportation conformity
only applies inside the nonattainment
area.
EPA Response: EPA’s final rule does
not change existing statutory
requirements that transportation
2 For example, Memorandum of March 28, 2002,
from John S. Seitz, ‘‘Boundary Guidance on Air
Quality Designations for the 8-Hour Ozone National
Ambient Air Quality Standards.’’
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Federal Register / Vol. 74, No. 153 / Tuesday, August 11, 2009 / Rules and Regulations
conformity determinations are only
required within the nonattainment area
boundary. CAA section 176(c)(5) and
section 93.102 of EPA’s transportation
conformity regulations only require
conformity determinations in
nonattainment and maintenance areas.
These requirements rely on SIP on-road
motor vehicle emission budgets that
address on-road emissions within the
boundary of the designated
nonattainment area. For this reason and
consistent with EPA’s PM2.5
implementation rule (72 FR 20636), if
the state addresses emissions outside
the nonattainment area for an ozone
precursor, the on-road mobile source
component of the RFP inventory will
not satisfy the requirements for
establishing a SIP budget for
transportation conformity purposes. In
such a case, the state must supplement
the RFP inventory with an inventory of
on-road mobile source emissions to be
used to establish a motor vehicle
emissions budget for transportation
conformity purposes, as described in
this final rule. As long as the state
provides this separate emissions budget
and conformity is determined to be
within the geographic boundary of the
nonattainment area, EPA believes that
this approach will optimally address
both the RFP and the transportation
conformity provisions of the CAA.
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Lack of Regulatory Text
6. Comment: One commenter believes
that the proposed revision appears to
provide an appropriate and reasonable
degree of flexibility to states in meeting
the RFP requirements. It is, however,
difficult for the commenter to evaluate
and comment on the proposal because
EPA has not provided any proposed
regulatory text that clearly states the
precise provisions and limitations of the
intended rule.
EPA Response: In this action we are
modifying a regulatory interpretation
that the Agency adopted in the Phase 2
rule (70 FR at 71647–48). Since
publication of that rule, EPA modified
its approach to RFP credits from outside
the nonattainment area in its PM2.5
Implementation Rule (72 FR 20636).
This action provides a regulatory
interpretation that is consistent with the
approach adopted in the PM2.5
Implementation Rule. Neither rule
included regulatory text on the specific
issue of RFP credits from outside the
nonattainment area and EPA believes
that it is unnecessary to include
regulatory text in this action.
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Substitution of NOX To Meet 15 Percent
VOC Requirement
7. Comment: The commenter assumes
that EPA does not intend to apply, and
will not apply, the policy reflected in
the proposal in a way that would allow
crediting of NOX emission reductions
outside the nonattainment area to meet
the 15 percent VOC emission reduction
requirement in section 182(b)(1) of the
CAA. Further the commenter stated that
allowing states to use NOx emission
reductions—wherever they may occur—
to satisfy section 182(b)(1) would
contradict the explicit statutory
provision that the 15 percent ROP
reduction requirement must be met by
VOC emission reductions only. See 70
FR 71,612, 71,636/1 (November 29,
2005).
The commenter also noted that this
principle is also reflected in the
December 1997 guidance memorandum
that addressed taking credit outside
nonattainment areas for purposes of
RFP.
EPA Response: The commenter is
correct that EPA does not intend to
apply the policy interpretation in the
proposed rule to allow substitution of
NOX emission reductions outside the
ozone nonattainment area to meet the 15
percent VOC requirement in section
182(b)(1). This is consistent with the
‘‘Guidance for Implementing the 1-Hour
Ozone and Pre-Existing PM10 NAAQS’’
that EPA issued on December 29, 1997
and the Phase 2 Ozone Implementation
Rule that EPA issued on November 29,
2005.
Lack of Mechanism for Addressing
Overwhelming Transport
8. Comment: One commenter feels
that EPA’s proposed rule lacks
reasonable, equitable mechanisms for
addressing overwhelming transport in
SIP requirements. This rule, as
proposed, would disallow RFP credit in
the Michigan SIP for out-of-state
reductions even though the local areas’
contribution to high ozone
concentrations measured at monitors in
counties abutting Lake Michigan are
negligible. The contributors, large urban
areas ‘across the lake, are in other states,
and West Michigan nonattainment areas
are not part of multistate nonattainment
areas. The proposed rule does nothing
to ameliorate the regulatory burdens of
ozone transport into West Michigan.
Additionally, the commenter stated that
the CAA lacks adequate provisions to
address ozone transport and include a
presumption that local emissions
reductions are necessary to reduce
ozone levels. The commenter
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recommends that amendments to the
CAA be pursued.
EPA Response: The regulatory
interpretation was not intended to
address the kind of situation posed by
the commenter. The revised
interpretation only applies to ROP plans
and does not attempt to resolve issues
of regional transport. Amendments to
the CAA to address regional transport
are only within Congress’ purview.
CAA Does Not Give EPA Authority To
Take Credit for Emissions Reductions
Outside the Nonattainment Area nor
Change the Emissions Baseline
9. Comment: One commenter believes
that the proposed rule is unlawful and
arbitrary. The commenter stated that
CAA sections 182(b)(1) and 182(c)(2)(B)
require SIPs for ozone nonattainment
areas to provide for an initial 15 percent
rate of progress cut in ozone-forming
emissions and subsequent three percent
per year emission cuts until attainment.
The CAA requires these cuts to be made
from emissions ‘‘in’’ each
nonattainment area. § 182(b)(1). The
commenter believes that allowing areas
to claim credit toward these ROP
requirements from emission cuts
outside the nonattainment area would
not require that outside reductions
provide the same ozone reduction
benefit to the nonattainment area as
would equivalent emission reductions
inside the nonattainment area. The
commenter feels that the EPA is without
authority to allow states to claim ROP
credit for emission reductions occurring
outside of the nonattainment area
because section 182(b)(1)(A) requires
each plan to provide for cuts in VOC
emissions ‘‘of at least 15 percent from
baseline emissions’’ (emphasis added).
The statute goes on to define ‘‘baseline
emissions’’ as ‘‘the total amount of
actual VOC or NOX emissions from all
anthropogenic sources in the area,’’
with certain exclusions not relevant
here. § 182(b)(1)(B) (emphasis added).
Thus, Congress explicitly mandated that
the required 15 percent emissions cut be
achieved from a baseline comprising
emissions from sources ‘‘in the
[nonattainment] area.’’ Congress did not
authorize EPA to grant rate of progress
credit for emission reductions outside
the nonattainment area or to redefine
‘‘baseline emissions’’ to include
emissions from sources outside of the
nonattainment area, even where those
outside reductions are alleged to or do
in fact ‘‘contribute’’ to ozone
concentrations in the nonattainment
area. The commenter feels that EPA
cannot allow states to credit emission
cuts from outside of the nonattainment
area toward meeting post-15 percent
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progress requirements. Nor can EPA
alter the baseline for the post-15 percent
cuts, a baseline that is identical to the
one set in the statute for the 15 percent
plans, and that is explicitly limited to
emissions from within the
nonattainment area.
EPA Response: The EPA notes first
that the regulatory interpretation set
forth here does not apply to the section
182(b)(1) requirement to provide 15
percent reductions within the first six
years from a baseline year, but only to
the section 182(c)(2)(B) requirement for
an average of three percent per year for
subsequent three year periods up to the
attainment date. The interpretation is
based on the December 29, 1997
memorandum from Richard D. Wilson,
‘‘Guidance for Implementing the 1–Hour
Ozone and Pre-Existing PM10 NAAQS.’’
Page 7 of the attachment to that
memorandum says: ‘‘The EPA believes
that the start date of the expanded
locality-based substitution credit for
ROP is changed from post-1999 ROP
requirements to post-1996 requirements.
EPA does not believe that it may allow
credit for substitutions to complete or
revise the 15 percent ROP requirement
for VOC emission reductions in
nonattainment areas through 1996.
Although the start date for application
of ROP substitution reductions from
outside the nonattainment area would
apply to post-1996 ROP requirements,
consistent with past Agency policy,
states would be able to bank excess
earlier reduction credits (NOX or VOC)
to apply to post-1996 and later
requirements.’’
Secondly, EPA disagrees with the
assertion in the comment that the
proposed rule is unlawful and arbitrary
and that EPA is without authority to
allow RFP credit for emission
reductions from outside the
nonattainment area. The CAA does not
expressly prohibit credits for emission
reductions outside the area. In fact, the
Fifth Circuit, which examined the same
language at issue here, found the
language ‘‘ambiguous’’ reasoning:
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On the one hand, the meaning of ‘‘in the
area’’ could be limited to emissions within
the nonattainment area. On the other hand,
the CAA does not expressly state that
emissions outside the nonattainment area are
prohibited, rather the Act only states that
emissions from sources ‘‘in the area’’ must be
included. We therefore find the CAA
ambiguous on this point.
Louisiana Envtl. Action Network
(‘‘LEAN’’) v. EPA, 382 F.3d 575, 585 (5th
Cir. 2004).3 If Congress intended to
3 Although the Fifth Circuit found application of
the 1997 policy as applied to the facts in that case
unsupported, it did so for reasons that are
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disallow credits from outside the
nonattainment area, it could have
expressly disallowed it as it did for RFP
credit for four other specific categories
of emission reductions, 42 U.S.C.
7511a(b)(1)(D)(i)–(iv), while otherwise
allowing credit for any reductions that
‘‘have actually occurred after November
15, 1990,’’ id. section 7511a(b)(1)(C).
See also the discussion in response to
comments 15 and 16.
Rule Is Unclear as to the Precise
Requirements for Crediting Outside
Reductions
10. Comment: One commenter stated
that the proposal is actually unclear as
to the precise requirements for crediting
these outside reductions. The Federal
Register notice describes EPA’s
approach for crediting outside
reductions in the PM2.5 Implementation
Rule, and states that EPA is proposing
to revise its earlier interpretation with
respect to ozone plans ‘‘to be consistent
with the analogous provisions in the
PM2.5 Implementation Rule.’’ The
proposal does not explain whether
‘‘consistent with’’ means ‘‘identical to’’
or whether it allows some differences
from the PM2.5 approach. For purposes
of these comments, the commenter will
assume EPA is proposing an identical
approach to the one adopted for PM2.5.
EPA Response: The commenter is
correct in the assumption that EPA’s
proposed approach follows the same
approach for ozone as followed for
PM2.5.
Rule Does Not Set Meaningful
Restrictions on Boundary Drawing for
the Outside Area
11. Comment: One commenter alleged
that the proposal sets no meaningful
restrictions on boundary drawing for the
‘‘outside’’ area, thereby allowing states
to gerrymander them in a way that
includes sources expected to cut
emissions while excluding sources that
are likely to increase their emissions.
Although the proposal appears to limit
the ‘‘outside’’ to a doughnut around the
nonattainment area of up to 200 km, it
inapposite here. First, the court was reviewing
EPA’s determination that continuing reductions
outside an area could be used as contingency
measures. The court found EPA had not
demonstrated that the policy had ‘‘any rational
connection with the relevant issue of what
contingency measures to apply when an attainment
deadline passes.’’ Id. at 586.
Second, the court found that in the specific case
under review there was no data to support the
presumption that the ‘‘outside’’ reductions selected
in that case ‘‘can affect emissions reductions in the
* * * area.’’ Id. In contrast, in its regulatory
interpretation, EPA is explicitly requiring that such
data be demonstrated in all cases prior to accepting
credits from outside a nonattainment area. 70 FR at
71,647/3.
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allows the states to choose the slice or
hole in that surrounding doughnut to
include for purposes of the RFP
calculation. Assuming EPA is proposing
the same approach used in the PM2.5
rule, the state need only show that
emissions from the area selected
substantially impact ambient
concentrations in the nonattainment
area. There is no stated requirement that
all areas substantially impacting the
nonattainment area be included. The
proposal does not prevent states from
defining whatever area they choose—
theoretically even the block on which
the selected source sits—for inclusion in
the RFP inventory.
EPA Response: Under this approach,
as a prerequisite to including emission
reductions from outside the
nonattainment area in the RFP
assessment, a state must justify the
outside area. The justification must
include a demonstration that these
outside emissions have a substantial
impact on nonattainment
concentrations. Because the
demonstration of such impacts likely
involve differing factors and
characteristics, EPA believes a one-size
fits all ‘‘boundary drawing’’ approach is
not an appropriate approach in this
instance. EPA will evaluate each RFP
assessment on a case-by-case basis to
determine whether a state using RFP
credits from outside the nonattainment
area has included the appropriate and
pertinent area for calculating the
emission reductions. In addition, if a
state wants to adopt this approach, the
RFP assessment must include emissions
for all sources within the pertinent area
in order to ensure that the RFP plan
reflects the actual net emissions changes
that occur within that area.
12. Comment: One commenter alleged
that the proposed 200 km radius for the
‘‘outside’’ area is also wholly arbitrary.
EPA offers no rational basis, and none
exists, for choosing that particular
distance and applying it to each and
every nonattainment area in the nation.
There is no evidence, for example, that
NOX emission reductions 200 km
outside a nonattainment area invariably
provide the same ROP benefit as the
same reductions inside the
nonattainment area. EPA appears to
have picked the 200 km figure out of
thin air. The arbitrariness of EPA’s
approach here is confirmed by
contrasting it with agency’s approach in
drawing nonattainment area boundaries.
In the latter situation, EPA has taken the
position that determining whether
nearby sources contribute to
nonattainment is too complex to be
dictated by hard and fast rules, and
instead requires a multi-factor analysis
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tailored to each area. See EPA’s Final
Brief in Catawba County v. EPA, No.
05–1064 (D.C. Cir) filed June 11, 2008.
EPA Response: The commenter’s
assertions are incorrect. EPA has not
picked the distances ‘‘out of thin air.’’
As described below, EPA has had this
policy, adopted after discussions and
input from the scientific community, in
place for over ten years. The December
1997 policy was developed ‘‘as a result
of the modeling results relating to the
NOX SIP Call, [which] 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.’’
1997 Policy at 5–6. In addition, under
the Federal Advisory Committee Act
(FACA), we formed a Subcommittee for
Development of Ozone, Particulate
Matter and Regional Haze
Implementation Programs that provided
recommendations and ideas to assist us
in developing implementation
approaches for these programs. We have
incorporated ideas from the FACA
process for a number of SIP elements,
particularly those related to transport of
ozone, the process for demonstrating
attainment of the ozone standard, and
requirements for ensuring reasonable
further progress. The distance of 100 km
for VOC and 200 km for NOX resulted
from discussions of the FACA
Subcommittee and generally represent
transport of one to two days.4 Further
information on the FACA process and
its reports is found at the following Web
site: https://www.epa.gov/ttn/faca/. This
regulatory interpretation incorporates
the same distance limitations, which
must be supported in an individual area
by data ‘‘that are shown to be beneficial
toward reducing ozone in the
nonattainment area.’’ 5 In addition, the
proposed regulatory interpretation does
not change the distances for crediting
emissions from outside the
nonattainment area for NOX and VOCs.
EPA proposed and finalized those
distances in the rulemaking for the
Phase 2 rule. The proposed regulatory
interpretation only modifies those
instances where the ozone RFP
interpretations were not consistent with
the PM2.5 Implementation Rule such as
whether emissions from all sources
should be included in the RFP
assessments for the pertinent area
outside the nonattainment area. Thus,
the comments on the distances
themselves are outside the scope of this
rulemaking.
4 See
5 70
Footnote 43 at 68 FR 32833 (June 2, 2003).
FR 71647, col 3. (November 29, 2005).
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Lack of Justification for Proposal
13. Comment: The commenter states
that the proposed rule is unlawful and
arbitrary in that EPA has failed to offer
a lawful or rational justification for the
proposal. The commenter states that the
notice of proposed rulemaking offers no
justification for allowing credit for
outside reductions, other than a desire
to provide ‘‘flexibility.’’ In the past, EPA
has stated other rationales for allowing
ROP credit for outside reductions, but as
the agency does not state any intent to
rely on them here, they cannot support
this iteration of the proposal. If EPA
wants to provide other rationales for the
proposal, it must first provide public
notice and an opportunity to comment.
EPA Response: EPA disagrees with
the commenter’s assertion that it has
provided no justification for its proposal
to modify its regulatory interpretation of
the RFP provisions. First, in the
preamble to the Phase 2 rule, EPA
explained its rationale for permitting
credits for reductions outside the
nonattainment area (70 FR 71647–48).
The proposed modification of that
regulatory interpretation does not
change the distances or the precursors
for which such credits may be taken
provided other conditions such as
reductions are not attributed to
measures otherwise mandated by the
CAA are met. Second, the preamble to
the proposed regulatory interpretation
explains that EPA is modifying its
approach to allowing credits for
emission reductions from outside the
nonattainment area to make it consistent
with the approach that the Agency
adopted in the PM2.5 Implementation
Rule. In the PM2.5 Implementation Rule,
EPA received comments that indicated
that RFP inventories for areas outside
the nonattainment area could include
selected sources expecting substantial
emissions reductions while excluding
other sources in the area expecting
emission increases. In response to those
comments, EPA modified its approach
and required that if a state justifies
consideration of emissions for an area
outside the nonattainment area, the RFP
assessments will be expected to reflect
emission changes from all sources in
this area and would no longer allow
states to include only selected sources
that provide emission reductions.
Because the rationale for the change
there is equally applicable for ozone,
EPA proposed the same regulatory
interpretation for RFP assessments for
ozone.
14. Comment: The commenter noted
that EPA has also tried to justify
overriding the statutory language by
citing section 182(c)(2)(C) which
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40079
provides for substitution of NOX
emission cuts for VOC emission cuts to
meet the percentage reduction
requirements in serious and above areas,
where the state shows that equivalent
ozone reductions will be achieved. EPA
erroneously claimed that this provision
somehow shows intent to allow even
broader exceptions, such as the one
here, as long as some ozone reductions
are achieved within the nonattainment
area. In reality, section 182(c)(2)(C)
contains no language at all authorizing
states to claim emission reduction credit
for emission cuts outside of the
nonattainment area, nor does it redefine
‘‘baseline emissions’’ to include
emissions from outside the
nonattainment area. The provision
merely defines the limited
circumstances in which an area can
substitute NOX emission cuts for VOC
emission cuts to meet percentage
reduction requirements. It does not
allow the required reductions to be
achieved outside the nonattainment
area. Moreover, a key requirement of
section 182(c)(2)(C) is that any
substitution of NOX reductions for VOC
reductions will ‘‘result in a reduction in
ozone concentrations at least
equivalent’’ to that which would result
from the required VOC percentage
reduction (emphasis added). EPA’s
proposed rule merely requires that
emissions from the ‘‘outside’’ area
‘‘contribute to’’ ozone concentrations in
the nonattainment area—it does not
require the ozone benefits from cutting
those outside emissions to be at least
equivalent to those achievable by
reductions inside the nonattainment
area (70 FR 71647).
EPA Response: The Phase 2 rule
clarified the 1997 policy to respond to
concerns identified in the Office of
Inspector General Report [OAR–2003–
0079–0849 AT 80 (‘‘OIG Report’’)]. The
regulatory interpretation for RFP did not
allow crediting of outside emissions
based solely on distance from the
nonattainment area boundary. Instead,
the regulatory interpretation stated that
the distances are only a general
presumption that would need areaspecific data showing that reductions
from sources in attainment areas benefit
the particular nonattainment area. 70 FR
71647–49. Under this approach, as a
prerequisite to including emission
reductions from outside the
nonattainment area in the RFP
assessment, a state must justify the
inclusion of sources outside the area.
The justification must include a
demonstration that these outside
emissions have a substantial impact on
nonattainment concentrations and that
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reductions in these emissions would
have a beneficial impact on the
nonattainment area.
As clarified in a response below, in
evaluating RFP submittals, EPA would
consider whether the reductions from
outside the nonattainment area could
reasonably be expected to yield
comparable air quality benefits as would
be obtained if the same quantity of
reductions were to occur inside the
nonattainment area.
15. Comment: The commenter offers
as support for the previous comment
based on the fact that EPA’s Office of
Inspector General (OIG) observed that
EPA’s policy allows credit ‘‘for all
emission reductions achieved by
outside sources within specified
distances outside the nonattainment
area boundaries without any
demonstration of the actual impact of
these specific emissions on the area’s
nonattainment * * *’’ OAR–2003–
0079–0849 AT 80 (‘‘OIG Report’’).
EPA Response: EPA believes that
when Congress allowed the substitution
of NOX controls for VOC controls to
meet the section 182(c)(2)(C) RFP
requirement, its choice of specific words
is telling because it referred to
‘‘reductions in ozone concentrations’’ in
the applicable nonattainment area,
rather than ‘‘reductions in emissions.’’
70 FR 71648. While the language in the
CAA does not explicitly state that
emission reductions from outside the
nonattainment area may be credited for
RFP assessments, EPA reasonably
interpreted this language as an
indication that Congress’ intent was to
lower ‘‘ozone concentrations’’—not just
‘‘emissions’’ of ozone precursors—
within the nonattainment area. As EPA
explained, ‘‘(i)t 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
(toward) RFP.’’ 70 FR 71648.
As for the commenter’s assertion that
VOC and NOX reductions should result
in equivalent benefits within the area,
the fact that EPA’s policy always had
limits for the distance outside the
nonattainment area was intended to
preclude emission reductions from
having negligible ozone benefits within
the nonattainment area. While it is
implicit in EPA’s proposed regulatory
interpretation in its evaluation of the
appropriateness of the credit reductions,
the Agency is now clarifying in
response to the commenter’s statement
that EPA, in evaluating RFP submittals,
would consider whether the reductions
from outside the nonattainment area
could reasonably be expected to yield
comparable air quality benefits as would
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be obtained if the same quantity of
reductions were to occur inside the
nonattainment area.
In setting forth a requirement for the
ozone transport region in section 184 of
the CAA, Congress realized that
controlling ozone would require
emission reductions from not just
nonattainment areas, but all areas that
were shown to contribute to ozone
concentrations, including areas outside
nonattainment areas. The work done
under the Ozone Transport Assessment
Group (OTAG) led to the NOX SIP call,
which resulted in State-wide NOX
emission budgets. The NOX SIP call,
with its significant NOX emission
reductions from attainment as well as
nonattainment areas, was highly
successful in reducing ozone
concentrations, and indeed provided
progress toward attainment for many of
the nonattainment areas in the eastern
portion of the U.S.6
A state’s ozone attainment
demonstration performed with
photochemical grid modeling will
invariably take account of emission
reductions not only from within the
nonattainment area, but also from
outside the nonattainment area.
Generally, a state will be unable to
demonstrate attainment for many areas
unless there are emission reductions
from attainment and nonattainment
areas outside the area for which the
state is performing the attainment
demonstration. An extreme hypothetical
example of this situation would be a
nonattainment area that is mostly rural
with few emissions of its own, but
which is ineligible for rural transport
area treatment and that is affected by
significant transport from upwind areas.
For its attainment demonstration, it
must rely totally on emission reductions
from upwind areas and may not be able
to demonstrate RFP from emission
reductions totally within the
nonattainment area.
Additionally, air quality modeling to
make a determination of equivalent
ozone reductions would be very
difficult. Ozone reductions from a
particular strategy of emission
reductions vary based on a number of
factors such as wind, climate, type of
emission source, location of sources,
and height of emissions release above
the ground. Therefore, the location and
6 ‘‘Evaluating Ozone Control Programs in the
Eastern United States: Focus on the NOX Budget
Trading Program, 2004’’ United States
Environmental Protection Agency; Office of Air and
Radiation; Office of Air Quality Planning and
Standards; Office of Atmospheric Programs. 1200
Pennsylvania Ave., NW., Washington, DC 20460.
EPA454–K–05–001. August 2005. Found at:
https://www.epa.gov/airmarkt/progress/docs/
ozonenbp.pdf.
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spatial extent of ozone reductions may
be highly variable on a day-to-day basis.
In many cases, emission reductions
from farther away from a receptor
location could be more beneficial in
reducing ozone than emission
reductions from a nearer location in the
nonattainment area. The fact that the
NOX SIP call regional emission
reductions have been shown to reduce
ozone concentrations in almost all
nonattainment areas is a testament to
the fact that regional NOX controls are
beneficial in reducing ozone. The
current policy of allowing reductions for
RFP purposes only out to certain welldefined geographic distances would
serve to prevent abuse.
Section 182(c)(2)(C) does require that
NOX reductions must be shown to
reduce ozone concentrations ‘‘at least
equivalent’’ to that which would result
from VOC reductions. In response to the
CAA’s requirement of section
182(c)(2)(C), EPA had in the early- and
mid-1990’s issued guidance,7 8 for
implementation of this provision. The
guidance is based on two principles:
First, an equivalency demonstration
requires that cumulative RFP emission
reductions must be consistent with the
NOX and VOC emission reductions
determined in the ozone attainment
modeling demonstration; in other
words, a ton of NOX cannot simply
substitute for a ton of VOC since the air
quality impact might be entirely
different. Second, specified reductions
in NOX and VOC emissions should be
accomplished in the interim period
between the time of the beginning of the
RFP period in question (at the time, that
was the end of 1996) and the attainment
date, consistent with the continuous
RFP emission reduction requirement.
Thus, substituting NOX emission
reductions for VOC emission reductions
for RFP purposes has consistently been
done in the context of the area’s
attainment demonstration in order to
demonstrate equivalent ozone
reductions regardless of whether the
emission reductions that are credited for
RFP purposes come wholly within the
nonattainment area or where some come
from outside the nonattainment area.9
7 NO Substitution Guidance, December, 1993.
X
Office of Air Quality Planning and Standards; U.S.
Environmental Protection Agency; Research
Triangle Park, North Carolina 27711.
8 Memorandum from John Seitz, ‘‘Clarification of
Policy for Nitrogen Oxides (NOX) Substitution.’’
August 8, 1994.
9 It should be noted that reductions toward the
RFP requirement of the CAA that actually occur
within one part of a nonattainment area do not
necessarily produce the same ozone reductions as
emissions reductions in another part of the
nonattainment area. Depending on where the
reductions occur, even if all the RFP emission
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Mandate From Subpart 1 for RFP
16. Comment: The commenter also
feels that EPA has erroneously claimed
support from Subpart 1’s mandate for
‘‘reasonable further progress,’’ defined
as ‘‘such annual incremental reductions
in emissions of the relevant air pollutant
as are required by this part or may
reasonably be required by the
Administrator for the purpose of
ensuring attainment of the applicable
national ambient air quality standard by
the applicable date.’’ Section 171(1).
The agency has asserted that this
Subpart 1 provision somehow shows
that Congress did not care about the
location of emission reductions as long
as they contributed to progress toward
attainment. 70 FR 71648, quoting CAA
section 171(1). This argument simply
ignores the express language of Subpart
2, which explicitly requires the
achievement of specified percentage
reductions ‘‘in’’ the nonattainment area.
EPA cannot rely on a general statutory
provision to override a more specific
one, or rely on policy goals to override
express statutory mandates.
EPA Response: The EPA believes that
its interpretation advances the general
statutory purpose underlying RFP. For
both Subparts 1 and 2,10 Congress
defined RFP to mean ‘‘such annual
incremental reductions in emissions of
the relevant pollutant as are required by
this part or may reasonably be required
by (EPA) for the purpose of ensuring
attainment * * * by the applicable
date.’’ CAA section 171(1). Under both
Sections 172 and 182, the stated
purpose of ‘reasonable further progress’
is to ensure attainment by the applicable
attainment date. Acknowledging this
stated purpose, EPA reasoned that
‘‘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’ * * * as are
required * * * for the purpose of
ensuring attainment * * *.’’ 70 FR
71,648/2. Therefore, while it is true that
the statute does not expressly authorize
RFP credit for outside emission
reductions, EPA believes its
interpretation of the statute to allow
such credit in the absence of an express
prohibition is reasonable. The
commenter is incorrect in stating that
this construction relies on a general
reductions occur wholly within the nonattainment
area, it is possible that there could actually be no
reduction in ozone concentrations within that
nonattainment area.
10 See 42 U.S.C. 7501 (stating that the ensuing
definitions apply ‘‘(f)or the purpose of this part’’).
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statutory provision to override a more
specific one. Although the RFP
requirements in Subpart 2 are more
specific than those in Subpart 1, they do
not expressly and unambiguously limit
the crediting of reductions in the
manner the commenter suggests.
Because no provision speaks precisely
to the relevant issue, EPA appropriately
considered the RFP and creditability
provisions (CAA section 182 (b)(1)(c)) as
a whole to reach a reasonable reading of
the statute.
IV. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
This action is not a ‘‘significant
regulatory action’’ under the terms of
Executive Order (EO) 12866 (58 FR
51735, October 4, 1993) and is therefore
not subject to review under the
Executive Order.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden.
However, the Office of Management and
Budget (OMB) has previously approved
the information collection requirements
contained in the existing regulations of
the Phase 2 Rule published on
November 29, 2005 under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. and has
assigned OMB control number 2060–
0594. The Phase 2 Rule’s information
collection request (ICR) covered the RFP
interpretation that is the subject of this
final rule. The OMB control numbers for
EPA’s regulations in 40 CFR are listed
in 40 CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an Agency to prepare
a regulatory flexibility analysis of any
regulation subject to notice and
comment rulemaking requirements
under the Administrative Procedures
Act or any other statute unless the
Agency certifies the rule will not have
a significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small organizations, and small
governmental jurisdictions.
For purposes of assessing the impacts
of this final rule on small entities, small
entity is defined as: (1) A small business
that is a small industrial entity as
defined in the U.S. Small Business
Administration (SBA) size standards.
(See 13 CFR 121.); (2) A governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
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40081
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
impact of this rule on small entities, I
certify that this action will not have a
significant economic impact on a
substantial number of small entities.
This rule will not directly impose any
requirements on small entities. Rather
this final rule interprets the RFP
requirements under the SIP for states to
submit RFP plans in order to attain the
ozone NAAQS.
D. Unfunded Mandates Reform Act
This action contains no federal
mandate under the provisions of Title II
of the Unfunded Mandates Reform Act
of 1995 (UMRA), 2 U.S.C. 1531–1538 for
state, local, or tribal governments or the
private sector. This action imposes no
enforceable duty on any state, local, and
tribal governments or the private sector.
Therefore, this action is not subject to
the requirements of section 202 and 205
of the UMRA.
This action is also not subject to the
requirements of section 203 of UMRA
because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. The
CAA imposes the obligation for states to
submit SIPs, including RFP, to
implement the Ozone NAAQS. In this
final rule, EPA is merely providing an
interpretation of those requirements.
However, even if this interpretation did
establish an independent requirement
for states to submit SIPs, it is
questionable whether such a
requirement would constitute a federal
mandate in any case. The obligation for
a state to submit a SIP that arises out of
section 110 and section 172 (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 21(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 21(5)(a)(i)(I) of
UMRA (2 U.S.C. 658(5)(a)(i)(I)).
The EPA has determined that this rule
contains merely an interpretation of
regulatory requirements and no
regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments because these regulations
affect federal agencies only.
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Federal Register / Vol. 74, No. 153 / Tuesday, August 11, 2009 / Rules and Regulations
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’’ are 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 final action does not have
federalism implications. It will not have
substantial direct effects on the states,
on the relationship between the national
government and the states, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. This rule
addresses the Court’s vacatur and
remand of a portion of the Phase 2
implementation rule for the 8-hour
standard, namely an interpretation that
allowed credit toward RFP for the 8hour standard from emission reductions
outside the nonattainment area. In
addressing the vacatur and remand, this
rule merely explains the requirements
for RFP and does not impose any
additional requirements. Thus,
Executive Order 13132 does not apply
to this rule.
In the spirit of Executive Order 13121
and consistent with EPA policy to
promote communications between EPA
and state and local governments, EPA
specifically solicited comments on the
proposed rule from state and local
officials.
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This final rule does not have tribal
implications as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). It does not have a substantial
direct effect on one or more Indian
tribes, since no tribe has to develop a
SIP under this final rule. Furthermore,
this final rule does not affect the
relationship or distribution of power
and responsibilities between the federal
government and Indian tribes. The CAA
and the Tribal Air Rule establish the
relationship of the federal government
and Tribes in developing plans to attain
the NAAQS, and these revisions to the
regulations do nothing to modify that
relationship. Thus, Executive Order
13175 does not apply to this action.
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G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
This final action is not subject to
Executive Order 13045 because it is not
economically significant as defined in
Executive Order 12866 and because EPA
does not have reason to believe the
environmental health or safety risk
addressed by the 8-hour ozone RFP
Regulations present a disproportionate
risk to children. This final action
addresses whether a SIP will adequately
and timely achieve reasonable further
progress to attain and maintain the
NAAQS and meet the obligations of the
CAA. The NAAQS are promulgated to
protect the health and welfare of
sensitive population, including
children. However, EPA solicited
comments on whether this action would
result in an adverse environmental
effect that would have a
disproportionate effect on children.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211 (66 FR 28355 (May 22,
2001)), because it is not a significant
regulatory action under Executive Order
12866.
I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus standards
bodies. NTTAA directs EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards.
This action does not involved
technical standards. Therefore, EPA did
not consider the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order (EO) 12898 (59 FR
7629, February 16, 1994) establishes
federal executive policy on
environmental justice. Its main
provision directs federal agencies, to the
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greatest extent practicable and
permitted by law, to make
environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that this final
rule will not have disproportionately
high and adverse human health or
environmental effects on minority or
low-income populations because it does
not affect the level of protection
provided to human health or the
environment. This final action will
address the Court’s vacatur and remand
of a portion of the Phase 2
implementation rule for the 8-hour
standard, namely an interpretation that
allowed credit toward RFP for the 8hour standard from emission reductions
outside the nonattainment area. This
final action merely explains the
requirements for RFP and does not
impose any additional requirements.
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. 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 October 13, 2009.
L. Determination Under Section 307(d)
Under section 307(b)(1) of the Act,
judicial review of today’s final action is
available by filing of a petition for
review in the U.S. Court of Appeals for
the District of Columbia Circuit by
October 13, 2009. Any such judicial
review is limited to only those
objections that are raised with
reasonable specificity in timely
comments. Under section 307(b)(2) of
the Act, the requirements of this final
action may not be challenged later in
civil or criminal proceedings brought by
us to enforce these requirements.
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Federal Register / Vol. 74, No. 153 / Tuesday, August 11, 2009 / Rules and Regulations
List of Subjects
40 CFR Part 50
Environmental protection, Air
pollution control, Carbon monoxide,
Lead, Nitrogen dioxide, Ozone,
Particulate matter, Sulfur oxides.
40 CFR Part 51
Air pollution control,
Intergovernmental relations, Ozone,
Particulate matter, Transportation,
Volatile organic compounds.
Authority: 42 U.S.C. 7409; 42 U.S.C. 7410;
42 U.S.C. 7511–7511f; 42 U.S.C. 7601(a)(1).
Dated: August 4, 2009.
Lisa P. Jackson,
Administrator.
[FR Doc. E9–19190 Filed 8–10–09; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R03–OAR–2009–0311; FRL–8941–6]
Approval and Promulgation of Air
Quality Implementation Plans;
Pennsylvania; Revised Motor Vehicle
Emission Budgets for the Scranton/
Wilkes-Barre 8-Hour Ozone
Maintenance Area
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AGENCY: Environmental Protection
Agency (EPA).
ACTION: Direct final rule.
SUMMARY: EPA is taking direct final
action to approve a State
Implementation Plan (SIP) revision
submitted by the Commonwealth of
Pennsylvania. The revision amends the
8-hour ozone maintenance plan for the
Scranton/Wilkes-Barre Area 8-Hour
Ozone Maintenance Area (the Area).
This revision amends the maintenance
plan’s 2009 and 2018 motor vehicle
emissions budgets (MVEBs) by
unequally dividing the existing
approved MVEBs which covers the
entire maintenance area into three subregional MVEBs, one set of MVEBs for
each county comprising the area. The
revised plan continues to demonstrate
maintenance of the 8-hour national
ambient air quality standard (NAAQS)
for ozone. EPA is approving this SIP
revision to the Pennsylvania
maintenance plan for the Scranton/
Wilkes-Barre Area in accordance with
the requirements of the Clean Air Act
(CAA).
DATES: This rule is effective on October
13, 2009 without further notice, unless
EPA receives adverse written comment
by September 10, 2009. If EPA receives
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16:58 Aug 10, 2009
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such comments, it will publish a timely
withdrawal of the direct final rule in the
Federal Register and inform the public
that the rule will not take effect.
ADDRESSES: Submit your comments,
identified by Docket ID Number EPA–
R03–OAR–2009–0311 by one of the
following methods:
A. www.regulations.gov. Follow the
on-line instructions for submitting
comments.
B. E-mail: febbo.carol@epa.gov.
C. Mail: EPA–R03–OAR–2009–0311,
Carol Febbo, Chief, Energy, Radiation
and Indoor Environment Branch,
Mailcode 3AP23, U.S. Environmental
Protection Agency, Region III, 1650
Arch Street, Philadelphia, Pennsylvania
19103.
D. Hand Delivery: At the previously
listed EPA Region III address. Such
deliveries are only accepted during the
Docket’s normal hours of operation, and
special arrangements should be made
for deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–R03–OAR–2009–
0311. EPA’s policy is that all comments
received will be included in the public
docket without change, and may be
made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or e-mail. The www.regulations.gov Web
site is an anonymous access system,
which means EPA will not know your
identity or contact information unless
you provide it in the body of your
comment. If you send an e-mail
comment directly to EPA without going
through www.regulations.gov, your email address will be automatically
captured and included as part of the
comment that is placed in the public
docket and made available on the
Internet. If you submit an electronic
comment, EPA recommends that you
include your name and other contact
information in the body of your
comment and with any disk or CD–ROM
you submit. If EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should avoid
the use of special characters, any form
of encryption, and be free of any defects
or viruses.
Docket: All documents in the
electronic docket are listed in the
www.regulations.gov index. Although
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40083
listed in the index, some information is
not publicly available, i.e., CBI 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 www.regulations.gov or
in hard copy during normal business
hours at the Air Protection Division,
U.S. Environmental Protection Agency,
Region III, 1650 Arch Street,
Philadelphia, Pennsylvania 19103.
Copies of the State submittal are
available at the Pennsylvania
Department of Environmental
Protection, Bureau of Air Quality, P.O.
Box 8468, 400 Market Street, Harrisburg,
Pennsylvania.
FOR FURTHER INFORMATION CONTACT:
Martin Kotsch, (215) 814–3335, or by
e-mail at kotsch.martin@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document whenever
‘‘we’’, ‘‘us’’, or ‘‘our’’ is used, we mean
EPA.
Table of Contents
I. Background
II. Summary of Pennsylvania’s SIP Revision
and EPA’s Review
III. Final Action
IV. Statutory and Executive Order Reviews
I. Background
On November 11, 2007 (72 FR 64948)
EPA redesignated the Scranton/WilkesBarre area of Pennsylvania to attainment
for the 8-hour ozone NAAQS. For this
area, the redesignation included
approval of an 8-hour ozone
maintenance plan, which identifies onroad MVEBs for Volatile Organic
Compounds (VOCs) and Nitrous Oxides
(NOX), which are ozone precursors,
which are then used for transportation
planning and conformity purposes.
There are three separate metropolitan
planning organizations (MPOs) in this
maintenance area—one for Lackawana
and Luzerne Counties, one for Monroe
County and one for Wyoming County,
with individual responsibility for doing
transportation conformity within their
respective planning boundaries within
the Area. Pennsylvania has unequally
divided the existing MVEBs and created
sub-regional MVEBs for each MPO to
better accommodate the transportation
planning and conformity processes
within the Area.
II. Summary of Pennsylvania’s SIP
Revision and EPA’s Review
On April 21, 2008, the State of
Pennsylvania submitted to EPA a formal
revision to its State Implementation
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Agencies
[Federal Register Volume 74, Number 153 (Tuesday, August 11, 2009)]
[Rules and Regulations]
[Pages 40074-40083]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-19190]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 50 and 51
[EPA-HQ-OAR-2008-0419, FRL-8943-3]
RIN 2060-AP96
Implementation of the 1997 8-Hour Ozone National Ambient Air
Quality Standard: Addressing a Portion of the Phase 2 Ozone
Implementation Rule Concerning Reasonable Further Progress Emissions
Reductions Credits Outside Ozone Nonattainment Areas
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is taking final action to revise a portion of its Phase 2
implementation rule for the 8-hour ozone National Ambient Air Quality
Standard (NAAQS or standard) for which the Agency had sought a
voluntary remand from the U.S. Circuit Court of Appeals for the
District of Columbia Circuit. The Court granted EPA's request by
remanding and vacating that portion of the rule. Specifically, this
rule addresses an interpretation that allowed certain credits toward
reasonable further progress (RFP) for the 8-hour standard from
emissions reductions outside the nonattainment area.
DATES: This rule is effective on October 13, 2009.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-HQ-OAR-2008-0419. All documents in the docket are
listed in https://www.regulations.gov. Although listed in the index,
some information is not publicly available, i.e., Confidential Business
Information (CBI) 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 https://www.regulations.gov or in hard copy at the Air
and Radiation Docket and Information Center in the EPA Headquarters
Library, Room Number 3334 in the EPA West Building, located at 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.
FOR FURTHER INFORMATION CONTACT: For further information on the this
final rule contact: Ms. Denise Gerth, Office of Air Quality Planning
and Standards, (C539-01), U.S. EPA, Research Triangle Park, North
Carolina 27711, telephone number (919) 541-5550 or by e-mail at
gerth.denise@epa.gov, fax number (919) 541-0824; or Mr. John Silvasi,
Office of Air Quality Planning and Standards, U.S. Environmental
Protection Agency, (C539-01), Research Triangle Park, NC 27711,
telephone number (919) 541-5666, fax number (919) 541-0824 or by e-mail
at silvasi.john@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
Entities potentially affected directly by this action include
state, local, and tribal governments. Entities potentially affected
indirectly by this rule include owners and operators of sources of
emissions [volatile organic compounds (VOCs) and nitrogen oxides
(NOx)] that contribute to ground-level ozone concentrations.
B. Where Can I Get a Copy of This Document and Other Related
Information?
A copy of this document and other related information is available
from the docket EPA-HQ-OAR-2008-0419.
C. How Is This Notice Organized?
The information presented in this notice is organized as follows:
I. General Information
A. Does This Action Apply to Me?
B. Where Can I Get a Copy of This Document and Other Related
Information?
C. How Is This Notice Organized?
II. What is the Background for This Rule?
A. Proposed Regulatory Interpretation of the Phase 2 Rule To
Address RFP Emission Credits Outside Ozone Nonattainment Areas
III. This Action
A. Background
B. Final Rule
C. Comments and Responses
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act (RFA)
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
L. Determination Under Section 307(d)
II. What Is the Background for This Rule?
A. Proposed Regulatory Interpretation of the Phase 2 Rule To Address
RFP Emission Credits Outside Ozone Nonattainment Areas
On July 21, 2008 (73 FR 42294), EPA published a proposed rule to
revise its regulatory interpretation of the Phase 2 implementation rule
for the 8-hour ozone NAAQS to address the U.S. Circuit Court of Appeals
for the District of Columbia Circuit's vacatur and remand of that
portion of the interpretation of the Phase 2 implementation rule for
which EPA had asked for a voluntary remand. The proposal addressed a
provision that allowed credit toward RFP for the 8-hour NAAQS from
emission reductions outside the nonattainment area. Readers should
refer to the proposed rule for additional background on this action,
including the final Phase 2 ozone implementation rule and the Court's
vacatur and remand of the provision allowing credit for emissions
reductions outside a nonattainment area for the purposes of RFP for the
8-hour NAAQS.
III. This Action
A. Background
In the Phase 2 Rule to implement the 8-hour ozone NAAQS, EPA set
forth an interpretation that stated that credits could be taken for
emissions reductions from a source outside the nonattainment
[[Page 40075]]
area provided that emissions from these sources were included in the
baseline for calculating the percent reduction needed. 70 FR 71612.
However, emissions from other sources outside the nonattainment area
did not have to be included in the baseline if they did not provide RFP
credit for the nonattainment area. The regulatory interpretation stated
that certain additional conditions must be met for such reductions to
qualify for credit, including that credit could be taken for VOCs and
NOX emissions reductions within 100 kilometers (km) and 200
km respectively, and there must be a demonstration that the emissions
from outside the nonattainment area had an impact on air quality levels
within the nonattainment area.
The Natural Resources Defense Council (NRDC) filed a petition for
review of the Phase 2 Rule including the implementation of the
statutory provisions regarding RFP. After briefing had concluded in
this case, EPA published its final rule implementing the NAAQS for fine
particulate matter (the ``PM2.5 Implementation Rule'') 72 FR
20586 (April 25, 2007). Because the PM2.5 Implementation
Rule significantly modified the interpretation regarding credits for
emissions outside the nonattainment area, EPA requested a voluntary
remand from the Court on July 17, 2007, to consider whether to revise
the Phase 2 implementation rule to be consistent with the provisions in
the PM2.5 rule. In response, the U.S. Court of Appeals for
the District of Columbia Circuit vacated and remanded that portion of
the Phase 2 Rule which provided credit under the 8-hour ozone RFP
requirement for VOCs and NOX emission reductions from
outside a nonattainment area. EPA proposed to revise its regulatory
interpretation of the RFP provisions in the Phase 2 Rule to be
consistent with its regulatory interpretation of the RFP provisions in
the PM2.5 Implementation Rule. 73 FR 42294 (July 21, 2008).
EPA received seven comments on this proposed rule. A few commenters
supported the proposal while others opposed the action we proposed. The
commenters addressed the following topics: requested clarification on
how the rule affects general conformity and whether the transportation
conformity determinations are only required within the nonattainment
areas; stated that nonattainment areas should be expanded to include
areas that contribute to nonattainment as required under section 107(d)
of the Clean Air Act (CAA) rather than allowing areas to take credit
outside of their nonattainment for RFP reductions; requested assurance
that the rules do not allow substitution of NOX to meet the
15 percent VOC reduction requirement; stated that the rule lacks
mechanisms for addressing overwhelming transport in State
Implementation Plan (SIP) requirements; stated that the proposed rule
flouts the language and purpose of the CAA and is arbitrary and that
EPA fails to offer a lawful or rational justification for the proposal,
etc. Detailed responses to these comments are in section C under
Comments and Responses.
B. Final Rule
Following its stated objective in the request for a voluntary
remand, EPA re-evaluted its interpretation of the RFP provision and is
taking final action to revise the earlier interpretation as proposed on
July 21, 2008 (73 FR 42294) which is consistent with the provisions in
the PM2.5 Implementation Rule (72 FR 20636). Consequently if
the state justifies consideration of precursor emissions for an area
outside the nonattainment area, EPA will expect state RFP assessments
to reflect emissions changes from all sources in this area. The state
must include all sources, not just some selected sources, for the area
providing emission reductions in the calculation of either (a) the RFP
baseline from which to calculate the percent reduction needed for RFP
or (b) the reductions obtained that would be credited toward the RFP
requirement and the analysis of whether the reductions from areas
outside the nonattainment area would contribute to decreases in ozone
levels in the nonattainment area. Also, the justification for
considering emissions outside the nonattainment area will include
justification of the state's selection of the area used in the RFP plan
for each pollutant. As is the case with the PM2.5 rule, if a
state justifies consideration of precursor emissions for an area
outside the nonattainment area, EPA expects state RFP assessments to
reflect emissions changes from all sources in the area. The state
cannot include only selected sources providing emission reductions in
the analysis. The inventories for 2002, 2009, 2012 (where applicable)
and the attainment year would all reflect the same source domain, i.e.,
the same set of sources except for the addition of any known new
sources or removal of known, permanently shut down sources.
In cases where the state justifies consideration of emissions of
one or both of the ozone precursors (i.e.,VOC and NOX) from
outside the nonattainment area, states must provide separate
information regarding on-road mobile source emissions within the
nonattainment area for transportation conformity purposes.\1\ However,
this final rule does not change existing statutory requirements that
transportation conformity determinations are only required within the
nonattainment area boundary. The CAA section 176(c)(5) and EPA's
transportation conformity regulations (40 CFR 93.102(b)) only require
conformity determinations in nonattainment and maintenance areas, and
these requirements rely on SIP on-road motor vehicle emission budgets
that address on-road emissions within the boundary of the designated
nonattainment area. For this reason and consistent with the
PM2.5 Implementation Rule (72 FR 20636), if the state
addresses emissions outside the nonattainment area for an ozone
precursor, the on-road mobile source component of the RFP inventory
will not satisfy the requirements for establishing a SIP budget for
transportation conformity purposes. In such a case, the state must
supplement the RFP inventory with an inventory of on-road mobile source
emissions to be used to establish a motor vehicle emissions budget for
transportation conformity purposes. This inventory must: (1) Address
on-road motor vehicle emissions that occur only within the designated
nonattainment area, (2) provide for the same milestone year or years as
the RFP demonstration, and (3) satisfy other applicable requirements of
the transportation conformity regulations (40 CFR part 93). As long as
the state provides this separate emissions budget and conformity is
determined to that budget, EPA believes that this approach will
optimally address both the RFP and the transportation conformity
provisions of the CAA.
---------------------------------------------------------------------------
\1\ Transportation conformity is required under CAA section
176(c) to ensure that federally supported transportation plans,
programs, and highway and transit projects are consistent with the
purpose of the SIP.
---------------------------------------------------------------------------
In addition, we interpret this final rule to restrict the use of
emission reductions for RFP credit to areas within the state, except in
the case of multi-state nonattainment areas, and only then would allow
RFP reductions from outside the state to be credited from outside the
nonattainment area if the states involved develop and submit a
coordinated RFP plan. EPA expects states with multi-state nonattainment
areas to consult with other involved states, to formulate a list of the
measures that they will adopt and the measures
[[Page 40076]]
that the other state(s) will adopt, and then to adopt their list of
measures under the assumption that the other state(s) will adopt their
listed measures. Each state would be responsible for adopting and
thereby providing for enforcement of its list of measures, and then
that state and ultimately EPA (at such time as the plan is approved)
would be responsible for assuring compliance with the SIP requirements
which is an approach consistent with the approach for RFP in the
PM2.5 Implementation rule. (72 FR 20640).
C. Comments and Responses
Comments Supporting EPA's Approach
1. Comment: One commenter noted that, in the Phase 2 Ozone
Implementation Rule (70 FR 71648, November 29, 2005), EPA stated that
modeling analyses relating to the NOX SIP call demonstrate
that significant contribution to nonattainment results not only from
source emissions within a nonattainment area but also from source
emissions over a much broader area. The commenter agrees that allowing
states to take credit for reductions from sources outside of their
nonattainment areas may help reduce ozone levels in the nonattainment
area and believes that reductions from outside the nonattainment area
are sometimes necessary to attain the standard.
EPA Response: The EPA agrees with commenter. The preamble to the
final Phase 2 rule explains that the rationale for allowing emission
reduction credits from outside the nonattainment area for RFP purposes
is based on modeling analyses that showed that emissions from outside
the nonattainment area could affect the nonattainment area and that
emission reductions from upwind of a nonattainment area will help the
nonattainment area achieve progress toward attainment. 70 FR 71648; 61
FR 65758 (December 13, 1996), and Memorandum of December 29, 1997 from
Richard D. Wilson to Regional Administrators, Regions I-X entitled:
``Guidance for Implementing the 1-Hour Ozone and Pre-Existing
PM10 NAAQS'' (the 1997 Policy) located at URL: https://www.epa.gov/ttn/oarpg/t1/memoranda/iig.pdf.
2. Comment: One commenter supports the proposal to revise the
interpretation for crediting emissions reductions from outside a
nonattainment area for RFP to be analogous with the provision in the
PM2.5 Implementation Rule. Specifically, the commenter
supports the portion of the proposal that allows RFP reductions from
outside the state to be credited from outside the nonattainment area if
states develop a coordinated RFP plan as part of their SIPs.
EPA Response: The EPA agrees with commenter. The EPA by this action
makes the RFP provisions regarding credits from emission reductions
outside the nonattainment area in the context of the ozone NAAQS
consistent with the interpretation in the context of the
PM2.5 NAAQS with respect to multi-state areas.
Clarification Requested on How This Rule Affects General Conformity
3. Comment: One commenter appreciates EPA's efforts in the proposal
to clarify that a state may no longer include only selected sources
from an area outside of a nonattainment area for emissions reduction
credit in the SIP. The commenter also appreciates EPA's efforts to
address how the proposed rule affects transportation conformity. The
commenter requests that EPA provide clarity on how the proposed rule
affects general conformity requirements and determinations in the final
rule.
EPA Response: This regulatory interpretation does not affect the
requirement for federal agencies to demonstrate conformity with SIPs.
These requirements stem from section 176(c) of the CAA. Implementing
regulations published by EPA (40 CFR 93.150 -160) provide for when and
how federal agencies can make these determinations. EPA discussed
transportation conformity in the proposal only to clarify that it
applies only within nonattainment areas and to facilitate development
of appropriate budgets for use in areas that take rate of progress
(ROP) credit from outside the nonattainment area.
Nonattainment Areas Should Be Expanded To Include Contributing Sources
4. Comment: One commenter is opposed to the revision because it is
contrary to the CAA. Section 107(d)(1)(A)(i) of the CAA requires the
designation as nonattainment for ``any area that does not meet (or that
contributes to ambient air quality in a nearby area that does not meet)
the national primary or secondary ambient air quality standard for that
pollutant.'' The CAA requires that instead of allowing an area that is
contributing to the nonattainment area to be used to demonstrate RFP
goals, the designated nonattainment area must be expanded to include
that area. A commenter also feels that the proposal illegally
circumvents the statutory designation provisions by allowing states to
selectively claim credit for reductions from outside areas without
subjecting those areas to the full range of safeguards mandated by
Congress for such areas.
EPA Response: As a threshold matter, EPA is not taking any action
through this regulatory interpretation to establish procedures for
designating or not designating areas. The designations process for each
NAAQS generally provides guidance on how to determine nonattainment
areas. Under CAA section 107 (d)(1)(A) an area is designated
``nonattainment'' if it does not meet the NAAQS or is a ``nearby'' area
that contributes to ambient air quality in an area that is violating
the NAAQS.\2\
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\2\ For example, Memorandum of March 28, 2002, from John S.
Seitz, ``Boundary Guidance on Air Quality Designations for the 8-
Hour Ozone National Ambient Air Quality Standards.''
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As the Agency explained in the final preamble to the Phase 2 rule,
the CAA does not specify a distance that is ``nearby'' or a specific
level of emissions that is deemed to ``contribute to'' nonattainment
(70 FR at 71648). EPA also did not establish a hard-and-fast set of
rules to determine which areas are ``nearby'' or ``contribute to''
nonattainment. Instead, in guidance EPA listed a broad set of factors
for states and EPA to consider in determining the boundaries of each
nonattainment area. As for the comment that EPA is circumventing the
statutory designations provisions by not subjecting the outside areas
to all the requirements for nonattainment areas, EPA believes that
since these areas are not necessarily ``nearby'' for designations
purposes, it is not appropriate to subject these areas to all of the
requirements for nonattainment areas. In this rule EPA is allowing
emissions reductions outside a nonattainment area that benefits the
nonattainment area to be considered for credit in emission reductions
for ROP purposes. Whether an area is ``nearby'' for purposes of
designations is an issue that would be considered on a case-by-case
basis when the area is initially designated nonattainment.
Clarification Requested That Transportation Conformity Only Applies in
the Nonattainment Area
5. Comment: One state transportation agency requested clarification
in the final rule that transportation conformity only applies inside
the nonattainment area.
EPA Response: EPA's final rule does not change existing statutory
requirements that transportation
[[Page 40077]]
conformity determinations are only required within the nonattainment
area boundary. CAA section 176(c)(5) and section 93.102 of EPA's
transportation conformity regulations only require conformity
determinations in nonattainment and maintenance areas. These
requirements rely on SIP on-road motor vehicle emission budgets that
address on-road emissions within the boundary of the designated
nonattainment area. For this reason and consistent with EPA's
PM2.5 implementation rule (72 FR 20636), if the state
addresses emissions outside the nonattainment area for an ozone
precursor, the on-road mobile source component of the RFP inventory
will not satisfy the requirements for establishing a SIP budget for
transportation conformity purposes. In such a case, the state must
supplement the RFP inventory with an inventory of on-road mobile source
emissions to be used to establish a motor vehicle emissions budget for
transportation conformity purposes, as described in this final rule. As
long as the state provides this separate emissions budget and
conformity is determined to be within the geographic boundary of the
nonattainment area, EPA believes that this approach will optimally
address both the RFP and the transportation conformity provisions of
the CAA.
Lack of Regulatory Text
6. Comment: One commenter believes that the proposed revision
appears to provide an appropriate and reasonable degree of flexibility
to states in meeting the RFP requirements. It is, however, difficult
for the commenter to evaluate and comment on the proposal because EPA
has not provided any proposed regulatory text that clearly states the
precise provisions and limitations of the intended rule.
EPA Response: In this action we are modifying a regulatory
interpretation that the Agency adopted in the Phase 2 rule (70 FR at
71647-48). Since publication of that rule, EPA modified its approach to
RFP credits from outside the nonattainment area in its PM2.5
Implementation Rule (72 FR 20636). This action provides a regulatory
interpretation that is consistent with the approach adopted in the
PM2.5 Implementation Rule. Neither rule included regulatory
text on the specific issue of RFP credits from outside the
nonattainment area and EPA believes that it is unnecessary to include
regulatory text in this action.
Substitution of NOX To Meet 15 Percent VOC Requirement
7. Comment: The commenter assumes that EPA does not intend to
apply, and will not apply, the policy reflected in the proposal in a
way that would allow crediting of NOX emission reductions
outside the nonattainment area to meet the 15 percent VOC emission
reduction requirement in section 182(b)(1) of the CAA. Further the
commenter stated that allowing states to use NOx emission reductions--
wherever they may occur--to satisfy section 182(b)(1) would contradict
the explicit statutory provision that the 15 percent ROP reduction
requirement must be met by VOC emission reductions only. See 70 FR
71,612, 71,636/1 (November 29, 2005).
The commenter also noted that this principle is also reflected in
the December 1997 guidance memorandum that addressed taking credit
outside nonattainment areas for purposes of RFP.
EPA Response: The commenter is correct that EPA does not intend to
apply the policy interpretation in the proposed rule to allow
substitution of NOX emission reductions outside the ozone
nonattainment area to meet the 15 percent VOC requirement in section
182(b)(1). This is consistent with the ``Guidance for Implementing the
1-Hour Ozone and Pre-Existing PM10 NAAQS'' that EPA issued
on December 29, 1997 and the Phase 2 Ozone Implementation Rule that EPA
issued on November 29, 2005.
Lack of Mechanism for Addressing Overwhelming Transport
8. Comment: One commenter feels that EPA's proposed rule lacks
reasonable, equitable mechanisms for addressing overwhelming transport
in SIP requirements. This rule, as proposed, would disallow RFP credit
in the Michigan SIP for out-of-state reductions even though the local
areas' contribution to high ozone concentrations measured at monitors
in counties abutting Lake Michigan are negligible. The contributors,
large urban areas `across the lake, are in other states, and West
Michigan nonattainment areas are not part of multistate nonattainment
areas. The proposed rule does nothing to ameliorate the regulatory
burdens of ozone transport into West Michigan. Additionally, the
commenter stated that the CAA lacks adequate provisions to address
ozone transport and include a presumption that local emissions
reductions are necessary to reduce ozone levels. The commenter
recommends that amendments to the CAA be pursued.
EPA Response: The regulatory interpretation was not intended to
address the kind of situation posed by the commenter. The revised
interpretation only applies to ROP plans and does not attempt to
resolve issues of regional transport. Amendments to the CAA to address
regional transport are only within Congress' purview.
CAA Does Not Give EPA Authority To Take Credit for Emissions Reductions
Outside the Nonattainment Area nor Change the Emissions Baseline
9. Comment: One commenter believes that the proposed rule is
unlawful and arbitrary. The commenter stated that CAA sections
182(b)(1) and 182(c)(2)(B) require SIPs for ozone nonattainment areas
to provide for an initial 15 percent rate of progress cut in ozone-
forming emissions and subsequent three percent per year emission cuts
until attainment. The CAA requires these cuts to be made from emissions
``in'' each nonattainment area. Sec. 182(b)(1). The commenter believes
that allowing areas to claim credit toward these ROP requirements from
emission cuts outside the nonattainment area would not require that
outside reductions provide the same ozone reduction benefit to the
nonattainment area as would equivalent emission reductions inside the
nonattainment area. The commenter feels that the EPA is without
authority to allow states to claim ROP credit for emission reductions
occurring outside of the nonattainment area because section
182(b)(1)(A) requires each plan to provide for cuts in VOC emissions
``of at least 15 percent from baseline emissions'' (emphasis added).
The statute goes on to define ``baseline emissions'' as ``the total
amount of actual VOC or NOX emissions from all anthropogenic
sources in the area,'' with certain exclusions not relevant here. Sec.
182(b)(1)(B) (emphasis added). Thus, Congress explicitly mandated that
the required 15 percent emissions cut be achieved from a baseline
comprising emissions from sources ``in the [nonattainment] area.''
Congress did not authorize EPA to grant rate of progress credit for
emission reductions outside the nonattainment area or to redefine
``baseline emissions'' to include emissions from sources outside of the
nonattainment area, even where those outside reductions are alleged to
or do in fact ``contribute'' to ozone concentrations in the
nonattainment area. The commenter feels that EPA cannot allow states to
credit emission cuts from outside of the nonattainment area toward
meeting post-15 percent
[[Page 40078]]
progress requirements. Nor can EPA alter the baseline for the post-15
percent cuts, a baseline that is identical to the one set in the
statute for the 15 percent plans, and that is explicitly limited to
emissions from within the nonattainment area.
EPA Response: The EPA notes first that the regulatory
interpretation set forth here does not apply to the section 182(b)(1)
requirement to provide 15 percent reductions within the first six years
from a baseline year, but only to the section 182(c)(2)(B) requirement
for an average of three percent per year for subsequent three year
periods up to the attainment date. The interpretation is based on the
December 29, 1997 memorandum from Richard D. Wilson, ``Guidance for
Implementing the 1-Hour Ozone and Pre-Existing PM10 NAAQS.''
Page 7 of the attachment to that memorandum says: ``The EPA believes
that the start date of the expanded locality-based substitution credit
for ROP is changed from post-1999 ROP requirements to post-1996
requirements. EPA does not believe that it may allow credit for
substitutions to complete or revise the 15 percent ROP requirement for
VOC emission reductions in nonattainment areas through 1996. Although
the start date for application of ROP substitution reductions from
outside the nonattainment area would apply to post-1996 ROP
requirements, consistent with past Agency policy, states would be able
to bank excess earlier reduction credits (NOX or VOC) to
apply to post-1996 and later requirements.''
Secondly, EPA disagrees with the assertion in the comment that the
proposed rule is unlawful and arbitrary and that EPA is without
authority to allow RFP credit for emission reductions from outside the
nonattainment area. The CAA does not expressly prohibit credits for
emission reductions outside the area. In fact, the Fifth Circuit, which
examined the same language at issue here, found the language
``ambiguous'' reasoning:
On the one hand, the meaning of ``in the area'' could be limited
to emissions within the nonattainment area. On the other hand, the
CAA does not expressly state that emissions outside the
nonattainment area are prohibited, rather the Act only states that
emissions from sources ``in the area'' must be included. We
therefore find the CAA ambiguous on this point.
Louisiana Envtl. Action Network (``LEAN'') v. EPA, 382 F.3d 575, 585
(5th Cir. 2004).\3\ If Congress intended to disallow credits from
outside the nonattainment area, it could have expressly disallowed it
as it did for RFP credit for four other specific categories of emission
reductions, 42 U.S.C. 7511a(b)(1)(D)(i)-(iv), while otherwise allowing
credit for any reductions that ``have actually occurred after November
15, 1990,'' id. section 7511a(b)(1)(C). See also the discussion in
response to comments 15 and 16.
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\3\ Although the Fifth Circuit found application of the 1997
policy as applied to the facts in that case unsupported, it did so
for reasons that are inapposite here. First, the court was reviewing
EPA's determination that continuing reductions outside an area could
be used as contingency measures. The court found EPA had not
demonstrated that the policy had ``any rational connection with the
relevant issue of what contingency measures to apply when an
attainment deadline passes.'' Id. at 586.
Second, the court found that in the specific case under review
there was no data to support the presumption that the ``outside''
reductions selected in that case ``can affect emissions reductions
in the * * * area.'' Id. In contrast, in its regulatory
interpretation, EPA is explicitly requiring that such data be
demonstrated in all cases prior to accepting credits from outside a
nonattainment area. 70 FR at 71,647/3.
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Rule Is Unclear as to the Precise Requirements for Crediting Outside
Reductions
10. Comment: One commenter stated that the proposal is actually
unclear as to the precise requirements for crediting these outside
reductions. The Federal Register notice describes EPA's approach for
crediting outside reductions in the PM2.5 Implementation
Rule, and states that EPA is proposing to revise its earlier
interpretation with respect to ozone plans ``to be consistent with the
analogous provisions in the PM2.5 Implementation Rule.'' The
proposal does not explain whether ``consistent with'' means ``identical
to'' or whether it allows some differences from the PM2.5
approach. For purposes of these comments, the commenter will assume EPA
is proposing an identical approach to the one adopted for
PM2.5.
EPA Response: The commenter is correct in the assumption that EPA's
proposed approach follows the same approach for ozone as followed for
PM2.5.
Rule Does Not Set Meaningful Restrictions on Boundary Drawing for the
Outside Area
11. Comment: One commenter alleged that the proposal sets no
meaningful restrictions on boundary drawing for the ``outside'' area,
thereby allowing states to gerrymander them in a way that includes
sources expected to cut emissions while excluding sources that are
likely to increase their emissions. Although the proposal appears to
limit the ``outside'' to a doughnut around the nonattainment area of up
to 200 km, it allows the states to choose the slice or hole in that
surrounding doughnut to include for purposes of the RFP calculation.
Assuming EPA is proposing the same approach used in the
PM2.5 rule, the state need only show that emissions from the
area selected substantially impact ambient concentrations in the
nonattainment area. There is no stated requirement that all areas
substantially impacting the nonattainment area be included. The
proposal does not prevent states from defining whatever area they
choose--theoretically even the block on which the selected source
sits--for inclusion in the RFP inventory.
EPA Response: Under this approach, as a prerequisite to including
emission reductions from outside the nonattainment area in the RFP
assessment, a state must justify the outside area. The justification
must include a demonstration that these outside emissions have a
substantial impact on nonattainment concentrations. Because the
demonstration of such impacts likely involve differing factors and
characteristics, EPA believes a one-size fits all ``boundary drawing''
approach is not an appropriate approach in this instance. EPA will
evaluate each RFP assessment on a case-by-case basis to determine
whether a state using RFP credits from outside the nonattainment area
has included the appropriate and pertinent area for calculating the
emission reductions. In addition, if a state wants to adopt this
approach, the RFP assessment must include emissions for all sources
within the pertinent area in order to ensure that the RFP plan reflects
the actual net emissions changes that occur within that area.
12. Comment: One commenter alleged that the proposed 200 km radius
for the ``outside'' area is also wholly arbitrary. EPA offers no
rational basis, and none exists, for choosing that particular distance
and applying it to each and every nonattainment area in the nation.
There is no evidence, for example, that NOX emission
reductions 200 km outside a nonattainment area invariably provide the
same ROP benefit as the same reductions inside the nonattainment area.
EPA appears to have picked the 200 km figure out of thin air. The
arbitrariness of EPA's approach here is confirmed by contrasting it
with agency's approach in drawing nonattainment area boundaries. In the
latter situation, EPA has taken the position that determining whether
nearby sources contribute to nonattainment is too complex to be
dictated by hard and fast rules, and instead requires a multi-factor
analysis
[[Page 40079]]
tailored to each area. See EPA's Final Brief in Catawba County v. EPA,
No. 05-1064 (D.C. Cir) filed June 11, 2008.
EPA Response: The commenter's assertions are incorrect. EPA has not
picked the distances ``out of thin air.'' As described below, EPA has
had this policy, adopted after discussions and input from the
scientific community, in place for over ten years. The December 1997
policy was developed ``as a result of the modeling results relating to
the NOX SIP Call, [which] 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.'' 1997 Policy at 5-6. In addition, under the Federal
Advisory Committee Act (FACA), we formed a Subcommittee for Development
of Ozone, Particulate Matter and Regional Haze Implementation Programs
that provided recommendations and ideas to assist us in developing
implementation approaches for these programs. We have incorporated
ideas from the FACA process for a number of SIP elements, particularly
those related to transport of ozone, the process for demonstrating
attainment of the ozone standard, and requirements for ensuring
reasonable further progress. The distance of 100 km for VOC and 200 km
for NOX resulted from discussions of the FACA Subcommittee
and generally represent transport of one to two days.\4\ Further
information on the FACA process and its reports is found at the
following Web site: https://www.epa.gov/ttn/faca/. This regulatory
interpretation incorporates the same distance limitations, which must
be supported in an individual area by data ``that are shown to be
beneficial toward reducing ozone in the nonattainment area.'' \5\ In
addition, the proposed regulatory interpretation does not change the
distances for crediting emissions from outside the nonattainment area
for NOX and VOCs. EPA proposed and finalized those distances
in the rulemaking for the Phase 2 rule. The proposed regulatory
interpretation only modifies those instances where the ozone RFP
interpretations were not consistent with the PM2.5
Implementation Rule such as whether emissions from all sources should
be included in the RFP assessments for the pertinent area outside the
nonattainment area. Thus, the comments on the distances themselves are
outside the scope of this rulemaking.
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\4\ See Footnote 43 at 68 FR 32833 (June 2, 2003).
\5\ 70 FR 71647, col 3. (November 29, 2005).
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Lack of Justification for Proposal
13. Comment: The commenter states that the proposed rule is
unlawful and arbitrary in that EPA has failed to offer a lawful or
rational justification for the proposal. The commenter states that the
notice of proposed rulemaking offers no justification for allowing
credit for outside reductions, other than a desire to provide
``flexibility.'' In the past, EPA has stated other rationales for
allowing ROP credit for outside reductions, but as the agency does not
state any intent to rely on them here, they cannot support this
iteration of the proposal. If EPA wants to provide other rationales for
the proposal, it must first provide public notice and an opportunity to
comment.
EPA Response: EPA disagrees with the commenter's assertion that it
has provided no justification for its proposal to modify its regulatory
interpretation of the RFP provisions. First, in the preamble to the
Phase 2 rule, EPA explained its rationale for permitting credits for
reductions outside the nonattainment area (70 FR 71647-48). The
proposed modification of that regulatory interpretation does not change
the distances or the precursors for which such credits may be taken
provided other conditions such as reductions are not attributed to
measures otherwise mandated by the CAA are met. Second, the preamble to
the proposed regulatory interpretation explains that EPA is modifying
its approach to allowing credits for emission reductions from outside
the nonattainment area to make it consistent with the approach that the
Agency adopted in the PM2.5 Implementation Rule. In the
PM2.5 Implementation Rule, EPA received comments that
indicated that RFP inventories for areas outside the nonattainment area
could include selected sources expecting substantial emissions
reductions while excluding other sources in the area expecting emission
increases. In response to those comments, EPA modified its approach and
required that if a state justifies consideration of emissions for an
area outside the nonattainment area, the RFP assessments will be
expected to reflect emission changes from all sources in this area and
would no longer allow states to include only selected sources that
provide emission reductions. Because the rationale for the change there
is equally applicable for ozone, EPA proposed the same regulatory
interpretation for RFP assessments for ozone.
14. Comment: The commenter noted that EPA has also tried to justify
overriding the statutory language by citing section 182(c)(2)(C) which
provides for substitution of NOX emission cuts for VOC
emission cuts to meet the percentage reduction requirements in serious
and above areas, where the state shows that equivalent ozone reductions
will be achieved. EPA erroneously claimed that this provision somehow
shows intent to allow even broader exceptions, such as the one here, as
long as some ozone reductions are achieved within the nonattainment
area. In reality, section 182(c)(2)(C) contains no language at all
authorizing states to claim emission reduction credit for emission cuts
outside of the nonattainment area, nor does it redefine ``baseline
emissions'' to include emissions from outside the nonattainment area.
The provision merely defines the limited circumstances in which an area
can substitute NOX emission cuts for VOC emission cuts to
meet percentage reduction requirements. It does not allow the required
reductions to be achieved outside the nonattainment area. Moreover, a
key requirement of section 182(c)(2)(C) is that any substitution of
NOX reductions for VOC reductions will ``result in a
reduction in ozone concentrations at least equivalent'' to that which
would result from the required VOC percentage reduction (emphasis
added). EPA's proposed rule merely requires that emissions from the
``outside'' area ``contribute to'' ozone concentrations in the
nonattainment area--it does not require the ozone benefits from cutting
those outside emissions to be at least equivalent to those achievable
by reductions inside the nonattainment area (70 FR 71647).
EPA Response: The Phase 2 rule clarified the 1997 policy to respond
to concerns identified in the Office of Inspector General Report [OAR-
2003-0079-0849 AT 80 (``OIG Report'')]. The regulatory interpretation
for RFP did not allow crediting of outside emissions based solely on
distance from the nonattainment area boundary. Instead, the regulatory
interpretation stated that the distances are only a general presumption
that would need area-specific data showing that reductions from sources
in attainment areas benefit the particular nonattainment area. 70 FR
71647-49. Under this approach, as a prerequisite to including emission
reductions from outside the nonattainment area in the RFP assessment, a
state must justify the inclusion of sources outside the area. The
justification must include a demonstration that these outside emissions
have a substantial impact on nonattainment concentrations and that
[[Page 40080]]
reductions in these emissions would have a beneficial impact on the
nonattainment area.
As clarified in a response below, in evaluating RFP submittals, EPA
would consider whether the reductions from outside the nonattainment
area could reasonably be expected to yield comparable air quality
benefits as would be obtained if the same quantity of reductions were
to occur inside the nonattainment area.
15. Comment: The commenter offers as support for the previous
comment based on the fact that EPA's Office of Inspector General (OIG)
observed that EPA's policy allows credit ``for all emission reductions
achieved by outside sources within specified distances outside the
nonattainment area boundaries without any demonstration of the actual
impact of these specific emissions on the area's nonattainment * * *''
OAR-2003-0079-0849 AT 80 (``OIG Report'').
EPA Response: EPA believes that when Congress allowed the
substitution of NOX controls for VOC controls to meet the
section 182(c)(2)(C) RFP requirement, its choice of specific words is
telling because it referred to ``reductions in ozone concentrations''
in the applicable nonattainment area, rather than ``reductions in
emissions.'' 70 FR 71648. While the language in the CAA does not
explicitly state that emission reductions from outside the
nonattainment area may be credited for RFP assessments, EPA reasonably
interpreted this language as an indication that Congress' intent was to
lower ``ozone concentrations''--not just ``emissions'' of ozone
precursors--within the nonattainment area. As EPA explained, ``(i)t 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 (toward) RFP.'' 70 FR 71648.
As for the commenter's assertion that VOC and NOX
reductions should result in equivalent benefits within the area, the
fact that EPA's policy always had limits for the distance outside the
nonattainment area was intended to preclude emission reductions from
having negligible ozone benefits within the nonattainment area. While
it is implicit in EPA's proposed regulatory interpretation in its
evaluation of the appropriateness of the credit reductions, the Agency
is now clarifying in response to the commenter's statement that EPA, in
evaluating RFP submittals, would consider whether the reductions from
outside the nonattainment area could reasonably be expected to yield
comparable air quality benefits as would be obtained if the same
quantity of reductions were to occur inside the nonattainment area.
In setting forth a requirement for the ozone transport region in
section 184 of the CAA, Congress realized that controlling ozone would
require emission reductions from not just nonattainment areas, but all
areas that were shown to contribute to ozone concentrations, including
areas outside nonattainment areas. The work done under the Ozone
Transport Assessment Group (OTAG) led to the NOX SIP call,
which resulted in State-wide NOX emission budgets. The
NOX SIP call, with its significant NOX emission
reductions from attainment as well as nonattainment areas, was highly
successful in reducing ozone concentrations, and indeed provided
progress toward attainment for many of the nonattainment areas in the
eastern portion of the U.S.\6\
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\6\ ``Evaluating Ozone Control Programs in the Eastern United
States: Focus on the NOX Budget Trading Program, 2004''
United States Environmental Protection Agency; Office of Air and
Radiation; Office of Air Quality Planning and Standards; Office of
Atmospheric Programs. 1200 Pennsylvania Ave., NW., Washington, DC
20460. EPA454-K-05-001. August 2005. Found at: https://www.epa.gov/airmarkt/progress/docs/ozonenbp.pdf.
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A state's ozone attainment demonstration performed with
photochemical grid modeling will invariably take account of emission
reductions not only from within the nonattainment area, but also from
outside the nonattainment area. Generally, a state will be unable to
demonstrate attainment for many areas unless there are emission
reductions from attainment and nonattainment areas outside the area for
which the state is performing the attainment demonstration. An extreme
hypothetical example of this situation would be a nonattainment area
that is mostly rural with few emissions of its own, but which is
ineligible for rural transport area treatment and that is affected by
significant transport from upwind areas. For its attainment
demonstration, it must rely totally on emission reductions from upwind
areas and may not be able to demonstrate RFP from emission reductions
totally within the nonattainment area.
Additionally, air quality modeling to make a determination of
equivalent ozone reductions would be very difficult. Ozone reductions
from a particular strategy of emission reductions vary based on a
number of factors such as wind, climate, type of emission source,
location of sources, and height of emissions release above the ground.
Therefore, the location and spatial extent of ozone reductions may be
highly variable on a day-to-day basis. In many cases, emission
reductions from farther away from a receptor location could be more
beneficial in reducing ozone than emission reductions from a nearer
location in the nonattainment area. The fact that the NOX
SIP call regional emission reductions have been shown to reduce ozone
concentrations in almost all nonattainment areas is a testament to the
fact that regional NOX controls are beneficial in reducing
ozone. The current policy of allowing reductions for RFP purposes only
out to certain well-defined geographic distances would serve to prevent
abuse.
Section 182(c)(2)(C) does require that NOX reductions
must be shown to reduce ozone concentrations ``at least equivalent'' to
that which would result from VOC reductions. In response to the CAA's
requirement of section 182(c)(2)(C), EPA had in the early- and mid-
1990's issued guidance,7 8 for implementation of this
provision. The guidance is based on two principles: First, an
equivalency demonstration requires that cumulative RFP emission
reductions must be consistent with the NOX and VOC emission
reductions determined in the ozone attainment modeling demonstration;
in other words, a ton of NOX cannot simply substitute for a
ton of VOC since the air quality impact might be entirely different.
Second, specified reductions in NOX and VOC emissions should
be accomplished in the interim period between the time of the beginning
of the RFP period in question (at the time, that was the end of 1996)
and the attainment date, consistent with the continuous RFP emission
reduction requirement. Thus, substituting NOX emission
reductions for VOC emission reductions for RFP purposes has
consistently been done in the context of the area's attainment
demonstration in order to demonstrate equivalent ozone reductions
regardless of whether the emission reductions that are credited for RFP
purposes come wholly within the nonattainment area or where some come
from outside the nonattainment area.\9\
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\7\ NOX Substitution Guidance, December, 1993. Office
of Air Quality Planning and Standards; U.S. Environmental Protection
Agency; Research Triangle Park, North Carolina 27711.
\8\ Memorandum from John Seitz, ``Clarification of Policy for
Nitrogen Oxides (NOX) Substitution.'' August 8, 1994.
\9\ It should be noted that reductions toward the RFP
requirement of the CAA that actually occur within one part of a
nonattainment area do not necessarily produce the same ozone
reductions as emissions reductions in another part of the
nonattainment area. Depending on where the reductions occur, even if
all the RFP emission reductions occur wholly within the
nonattainment area, it is possible that there could actually be no
reduction in ozone concentrations within that nonattainment area.
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[[Page 40081]]
Mandate From Subpart 1 for RFP
16. Comment: The commenter also feels that EPA has erroneously
claimed support from Subpart 1's mandate for ``reasonable further
progress,'' defined as ``such annual incremental reductions in
emissions of the relevant air pollutant as are required by this part or
may reasonably be required by the Administrator for the purpose of
ensuring attainment of the applicable national ambient air quality
standard by the applicable date.'' Section 171(1). The agency has
asserted that this Subpart 1 provision somehow shows that Congress did
not care about the location of emission reductions as long as they
contributed to progress toward attainment. 70 FR 71648, quoting CAA
section 171(1). This argument simply ignores the express language of
Subpart 2, which explicitly requires the achievement of specified
percentage reductions ``in'' the nonattainment area. EPA cannot rely on
a general statutory provision to override a more specific one, or rely
on policy goals to override express statutory mandates.
EPA Response: The EPA believes that its interpretation advances the
general statutory purpose underlying RFP. For both Subparts 1 and
2,\10\ Congress defined RFP to mean ``such annual incremental
reductions in emissions of the relevant pollutant as are required by
this part or may reasonably be required by (EPA) for the purpose of
ensuring attainment * * * by the applicable date.'' CAA section 171(1).
Under both Sections 172 and 182, the stated purpose of `reasonable
further progress' is to ensure attainment by the applicable attainment
date. Acknowledging this stated purpose, EPA reasoned that ``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' * * * as are required * * * for the
purpose of ensuring attainment * * *.'' 70 FR 71,648/2. Therefore,
while it is true that the statute does not expressly authorize RFP
credit for outside emission reductions, EPA believes its interpretation
of the statute to allow such credit in the absence of an express
prohibition is reasonable. The commenter is incorrect in stating that
this construction relies on a general statutory provision to override a
more specific one. Although the RFP requirements in Subpart 2 are more
specific than those in Subpart 1, they do not expressly and
unambiguously limit the crediting of reductions in the manner the
commenter suggests. Because no provision speaks precisely to the
relevant issue, EPA appropriately considered the RFP and creditability
provisions (CAA section 182 (b)(1)(c)) as a whole to reach a reasonable
reading of the statute.
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\10\ See 42 U.S.C. 7501 (stating that the ensuing definitions
apply ``(f)or the purpose of this part'').
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IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
This action is not a ``significant regulatory action'' under the
terms of Executive Order (EO) 12866 (58 FR 51735, October 4, 1993) and
is therefore not subject to review under the Executive Order.
B. Paperwork Reduction Act
This action does not impose any new information collection burden.
However, the Office of Management and Budget (OMB) has previously
approved the information collection requirements contained in the
existing regulations of the Phase 2 Rule published on November 29, 2005
under the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et
seq. and has assigned OMB control number 2060-0594. The Phase 2 Rule's
information collection request (ICR) covered the RFP interpretation
that is the subject of this final rule. The OMB control numbers for
EPA's regulations in 40 CFR are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA) generally requires an Agency
to prepare a regulatory flexibility analysis of any regulation subject
to notice and comment rulemaking requirements under the Administrative
Procedures Act or any other statute unless the Agency certifies the
rule will not have a significant economic impact on a substantial
number of small entities. Small entities include small businesses,
small organizations, and small governmental jurisdictions.
For purposes of assessing the impacts of this final rule on small
entities, small entity is defined as: (1) A small business that is a
small industrial entity as defined in the U.S. Small Business
Administration (SBA) size standards. (See 13 CFR 121.); (2) A
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 impact of this rule on small
entities, I certify that this action will not have a significant
economic impact on a substantial number of small entities. This rule
will not directly impose any requirements on small entities. Rather
this final rule interprets the RFP requirements under the SIP for
states to submit RFP plans in order to attain the ozone NAAQS.
D. Unfunded Mandates Reform Act
This action contains no federal mandate under the provisions of
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), 2 U.S.C.
1531-1538 for state, local, or tribal governments or the private
sector. This action imposes no enforceable duty on any state, local,
and tribal governments or the private sector. Therefore, this action is
not subject to the requirements of section 202 and 205 of the UMRA.
This action is also not subject to the requirements of section 203
of UMRA because it contains no regulatory requirements that might
significantly or uniquely affect small governments. The CAA imposes the
obligation for states to submit SIPs, including RFP, to implement the
Ozone NAAQS. In this final rule, EPA is merely providing an
interpretation of those requirements. However, even if this
interpretation did establish an independent requirement for states to
submit SIPs, it is questionable whether such a requirement would
constitute a federal mandate in any case. The obligation for a state to
submit a SIP that arises out of section 110 and section 172 (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 21(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 21(5)(a)(i)(I) of UMRA (2 U.S.C. 658(5)(a)(i)(I)).
The EPA has determined that this rule contains merely an
interpretation of regulatory requirements and no regulatory
requirements that may significantly or uniquely affect small
governments, including tribal governments because these regulations
affect federal agencies only.
[[Page 40082]]
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'' are 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 final action does not have federalism implications. It will
not have substantial direct effects on the states, on the relationship
between the national government and the states, or on the distribution
of power and responsibilities among the various levels of government,
as specified in Executive Order 13132. This rule addresses the Court's
vacatur and remand of a portion of the Phase 2 implementation rule for
the 8-hour standard, namely an interpretation that allowed credit
toward RFP for the 8-hour standard from emission reductions outside the
nonattainment area. In addressing the vacatur and remand, this rule
merely explains the requirements for RFP and does not impose any
additional requirements. Thus, Executive Order 13132 does not apply to
this rule.
In the spirit of Executive Order 13121 and consistent with EPA
policy to promote communications between EPA and state and local
governments, EPA specifically solicited comments on the proposed rule
from state and local officials.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This final rule does not have tribal implications as specified in
Executive Order 13175 (65 FR 67249, November 9, 2000). It does not have
a substantial direct effect on one or more Indian tribes, since no
tribe has to develop a SIP under this final rule. Furthermore, this
final rule does not affect the relationship or distribution of power
and responsibilities between the federal government and Indian tribes.
The CAA and the Tribal Air Rule establish the relationship of the
federal government and Tribes in developing plans to attain the NAAQS,
and these revisions to the regulations do nothing to modify that
relationship. Thus, Executive Order 13175 does not apply to this
action.
G. Executive Order 13045: Protection of Children From Environmental
Health and Safety Risks
This final action is not subject to Executive Order 13045 because
it is not economically significant as defined in Executive Order 12866
and because EPA does not have reason to believe the environmental
health or safety risk addressed by the 8-hour ozone RFP Regulations
present a disproportionate risk to children. This final action
addresses whether a SIP will adequately and timely achieve reasonable
further progress to attain and maintain the NAAQS and meet the
obligations of the CAA. The NAAQS are promulgated to protect the health
and welfare of sensitive population, including children. However, EPA
solicited comments on whether this action would result in an adverse
environmental effect that would have a disproportionate effect on
children.
H. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution, or Use
This action is not subject to Executive Order 13211 (66 FR 28355
(May 22, 2001)), because it is not a significant regulatory action
under Executive Order 12866.
I. National Technology Transfer Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (``NTTAA''), Public Law 104-113, 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus standards in its regulatory
activities unless to do so would be inconsistent with applicable law or
otherwise impractical. Voluntary consensus standards are technical
standards (e.g., materials specifications, test methods, sampling
procedures, and business practices) that are developed or adopted by
voluntary consensus standards bodies. NTTAA directs EPA to provide
C