Transportation Conformity Rule PM2.5, 14260-14285 [2010-5703]
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 93
[EPA–HQ–OAR–2008–0540; FRL–9127–7]
RIN 2060–AP29
Transportation Conformity Rule PM2.5
and PM10 Amendments
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: In this action, EPA is
amending the transportation conformity
rule to finalize provisions that were
proposed on May 15, 2009. These
amendments primarily affect
conformity’s implementation in PM2.5
and PM10 nonattainment and
maintenance areas. EPA is updating the
transportation conformity regulation in
light of an October 17, 2006 final rule
that strengthened the 24-hour PM2.5
national ambient air quality standard
(NAAQS) and revoked the annual PM10
NAAQS. In addition, EPA is clarifying
the regulations concerning hot-spot
analyses to address a December 2007
remand from the Court of Appeals for
the District of Columbia Circuit. This
portion of the final rule applies to PM2.5
and PM10 nonattainment and
maintenance areas as well as carbon
monoxide nonattainment and
maintenance areas.
The Clean Air Act (CAA) requires
federally supported transportation
plans, transportation improvement
programs, and projects to be consistent
with (‘‘conform to’’) the purpose of the
state air quality implementation plan.
The U.S. Department of Transportation
(DOT) is EPA’s federal partner in
implementing the transportation
conformity regulation. EPA has
consulted with DOT, and they concur
with this final rule.
DATES: This final rule is effective on
April 23, 2010.
ADDRESSES: EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2008–0540. All
documents in the docket are listed on
the https://www.regulations.gov Web
site. Although listed in the index, some
information is not publicly available,
e.g., CBI or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
https://www.regulations.gov or in hard
copy at the Air and Radiation Docket,
EPA/DC, EPA West, Room 3334, 1301
Constitution Ave., NW., Washington,
DC. The Public Reading Room is open
from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744
and the telephone number for the Air
and Radiation Docket is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT:
Laura Berry, State Measures and
Conformity Group, Transportation and
Regional Programs Division,
Environmental Protection Agency, 2000
Traverwood Drive, Ann Arbor, MI
48105, e-mail address:
berry.laura@epa.gov, telephone number:
(734) 214–4858, fax number: (734) 214–
4052; or Patty Klavon, State Measures
and Conformity Group, Transportation
and Regional Programs Division,
Environmental Protection Agency, 2000
Traverwood Drive, Ann Arbor, MI
48105, e-mail address:
klavon.patty@epa.gov, telephone
number: (734) 214–4476, fax number:
(734) 214–4052.
The
contents of this preamble are listed in
the following outline:
SUPPLEMENTARY INFORMATION:
I. General Information
II. Background on the Transportation
Conformity Rule
III. General Overview of Transportation
Conformity for the 2006 PM2.5 NAAQS
IV. Baseline Year for Certain 2006 PM2.5
Nonattainment Areas
V. Regional Conformity Tests in 2006 PM2.5
Nonattainment Areas That Do Not Have
Adequate or Approved SIP Budgets for
the 1997 PM2.5 NAAQS
VI. Regional Conformity Tests in 2006 PM2.5
Areas That Have 1997 PM2.5 SIP Budgets
VII. Other Conformity Requirements for 2006
PM2.5 Areas
VIII. Transportation Conformity in PM10
Nonattainment and Maintenance Areas
and the Revocation of the Annual PM10
NAAQS
IX. Response to the December 2007 Hot-Spot
Court Decision
X. Statutory and Executive Order Reviews
I. General Information
A. Does This Action Apply to Me?
Entities potentially regulated by the
conformity rule are those that adopt,
approve, or fund transportation plans,
programs, or projects under title 23
U.S.C. or title 49 U.S.C. Regulated
categories and entities affected by
today’s action include:
Examples of regulated entities
Local government ......................................
State government ......................................
Federal government ...................................
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Category
Local transportation and air quality agencies, including metropolitan planning organizations (MPOs).
State transportation and air quality agencies.
Department of Transportation (Federal Highway Administration (FHWA) and Federal Transit Administration (FTA)).
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this final rule. This table
lists the types of entities of which EPA
is aware that potentially could be
regulated by the transportation
conformity rule. Other types of entities
not listed in the table could also be
regulated. To determine whether your
organization is regulated by this action,
you should carefully examine the
applicability requirements in 40 CFR
93.102. If you have questions regarding
the applicability of this action to a
particular entity, consult the persons
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listed in the preceding FOR FURTHER
section.
INFORMATION CONTACT
B. How Can I Get Copies of This
Document?
1. Docket
EPA has established an official public
docket for this action under Docket ID
No. EPA–HQ–OAR–2008–0540. You can
get a paper copy of this Federal Register
document, as well as the documents
specifically referenced in this action,
any public comments received, and
other information related to this action
at the official public docket. See the
ADDRESSES section for its location.
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2. Electronic Access
You may access this Federal Register
document electronically through EPA’s
Transportation Conformity Web site at
https://www.epa.gov/otaq/
stateresources/transconf/index.htm.
You may also access this document
electronically under the Federal
Register listings at https://www.epa.gov/
fedrgstr/.
An electronic version of the official
public docket is available through
https://www.regulations.gov. You may
use https://www.regulations.gov to view
public comments, access the index
listing of the contents of the official
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public docket, and access those
documents in the public docket that are
available electronically. Once in the
system, select ‘‘search,’’ then key in the
appropriate docket identification
number.
Certain types of information will not
be placed in the electronic public
docket. Information claimed as CBI and
other information for which disclosure
is restricted by statute is not available
for public viewing in the electronic
public docket. EPA’s policy is that
copyrighted material is not placed in the
electronic public docket but is available
only in printed, paper form in the
official public docket.
To the extent feasible, publicly
available docket materials will be made
available in the electronic public
docket. When a document is selected
from the index list in EPA Dockets, the
system will identify whether the
document is available for viewing in the
electronic public docket. Although not
all docket materials may be available
electronically, you may still access any
of the publicly available docket
materials through the docket facility
identified in the ADDRESSES section.
EPA intends to provide electronic
access in the future to all of the publicly
available docket materials through the
electronic public docket.
For additional information about the
electronic public docket, visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets.htm.
II. Background on the Transportation
Conformity Rule
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A. What Is Transportation Conformity?
Transportation conformity is required
under CAA section 176(c) (42 U.S.C.
7506(c)) to ensure that transportation
plans, transportation improvement
programs (TIPs) and federally supported
highway and transit project activities
are consistent with (‘‘conform to’’) the
purpose of the state air quality
implementation plan (SIP). Conformity
to the purpose of the SIP means that
transportation activities will not cause
new air quality violations, worsen
existing violations, or delay timely
attainment of the relevant national
ambient air quality standards (NAAQS)
or any interim milestones.1
Transportation conformity applies to
areas that are designated nonattainment,
and those areas redesignated to
1 These requirements are found in Clean Air Act
section 176(c)(B)(i), (ii), and (iii): ‘‘That such
activities will not cause or contribute to any new
violation of any standard in any area; increase the
frequency or severity of any existing violation of
any standard in any area; or delay timely attainment
of any standard or any required interim emissions
reductions or other milestones in any area.’’
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attainment after 1990 (‘‘maintenance
areas’’) for transportation-related criteria
pollutants: Carbon monoxide (CO),
ozone, nitrogen dioxide (NO2) and
particulate matter (PM2.5, and PM10).2
EPA’s transportation conformity rule
(40 CFR Parts 51 and 93) establishes the
criteria and procedures for determining
whether transportation activities
conform to the SIP. EPA first
promulgated the transportation
conformity rule on November 24, 1993
(58 FR 62188), and subsequently
published several other amendments.
DOT is EPA’s federal partner in
implementing the transportation
conformity regulation. EPA has
consulted with DOT, which concurs
with this final rule.
A few recent amendments to the
transportation conformity rule are
useful background for today’s final rule.
In a final rule EPA published on July 1,
2004 (69 FR 40004), EPA provided
conformity procedures for state and
local agencies under the 1997 8-hour
ozone and PM2.5 national ambient air
quality standards (NAAQS). EPA’s
nonattainment area designations for the
1997 8-hour ozone and PM2.5 NAAQS
were effective in June 2004 and April
2005, respectively. The July 2004
update provided rules for implementing
conformity for these NAAQS. In
addition, on May 6, 2005, EPA
promulgated a final rule entitled,
‘‘Transportation Conformity Rule
Amendments for the New PM2.5
National Ambient Air Quality Standard:
PM2.5 Precursors’’ (70 FR 24280). This
final rule specified transportationrelated PM2.5 precursors and when they
must be considered in transportation
conformity determinations in PM2.5
nonattainment and maintenance areas.
On March 10, 2006, EPA promulgated
a final rule (71 FR 12468) entitled,
‘‘PM2.5 and PM10 Hot-Spot Analyses in
Project-Level Transportation Conformity
Determinations for the New PM2.5 and
Existing PM10 National Ambient Air
Quality Standards.’’ This rule
established the criteria and procedures
for determining which transportation
projects must be analyzed for local air
quality impacts—or ‘‘hot-spots’’—in
PM2.5 and PM10 nonattainment and
maintenance areas. See Section IX. of
today’s preamble for more information
regarding the March 2006 rule; see
EPA’s Web site at https://www.epa.gov/
otaq/stateresources/transconf/
index.htm for further information about
2 40 CFR 93.102(b)(1) defines PM
2.5 and PM10 as
particles with an aerodynamic diameter less than or
equal to a nominal 2.5 and 10 micrometers,
respectively.
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any of EPA’s transportation conformity
rulemakings.3
B. Why Are We Issuing This Final Rule?
Today’s action is necessary because
EPA promulgated a final rule on
October 17, 2006 that changed the PM2.5
and PM10 NAAQS, as described further
below. Today’s action provides rules for
implementing conformity for these
revisions to the PM2.5 and PM10
NAAQS. Sections III. through VIII.
describe the changes to the
transportation conformity rule that are a
result of the October 2006 revisions to
the PM2.5 and PM10 NAAQS.
Today’s final rule is the second
transportation conformity rulemaking
undertaken primarily for the purpose of
addressing a new or revised NAAQS.
Due to other statutory requirements,
EPA will continue to establish new or
revised NAAQS in the future. Therefore,
EPA may consider restructuring certain
sections of the conformity rule in a
future rulemaking so that existing rule
requirements would clearly apply to
areas designated for future new or
revised NAAQS, without having to
update the rule each time a new or
revised NAAQS is established.
Note that in 2009, EPA issued an
interim conformity guidance for areas
designated nonattainment for the 2006
PM2.5 NAAQS 4 (‘‘2006 PM2.5 areas’’).5
EPA issued this interim guidance to
help new nonattainment areas meet
conformity requirements by the end of
the one-year grace period. While this
interim guidance is superseded by
today’s final rule, conformity
determinations done according to the
interim guidance are consistent with the
CAA, and with the transportation
conformity rule.6 Therefore, conformity
determinations based on the interim
guidance and the transportation
conformity rule in effect at the time of
the conformity determination will
remain valid. Conformity
determinations completed on or after
the effective date of this final rule must
meet all the requirements in the final
rule. EPA will work with the 2006 PM2.5
3 At this website, click on ‘‘Regulations’’ to find
all of EPA’s proposed and final rules as well as the
current transportation conformity regulations.
4 ‘‘2006 PM
2.5 NAAQS’’ refers to the 24-hour PM2.5
NAAQS promulgated in 2006.
5 ‘‘Interim Transportation Conformity Guidance
for 2006 PM2.5 Nonattainment Areas,’’ EPA–420–B–
09–036, November 2009, available on EPA’s Web
site at: https://www.epa.gov/otaq/stateresources/
transconf/policy/420b09036.pdf.
6 Today’s final rule changes the baseline year
used to demonstrate conformity for the 2006 PM2.5
NAAQS prior to having an adequate or approved
PM2.5 SIP budget; the interim guidance addressed
this change. Refer to Section IV. for further
discussion of the baseline year for conformity
purposes.
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areas to ensure they can meet
conformity requirements on time.
Today’s final rule also responds to a
court decision regarding the March 2006
hot-spot rulemaking. Section IX. of this
preamble describes the issue, the court’s
decision, and EPA’s response.
III. General Overview of
Transportation Conformity for the 2006
PM2.5 NAAQS
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A. Background on 2006 PM2.5 NAAQS
Development
EPA issued a final rule on October 17,
2006, effective December 18, 2006, that
strengthened the 24-hour PM2.5 NAAQS
and revoked the annual PM10 NAAQS
(71 FR 61144). In that final rule, EPA
strengthened the 24-hour PM2.5 NAAQS
from the 1997 level of 65 micrograms
per cubic meter (μg/m3) (average of 98th
percentile values for three consecutive
years) to 35 μg/m3, while the level of the
annual PM2.5 NAAQS remained
unchanged at 15.0 μg/m3 (average of
three consecutive annual average
values). EPA selected levels for the final
NAAQS after completing an extensive
review of thousands of scientific studies
on the impact of fine and coarse
particles on public health and welfare.
For additional information about the
October 17, 2006 rulemaking, the final
rule and EPA outreach materials can be
found at: https://www.epa.gov/
pmdesignations/.
The October 2006 rule establishing
the 2006 PM2.5 NAAQS did not revoke
the 1997 annual or 24-hour PM2.5
NAAQS. See Section III.D. below for
details on how today’s final rule
interacts with conformity requirements
for those areas designated
nonattainment for the 1997 PM2.5
NAAQS.7
EPA signed the final rule designating
areas for the 2006 PM2.5 NAAQS on
October 8, 2009.8 This final rule was
7 ‘‘1997 PM
2.5 NAAQS’’ includes both the annual
and the 24-hour 1997 PM2.5 NAAQS unless noted
otherwise.
8 A Federal Register notice designating areas for
the 2006 PM2.5 NAAQS had been signed in late
December 2008 by then-Administrator Johnson,
where the designations were based on air quality
data from 2005–2007. The December 2008 notice
was awaiting publication in January 2009 when the
newly elected Administration identified the notice
as one that should receive additional review before
publication. However, this notice was never
published in the Federal Register and, therefore,
designations were not officially promulgated. CAA
section 107(d)(2)(A) requires EPA to publish the
notice in the Federal Register in order to
promulgate designations. Since January 2009,
monitoring data for 2008 has become available for
areas across the U.S. Therefore, the final
designations in the final rule signed by
Administrator Jackson on October 8, 2009 are based
on air quality monitoring data from Federal
Reference Method monitors for calendar years
2006–2008.
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published in the Federal Register on
November 13, 2009, and became
effective December 14, 2009. The
designations for the 2006 PM2.5 NAAQS
are separate from the existing
designations for the 1997 PM2.5 NAAQS.
However, in the final rule designating
areas for the 2006 PM2.5 NAAQS, EPA
has also clarified that all 39 areas
designated nonattainment for the 1997
PM2.5 NAAQS were violating the annual
PM2.5 NAAQS, and two of those were
also violating the 24-hour PM2.5
NAAQS.9 That is, EPA’s designations
rule clarifies that only two areas were
designated nonattainment for the 1997
24-hour PM2.5 NAAQS, and that all 39
nonattainment areas were designated
nonattainment for the 1997 annual
PM2.5 NAAQS.
Transportation conformity applies for
the NAAQS for which an area is
designated nonattainment.10 Therefore,
in two of the 1997 PM2.5 areas,
conformity applies for both the 1997
annual and 24-hour NAAQS. In the
other 37 1997 PM2.5 areas, conformity
applies for the 1997 annual NAAQS,
and not the 1997 24-hour PM2.5 NAAQS.
Refer to EPA’s Web site at: https://
www.epa.gov/pmdesignations/
2006standards/index.htm for additional
information about the nonattainment
designations.
B. When Does Conformity Apply for the
2006 PM2.5 NAAQS?
Transportation conformity for the
2006 PM2.5 NAAQS does not apply until
December 14, 2010, which is one year
after the effective date of nonattainment
designations for this NAAQS. CAA
section 176(c)(6) and 40 CFR 93.102(d)
provide a one-year grace period from the
effective date of designations before
transportation conformity applies in
areas newly designated nonattainment
for a particular NAAQS.11
The following discussion provides
more details on the application of the
one-year grace period in different types
of newly designated nonattainment
areas for the 2006 PM2.5 NAAQS. This
information is consistent with how
9 The two areas designated as nonattainment for
both the annual and 24-hour 1997 PM2.5 NAAQS
are the Los Angeles-South Coast Air Basin, CA
nonattainment area and the San Joaquin Valley, CA
nonattainment area.
10 Clean Air Act section 176(c)(5) and 40 CFR
93.102(b).
11 EPA began the process of notifying state and
local agencies, via the EPA regional offices, of the
timing of conformity under the 2006 PM2.5 NAAQS
in its April 16, 2007 memorandum entitled,
‘‘Transportation Conformity and the Revised 24hour PM2.5 Standard,’’ from Merrylin Zaw-Mon,
Director, Transportation and Regional Programs
Division, EPA Office of Transportation and Air
Quality, to EPA Regional Air Directors, Regions
I–X.
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conformity for new NAAQS has been
implemented in the past.12 The
conformity grace period will be
available to all newly designated
nonattainment areas for the 2006 PM2.5
NAAQS.
Metropolitan areas are urbanized
areas that have a population greater than
50,000 and a designated metropolitan
planning organization (MPO)
responsible for transportation planning
per 23 U.S.C. 134. Within one year after
the effective date of the initial
nonattainment designation for the 2006
PM2.5 NAAQS, a conformity
determination for this NAAQS must be
made by the MPO and DOT for the
MPO’s transportation plan and TIP.
MPOs must continue to meet conformity
requirements for any other applicable
NAAQS, including the 1997 PM2.5
NAAQS, if the area is designated
nonattainment or maintenance for such
NAAQS as well.
In nonattainment and maintenance
areas with a donut portion,13 adjacent
MPOs must meet conformity
requirements for the 2006 PM2.5
NAAQS. The MPO must also continue
to ensure that conformity is met for any
other applicable NAAQS, including any
1997 PM2.5 NAAQS for which the donut
area is designated nonattainment.14 The
interagency consultation partners for
each newly designated nonattainment
area that includes a donut portion
should determine how best to consider
the donut area transportation system
and new donut area projects in the
MPO’s regional emissions analyses and
transportation plan and TIP conformity
determinations.
If, at the end of the one-year grace
period, the MPO and DOT have not
made a transportation plan and TIP
conformity determination for the 2006
PM2.5 NAAQS, the entire area, including
any donut area, would be in a
conformity ‘‘lapse.’’ 15 During a
12 See EPA’s July 1, 2004 final rule for further
background on how EPA has implemented this
conformity grace period for the 1997 PM2.5 NAAQS
(69 FR 40004).
13 For the purposes of transportation conformity,
a ‘‘donut’’ area is the geographic area outside a
metropolitan planning area boundary, but inside a
designated nonattainment or maintenance area
boundary that includes an MPO (40 CFR 93.101).
For more discussion on how conformity
determinations should be made for donut areas, see
the preamble to the July 1, 2004 conformity rule
(69 FR 40013).
14 Determining conformity for these other NAAQS
during the one-year grace period is not necessary
unless required by 40 CFR 93.104 (for example, a
new or amended transportation plan and TIP are to
be adopted).
15 The lapse grace period provision in CAA
section 176(c)(9) does not apply to the deadline for
newly designated nonattainment areas to make the
initial transportation plan/TIP conformity
determination within 12 months of the effective
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conformity lapse, only certain projects
can receive additional federal funding
or approvals to proceed (e.g. exempt
projects, project phases that were
approved before the lapse).16 The
practical impact of a conformity lapse
will vary on an area-by-area basis.
The one-year grace period for
conformity also applies to project-level
conformity determinations (including
hot-spot analyses in certain cases) in
newly designated 2006 PM2.5
nonattainment areas. At the end of the
one-year grace period for conformity,
requirements for project-level
conformity determinations must be met
for the 2006 PM2.5 NAAQS (including
hot-spot analyses in certain cases)
before any new federal approvals for
such projects can occur. See Table 1 in
40 CFR 93.109 for the conformity
criteria that apply for project-level
conformity determinations.
Isolated rural nonattainment and
maintenance areas are areas that do not
contain or are not part of any
metropolitan planning area as
designated by 23 U.S.C. 134 and 49
U.S.C. 5303 (40 CFR 93.101). As in other
newly designated nonattainment areas,
the one-year conformity grace period for
the 2006 PM2.5 NAAQS will begin on
the effective date of an isolated rural
area’s initial nonattainment designation.
However, because these areas do not
have federally required metropolitan
transportation plans and TIPs, they are
not subject to the frequency
requirements for conformity
determinations on transportation plans
and TIPs (40 CFR 93.104(b),(c), and (e)).
Instead, conformity determinations in
isolated rural areas are required only
when a non-exempt FHWA/FTA
project(s) needs approval.
Therefore, although the one-year
conformity grace period is available to
isolated rural areas, most likely no
conformity consequences would occur
upon the expiration date of the one-year
grace period because these areas most
likely would not have any projects that
require federal funding or approval at
that time. Once the conformity grace
date of the nonattainment designation. For
additional details on the conformity lapse grace
period, see the preamble to the January 24, 2008
conformity rule (73 FR 4423–4425).
16 For additional information on projects that can
proceed during a conformity lapse, refer to the final
rule of July 1, 2004 (69 FR 40005–40006), which
addressed the March 2, 1999 U.S. Court of Appeals
decision that affected related provisions of the
conformity rule (Environmental Defense Fund v.
EPA, 167 F.3d 641 (D.C. Cir. 1999). See also the
following guidance memoranda that address this
court decision: DOT’s January 2, 2002 guidance,
published in the Federal Register on February 7,
2002 (67 FR 5882); DOT’s May 20, 2003 and FTA’s
April 9, 2003 supplemental guidance documents;
and, EPA’s May 14, 1999 guidance memorandum.
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period has expired, a conformity
determination would only be required
in such areas when a non-exempt
FHWA/FTA project needs approval.
Conformity requirements for isolated
rural areas can be found at 40 CFR
93.109(n).17
Response to comments about the
grace period. Some commenters
believed that the one-year grace period
would not allow enough time for some
areas to meet the conformity
requirements. These same commenters
questioned whether a year would be
enough time to adequately prepare
attainment SIPs, learn EPA’s new
emissions factor model (called the
Motor Vehicle Emissions Simulator, or
MOVES model) when final, and
complete their conformity
determinations. To address these
concerns, these commenters suggested
lengthening the conformity grace period
for newly designated nonattainment
areas from one to two years.
EPA understands that some areas,
such as areas that have never done
conformity before and multijurisdictional nonattainment areas (e.g.,
areas with multiple states and/or
multiple MPOs) may have additional
challenges in conducting their initial
conformity determinations. However,
the CAA as amended on October 27,
2000 specifically provides newly
designated nonattainment areas with
only a one-year grace period, after
which conformity applies as a matter of
law under the statute. Therefore, we
believe that the statutory language
precludes EPA from extending the
conformity grace period beyond one
year for new nonattainment areas.
In accordance with the CAA, states
were initially required to submit their
recommendations for nonattainment
areas based on monitored data by
December 18, 2007, well before
designations became effective.18
Additionally, EPA began the process of
notifying state and local agencies, via
the EPA regional offices, of the timing
of conformity under the 2006 PM2.5
NAAQS in the April 16, 2007
memorandum cited earlier.19 As
17 Prior to today’s rulemaking, the requirements
for isolated rural areas were found at § 93.109(l).
This section has been renamed as § 93.109(n), as a
result of other revisions and additions in this
regulatory section. This is merely an administrative
change and the conformity requirements for
isolated rural areas remain unchanged.
18 Information on 2006 PM
2.5 nonattainment
designations, including copies of EPA’s designation
letters, can be accessed from EPA’s Web site at
https://www.epa.gov/pmdesignations/
2006standards/state.htm.
19 Memorandum entitled, ‘‘Transportation
Conformity and the Revised 24-hour PM2.5
Standard,’’ from Merrylin Zaw-Mon, then-Director,
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mentioned, EPA provided interim
guidance for the 2006 PM2.5 areas to
assist in meeting conformity
requirements by the end of the one-year
grace period. Finally, EPA will be
working with 2006 PM2.5 areas to
provide technical assistance in an
expeditious manner, such as helping
each area determine which test applies
for the first 2006 PM2.5 conformity
determination.
We also want to clarify that while
areas will have to complete a conformity
determination for their transportation
plans and TIPs within one year, they are
not required to complete their
attainment demonstration SIPs for the
2006 PM2.5 NAAQS in that same time
period as the commenter suggested.
Instead, they will have three years from
the effective date of designations to
submit their attainment demonstrations,
per CAA section 172(b).
Also, implementers will have
additional time before MOVES is
required for conformity determinations,
as a different grace period will apply for
MOVES once it is released. The
conformity rule at 40 CFR 93.111
provides a grace period before a new
emissions model is required for
conformity. This grace period can be
anywhere from three months to two
years depending on the degree of change
from one model to another (40 CFR
93.111(b)(2)); EPA is intending to
provide the maximum length two-year
grace period for the transition to
MOVES. Therefore, MOVES will not be
required for the first transportation plan
and TIP conformity determination done
for the 2006 PM2.5 NAAQS. EPA will
provide specific guidance regarding the
MOVES grace period and when MOVES
will be required to be used for SIPs and
conformity. This guidance will be
available on EPA’s Web site at: https://
www.epa.gov/otaq/stateresources/
transconf/policy.htm#models.
EPA and DOT understand the concern
that the commenter notes with respect
to learning the new MOVES model, and
therefore have devoted significant staff
time and resources to training state and
local air quality and transportation
planners in using MOVES. During 2009,
20 MOVES training sessions were held
at locations across the U.S. Once
MOVES is final, EPA intends to offer
web-based training, and EPA and DOT
are planning to hold additional inperson training sessions as well. See
EPA’s Web site: https://www.epa.gov/
Transportation and Regional Programs Division,
EPA Office of Transportation and Air Quality, to
EPA Regional Air Directors, Regions I– X, found on
EPA’s Web site at: https://www.epa.gov/otaq/
stateresources/transconf/generalinfo/rev24hrpm25.pdf.
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otaq/models/moves/
trainingsessions.htm for information
about upcoming training sessions. Also
note that other MOVES related
guidance, including user guides and
other technical information is available
on EPA’s Web site at: https://
www.epa.gov/otaq/models/moves/
index.htm and https://www.epa.gov/
otaq/stateresources/transconf/
policy.htm
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C. Definitions for PM2.5 NAAQS
EPA is adding two new definitions to
§ 93.101 of the conformity rule to
distinguish between the 1997 PM2.5
NAAQS and the 2006 PM2.5 NAAQS.
These definitions will help implement
certain conformity requirements in areas
that have been designated
nonattainment for 1997 PM2.5 NAAQS
and/or 2006 PM2.5 NAAQS. Some areas
designated nonattainment for the 2006
PM2.5 NAAQS also are designated
nonattainment for the 1997 PM2.5
NAAQS. In addition, some areas are
designated for only the 2006 PM2.5
NAAQS.
These definitions are similar to the
rule’s definitions in 40 CFR 93.101 for
the 1-hour ozone NAAQS and 8-hour
ozone NAAQS, and are generally
consistent with how EPA is defining
both kinds of PM2.5 areas for air quality
planning purposes. EPA also notes that
any provision of the conformity rule
that references only ‘‘PM2.5’’ and does
not specify which PM2.5 NAAQS applies
to any area designated nonattainment
for a PM2.5 NAAQS. EPA received no
comments regarding these definitions.
D. How Does This Final Rule Interact
With Conformity Requirements for the
1997 PM2.5 NAAQS?
Sections IV. through VI. of today’s
final rule describe conformity
requirements for areas designated
nonattainment for the 2006 PM2.5
NAAQS. No changes have been made to
the existing transportation conformity
requirements for areas designated
nonattainment for the 1997 PM2.5
NAAQS.
Nonattainment designations for the
1997 and 2006 PM2.5 NAAQS are
different designations with separate SIP
requirements, different attainment
dates, etc. As a result, CAA section
176(c)(5) requires conformity
requirements to be met in both 1997 and
2006 PM2.5 nonattainment and
maintenance areas, as applicable.
Some areas designated nonattainment
for the 2006 PM2.5 NAAQS have never
been subject to PM2.5 conformity
requirements. Under today’s final rule
and CAA section 176(c)(5), these areas
must meet conformity requirements
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only for the 2006 PM2.5 NAAQS, and not
for the 1997 PM2.5 NAAQS, because
these areas are not designated
nonattainment for the 1997 PM2.5
NAAQS.
Other areas designated nonattainment
for the 2006 PM2.5 NAAQS have been
designated also, in whole or in part, for
the 1997 PM2.5 NAAQS. (See Section
III.A. for the clarification that EPA has
made in designations for the 1997 PM2.5
NAAQS areas.) These areas must
continue to meet their existing
conformity requirements for the 1997
PM2.5 NAAQS as well as those that
apply for the 2006 PM2.5 NAAQS.
One commenter was concerned that,
given identical boundaries, an area
could potentially be required to prepare
conformity determinations for three
different PM NAAQS (i.e., the 24-hr
PM10 NAAQS, 1997 PM2.5 NAAQS, and
2006 PM2.5 NAAQS), and believed that
this could mean three separate analyses
would be required. This commenter
recommended that an area should only
have to model to the most restrictive
NAAQS.
As described in the May 2009
proposal, nonattainment designations
for these NAAQS are different
designations with separate SIP
requirements, different attainment
dates, etc. As a result, CAA section
176(c)(5) requires conformity to be met
for all of the NAAQS for which an area
has been designated. However, MPOs
subject to more than one PM NAAQS
will be able to use existing
transportation models and data for
regional emissions analyses, especially
where nonattainment area boundaries
are the same. Some analysis years for
the regional emissions analyses will be
the same, such as the last year of the
transportation plan. In addition, MPOs
in areas designated for more than one
PM NAAQS will be able to meet
consultation and other conformity
requirements through the existing
processes.
Furthermore, if an area is designated
nonattainment for both the 1997 and
2006 PM2.5 NAAQS and it has no
adequate or approved PM2.5 budgets, it
could use the same interim emissions
test for both NAAQS (see Section V.;
note that the baseline year for these two
NAAQS are different, see Section IV.) If
such an area has budgets only for the
1997 PM2.5 NAAQS, conformity
determinations for the 2006 PM2.5
NAAQS will be based on the same
conformity test—i.e., the budget test—
that is being used for the 1997 PM2.5
NAAQS (note that the attainment year
for each of these NAAQS, which is a
required analysis year for the budget
test, will differ). As described in Section
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VI., MPOs must use any adequate or
approved SIP budgets for the 1997 PM2.5
NAAQS for conformity determinations
that are made prior to SIP budgets for
the 2006 PM2.5 NAAQS being found
adequate or approved.
Today’s final rule does not impact
project-level conformity requirements
for the 1997 PM2.5 NAAQS. For
example, this rule does not
substantively change the PM2.5 hot-spot
analysis requirements, and EPA and
FHWA’s existing qualitative guidance
for such analyses continues to be
available.20 For the purposes of PM2.5
conformity, a hot-spot analysis must
address the PM2.5 NAAQS for which the
area has been designated
nonattainment.21 See Section VII. for
further information regarding projectlevel conformity requirements for the
2006 PM2.5 NAAQS.
EPA will work with PM2.5
nonattainment areas as needed to ensure
that state and local agencies can meet
conformity requirements for both the
applicable 1997 and 2006 PM2.5 NAAQS
in a timely and efficient manner.
E. Precursors That Apply for 2006 PM2.5
Conformity
The existing transportation
conformity rule at 40 CFR 93.102(b)
describes the pollutants and precursors
that must be examined in a regional
emissions analysis in PM2.5 areas, and
these provisions apply to 2006 PM2.5
areas as well as 1997 PM2.5 areas. Direct
PM2.5 must be analyzed per 40 CFR
93.102(b)(1). Before SIP budgets are
adequate or approved, NOX must also be
analyzed, unless both EPA and the state
air quality agency find that
transportation-related emissions of NOX
are not a significant contributor to the
PM2.5 nonattainment problem and notify
the MPO and DOT (40 CFR
93.102(b)(iv)).22 Before SIP budgets are
adequate or approved, VOCs, sulfur
dioxide, and ammonia do not have to be
analyzed unless either EPA or the state
air quality agency finds that such a
precursor is a significant contributor,
and notifies the MPO and DOT (40 CFR
93.102(b)(v)). Similarly, before SIP
budgets are adequate or approved, road
dust does not have to be included in the
regional emission analysis of directly
20 ‘‘Transportation Conformity Guidance for
Qualitative Hot-spot Analyses in PM2.5 and PM10
Nonattainment and Maintenance Areas,’’ EPA420–
B–06–902, March 2006.
21 EPA notes that today’s final rule does not
address project requirements for the National
Environmental Policy Act or other environmental
programs.
22 Note that instead of establishing a budget for
direct PM2.5 or NOX, a SIP could demonstrate that
the pollutant or precursor is insignificant based on
40 CFR 93.109(k).
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emitted PM2.5 unless EPA or the state air
agency find that re-entrained road dust
emissions are a significant contributor,
and notifies the MPO and DOT (40 CFR
93.102(b)(3)).
Once budgets from a submitted PM2.5
SIP have been found adequate or
approved, a conformity determination
for the 2006 PM2.5 NAAQS must include
any precursors for which budgets are
established (40 CFR 93.102(b)(iv) and
(v)). If road dust is included in the
direct PM2.5 budget, it must also be
included in a regional emissions
analysis (40 CFR 93.102(b)(3)).
Please use the interagency
consultation process if there are
questions regarding whether a regional
emissions analysis for the 2006 PM2.5
NAAQS must include specific
precursors or road dust.
IV. Baseline Year for Certain 2006
PM2.5 Nonattainment Areas
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A. Background
Conformity determinations for
transportation plans, TIPs, and projects
not from a conforming transportation
plan and TIP must include a regional
emissions analysis that fulfills CAA
provisions. The conformity rule
provides for several different regional
emissions analysis tests that satisfy CAA
requirements in different situations.
Once a SIP with a motor vehicle
emissions budget (‘‘budget’’) is
submitted for an air quality NAAQS and
EPA finds the budget adequate for
conformity purposes or approves it as
part of the SIP, conformity is
demonstrated using the budget test for
that pollutant or precursor, as described
in 40 CFR 93.118.
Before an adequate or approved SIP
budget is available, conformity of the
transportation plan, TIP, or project not
from a conforming transportation plan
and TIP is demonstrated using the
interim emissions test(s), as described in
40 CFR 93.119. The interim emissions
tests include different forms of the
‘‘build/no-build’’ test and ‘‘baseline year’’
test. In general, for the baseline year
test, emissions from the planned
transportation system are compared to
emissions that occurred in the baseline
year. Today’s rule updates section
93.119 of the conformity rule for the
2006 PM2.5 NAAQS. The baseline year
for nonattainment areas under the 1997
PM2.5 NAAQS is 2002 (40 CFR
93.119(e)(2)). Sections V. and VI. of
today’s final rule go into further detail
about how the baseline year will be
applied in 2006 PM2.5 areas.
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B. Baseline Year for 2006 PM2.5 Areas
1. Description of Final Rule
In today’s final rule, EPA is defining
the baseline year as the most recent year
for which EPA’s Air Emissions
Reporting Requirements (AERR) (40
CFR Part 51) requires submission of onroad mobile source emissions
inventories,23 as of the effective date of
EPA’s nonattainment designations for
any PM2.5 NAAQS other than the 1997
PM2.5 NAAQS. EPA had proposed this
definition under ‘‘Option 2’’ in the
proposed rule. AERR requires on-road
mobile source emission inventories to
be submitted every three years, for
example, 2002, 2005, 2008, 2011, etc.
See § 93.119(e)(2)(B) for the regulatory
text.
Today’s final rule results in a baseline
year of 2008 for the 2006 PM2.5 areas.
The year 2008 is the most recent year as
of the effective date of the 2006 PM2.5
designations, December 14, 2009, for
which AERR requires submission of onroad mobile source emissions
inventories. In other words, the
designations were effective on
December 14, 2009, and the most recent
year for which an on-road mobile source
inventory was required as of that date
was 2008. Therefore, 2008 is the
baseline year for 2006 PM2.5 areas.
This final rule would also govern the
baseline year for conformity purposes
for any areas designated for a PM2.5
NAAQS that EPA promulgates in the
future. EPA will clarify the relevant
baseline year under today’s regulation
for each such future NAAQS for
conformity implementers in guidance
and maintain a list of baseline years that
result from today’s final rule on EPA’s
Web site.24
Today’s action does not change the
2002 baseline year for areas designated
nonattainment for the 1997 PM2.5
NAAQS and the conformity rule now
clarifies that 2002 applies as the
baseline year only to areas designated
nonattainment for the 1997 PM2.5
NAAQS. The baseline year for 1997
PM2.5 NAAQS areas is found in
§ 93.119(e)(2)(A).
The existing interagency consultation
process (40 CFR 93.105(c)(1)(i)) must be
used to determine the latest
assumptions and models for generating
baseline year motor vehicle emissions to
complete any baseline year test. The
baseline year emissions level that is
used in conformity must be based on the
latest planning assumptions available,
the latest emissions model, and
23 40
CFR 51.30(b).
https://www.epa.gov/otaq/stateresources/
transconf/index.htm.
24 See
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14265
appropriate methods for estimating
travel and speeds as required by 40 CFR
93.110, 93.111, and 93.122 of the
current conformity rule. The baseline
year test can be completed with a
submitted or draft baseline year motor
vehicle emissions SIP inventory, if the
SIP reflects the latest information and
models. If such a SIP baseline is not
available, an MPO, in consultation with
state and local air agencies, could also
develop baseline year emissions as part
of the conformity analysis.
2. Rationale and Response to Comments
General overview. EPA believes that
today’s definition for the baseline year
results in an environmentally protective
and legal baseline year for conformity
under the 2006 PM2.5 NAAQS and any
future PM2.5 NAAQS revisions, and best
accomplishes several important goals.
First, as EPA discussed in the
preamble to the proposed rule, EPA
believes that a more recent year than
2002 (the baseline year for 1997 PM2.5
areas) is appropriate for meeting CAA
conformity requirements for 2006 PM2.5
nonattainment areas. EPA also believes
that using a more recent year is more
environmentally protective than 2002,
and more relevant for the 2006 PM2.5
NAAQS. Several commenters agreed
with these points. Because the AERR
requires submission of inventories every
three years, today’s final rule results in
a baseline year that is recent for any
PM2.5 NAAQS established after 1997.
The baseline year will always be either
the same year as the year in which
designations are effective, or one or two
years prior to the effective date of
designations. For example, in the case of
the 2006 PM2.5 NAAQS, the baseline
year, 2008, is the year before the year in
which designations are effective, 2009.
EPA had also proposed 2005 as a
baseline year as it is also more recent
than 2002. One commenter preferred a
2005 baseline year because the
introduction of Tier 2 and improved
fuel and engine technologies since then
would allow transportation plans and
TIPs to meet conformity more easily.
However, because of the
implementation of EPA’s Tier 2 Vehicle
and Gasoline Program as well as other
federal programs, motor vehicle
emissions in the year 2005 were higher
than emissions in the year 2008. Thus
today’s rule, which results in a baseline
year of 2008, provides more protection
for the environment than would a
baseline year of 2005, in the time before
an area has adequate or approved motor
vehicle emissions budgets from a SIP
that addresses PM2.5.
Second, today’s baseline year
definition coordinates the conformity
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baseline year with other air quality
planning requirements, which allows
state and local governments to use their
resources more efficiently. Coordinating
the conformity baseline year with the
year used for SIP planning and an
emission inventory year was EPA’s
rationale for using 2002 as the baseline
year for conformity tests in existing
PM2.5 nonattainment areas for the 1997
NAAQS. Today’s regulatory text results
in a conformity baseline year that is
consistent with emission inventory
requirements, and most likely will be
consistent with the baseline year used
for SIP planning as well. Several
commenters voiced support for
coordinating the conformity baseline
year with these other air quality
planning requirements.
Third, today’s final rule provides
transportation planners with knowledge
of the baseline year for any future PM2.5
NAAQS upon the effective date of
designations for that NAAQS, without
having to wait either for EPA to amend
the transportation conformity rule or
select a SIP planning baseline year. As
a result, MPOs and other transportation
planners would understand conformity
requirements for future PM2.5 NAAQS
revisions more quickly, which may, in
turn, also allow more time to prepare
and complete necessary conformity
determinations. Several commenters
agreed that not having to wait for a rule
revision would be a benefit of defining
the baseline year as in today’s rule,
rather than choosing a specific year.
Some commenters preferred defining
the baseline year in terms of the year
used as the baseline year for SIP
planning. Today’s final rule addresses
these concerns since it will most likely
result in a conformity baseline year that
is consistent with the SIP baseline year,
and in the future will give
transportation planners the advantage of
knowing the baseline year at the
beginning of the grace period for newly
designated areas.
Last, given that the CAA requires EPA
to review the NAAQS for possible
revision once every five years, today’s
baseline year provision potentially
reduces the need for future rule
revisions for any future PM2.5 NAAQS.
While today’s final rule establishes a
baseline year for any PM2.5 NAAQS
other than the 1997 PM2.5 NAAQS, the
same rationale would apply for
establishing the same type of baseline
year definition for any future new or
revised NAAQS of a transportationrelated criteria pollutant. Therefore,
EPA may amend the rule in the future
to apply the baseline year language
found in today’s § 93.119(e)(2)(B) more
generally. However, EPA did not
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propose such an amendment, and
intends to solicit and consider public
comment before it would adopt any
such provision.
Specific comments. EPA is
responding today to several comments
regarding the baseline year. A couple of
commenters indicated that they thought
proposed Option 2 would create a
‘‘rolling’’ baseline year, that is, one that
would be updated every three years.
One commenter did not support such a
rolling baseline; another did support it
as long as motor vehicle emissions in an
inventory year were less than the prior
reporting year. However, today’s final
rule does not establish a rolling baseline
year for any PM2.5 NAAQS. It
establishes a single baseline year for
each PM2.5 NAAQS that does not change
over time. For example, for the 2006
PM2.5 NAAQS, the definition results in
a baseline year of 2008. The year 2008
will remain the baseline year for 2006
PM2.5 areas until it’s no longer needed,
i.e., until adequate or approved budgets
are available in a given area.
One commenter who supported the
option finalized in today’s rule
expressed concern that final emissions
data would not be available for 2008 for
some time. However, if a final AERR
inventory for 2008 is not available in a
particular area, there are other options
for generating the motor vehicle
emissions in the baseline year,
discussed above under ‘‘IV.B.1.
Description of Final Rule.’’
Another commenter expressed
concern that MOVES would not be
available in time for the year 2008 for
the first conformity determination for
the 2006 PM2.5 NAAQS. At this time,
the current emissions model,
MOBILE6.2, applies for conformity in
all areas except California, where
EMFAC2007 applies. Therefore, if the
MOVES model is not available to
generate a 2008 baseline estimate for use
in conformity, the MOBILE6.2 model
must be used. Once MOVES is available,
areas can create a new baseline
emissions estimate for use in conformity
using MOVES along with other interim
analysis years. EPA will provide a
policy guidance document for using
MOVES in conformity determinations
that will include more details about
when MOVES must be used. When
available, this guidance will be found
on EPA’s Web site at: https://
www.epa.gov/otaq/stateresources/
transconf/policy.htm#models. For more
information on MOVES, please see
EPA’s Web site at: https://www.epa.gov/
otaq/models/moves/index.htm.
One commenter thought that the
baseline year should be determined
through interagency consultation. This
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was not a proposed option. However,
EPA believes that details for the
baseline year test must be determined
through rulemaking, as EPA has done
for other NAAQS since 1993. Today’s
rule better accomplishes the purposes of
meeting the CAA’s requirements,
coordinating with SIP and inventory
planning, and providing certainty to
transportation planners. Furthermore,
today’s rule ensures consistency across
the nation, whereas allowing each area
to determine its own baseline year
through interagency consultation could
result in different baseline years in
different areas.
V. Regional Conformity Tests in 2006
PM2.5 Nonattainment Areas That Do
Not Have Adequate or Approved SIP
Budgets for the 1997 PM2.5 NAAQS
This section of the preamble discusses
regional conformity tests for
nonattainment areas for the 2006 PM2.5
NAAQS that do not have adequate or
approved PM2.5 SIP budgets for the 1997
NAAQS. This part of the final rule
applies to 2006 PM2.5 nonattainment
areas that were not covered by the 1997
PM2.5 NAAQS, as well as nonattainment
areas for both PM2.5 NAAQS that do not
have an adequate or approved 1997
PM2.5 SIP budget. EPA has addressed
conformity tests for these areas under
section 93.109(j) of the conformity rule.
See Section VI. of today’s final rule for
conformity tests in 2006 PM2.5 areas that
have adequate or approved SIP budgets
for the 1997 PM2.5 NAAQS.
Note that the rule finalizes new
requirements for conformity only under
the 2006 PM2.5 NAAQS. Today’s final
rule does not address or change the
requirements for demonstrating
conformity for the 1997 PM2.5 NAAQS.
A. Conformity After 2006 PM2.5 SIP
Budgets Are Adequate or Approved
1. Description of Final Rule
Once a SIP for the 2006 PM2.5 NAAQS
is submitted with a budget(s) that EPA
has found adequate or approved, the
budget test must be used in accordance
with 40 CFR 93.118 to complete all
applicable regional emissions analyses
for the 2006 PM2.5 NAAQS. This
requirement is found at § 93.109(j)(2).
Conformity is demonstrated if the
transportation system emissions
reflecting the proposed transportation
plan, TIP, or project not from a
conforming transportation plan and TIP
are less than or equal to the motor
vehicle emissions budget level defined
by the SIP as being consistent with CAA
requirements.
The first SIP for the 2006 PM2.5
NAAQS could be a control strategy SIP
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required by the CAA (i.e., reasonable
further progress SIP or attainment
demonstration) or a maintenance plan.
States could also voluntarily choose to
submit an ‘‘early progress SIP’’ prior to
required SIP submissions. Early
progress SIPs must demonstrate a
significant level of future emissions
reductions from a previous year’s
emissions. For example, an area could
submit an early progress SIP for the
2006 PM2.5 NAAQS that demonstrates a
specific percentage of emissions
reductions (e.g. 5–10%) in an area’s
attainment year from the baseline year
emissions (e.g., 2008). An early progress
SIP would include emissions
inventories for all emissions sources for
the entire 2006 PM2.5 nonattainment
area and would meet applicable
requirements for reasonable further
progress SIPs. EPA has discussed this
option in past conformity rule
preambles, e.g. the July 1, 2004
transportation conformity final rule (69
FR 40028), and many states have
established early progress SIP budgets
for conformity purposes.
Whatever the case, the interim
emissions test(s) would no longer be
used for direct PM2.5 or a relevant
precursor once an adequate or approved
SIP budget for the 2006 PM2.5 NAAQS
is established and effective for the
pollutant or precursor. States are
required to develop their future 2006
PM2.5 SIPs in consultation with MPOs,
state and local transportation agencies,
and local air quality agencies in an
effort to facilitate future conformity
determinations. EPA Regions will be
available to assist states in the
development of early progress SIPs for
the 2006 PM2.5 NAAQS, if desired.
2. Rationale and Response to Comments
EPA believes that this provision meets
statutory requirements for conformity
determinations that occur after SIP
budgets are available for the 2006 PM2.5
NAAQS. Section 176(c) of the CAA
states that transportation activities must
‘‘conform to an implementation plan…’’
(SIP) and states further that conformity
to an implementation plan means
conformity to the SIP’s purpose. Once
EPA finds a budget for the 2006 PM2.5
NAAQS adequate or approves the SIP
that includes it, the budget test provides
the best means to determine whether
transportation plans and TIPs meet the
statutory obligations in CAA sections
176(c)(1)(A) and (B) for that NAAQS.
That is, the budget test best shows that
transportation plans and TIPs conform
to the SIP’s purpose of eliminating or
reducing the severity and number of
violations of the NAAQS and achieving
expeditious attainment of the NAAQS
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(176(c)(1)(A)); and best confirms the
requirement that transportation plans
and TIPs not cause or contribute to any
new violation, worsen an existing
violation, or delay timely attainment or
any interim milestones (176(c)(1)(B)).
The budget test also best demonstrates
that transportation plans and TIPs
comply with the statutory obligation to
be consistent with the emissions
estimates in SIPs, according to CAA
section 176(c)(2)(A). By being consistent
with the on-road mobile source
emissions levels in the SIP,
transportation planners can ensure that
their activities remain consistent with
state and local air quality goals to
protect public health. EPA received no
comments on this aspect of today’s rule.
B. Conformity Before 2006 PM2.5 SIP
Budgets Are Adequate or Approved
1. Description of Final Rule
The 2006 PM2.5 nonattainment areas
that do not have existing adequate or
approved PM2.5 budgets for the 1997
PM2.5 NAAQS must meet one of the
following interim emissions tests for
conformity determinations conducted
before adequate or approved 2006 24hour PM2.5 SIP budgets are established:
• The build-no-greater-than-no-build
test (‘‘build/no-build test’’), or
• The no-greater-than-baseline year
emissions test (‘‘baseline year test’’).
This aspect of today’s final rule is
similar to the transportation conformity
rule at 40 CFR 93.119(e) for
nonattainment areas for the 1997 PM2.5
NAAQS. Today’s final rule allows 2006
PM2.5 nonattainment areas without SIP
budgets to choose between the two
interim emissions tests, rather than
require that one specific test or both
tests be completed. Conformity is
demonstrated if, for each analysis year,
the transportation emissions reflecting
the proposed transportation plan or TIP
(build) are less than or equal to either
the emissions from the existing
transportation system (no-build), or the
level of motor vehicle emissions in the
baseline year, as described in 40 CFR
93.119. For the discussion of the
baseline year for the 2006 PM2.5
NAAQS, please refer to Section IV. of
today’s notice.
2. Rationale and Response to Comments
EPA believes that this provision of
today’s rule meets statutory
requirements for conformity
determinations that occur before SIP
budgets are available for the 2006 PM2.5
NAAQS. EPA believes it is appropriate
to provide flexibility and allow 2006
PM2.5 areas to meet only one interim
emissions test before adequate or
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14267
approved PM2.5 SIP budgets are
established.
Using either the build/no-build test or
baseline year test is sufficient to meet
CAA section 176(c)(1)(B) requirements
that transportation activities do not
cause or contribute to new air quality
violations, worsen existing violations, or
delay timely attainment or any interim
milestones. The baseline year and the
build/no-build tests are sufficient for
demonstrating conformity when an area
does not have a SIP budget for a portion
of a nonattainment area.
Based on the CAA, EPA has
previously determined that only in
ozone and CO areas of higher
classifications 25 are transportation
plans and TIPs required to also satisfy
section 176(c)(3)(A)(iii), i.e., that the
transportation plan and TIP contribute
to emissions reductions, during the time
period before adequate or approved SIP
budgets are available (58 FR 3782–3783;
62 FR 43784–43785; 69 FR 40018,
40019–40031). As a result, the current
rule requires these ozone and CO areas
to meet both interim emissions tests,
rather than only one test.
However, prior to today’s rule, the
conformity rule already allowed areas
designated for the other pollutants, as
well as the lower classifications of
ozone and CO, to conform based on only
one interim emissions test, rather than
having to complete two tests and
thereby contribute further reductions
towards attainment. Today’s final rule
requiring the 2006 PM2.5 areas also to
meet only one of the interim emissions
tests meets the CAA’s requirements in
section 176(c)(1)(B) (described above in
Section II.A., footnote 1). For more
information and the full rationale for
allowing some areas to conform based
on only one interim emissions test, see
the November 24, 1993 final rule (58 FR
62197) that addressed interim
requirements for PM10 and NO2 areas,
the July 1, 2004 final rule (69 FR 40029)
that established interim requirements
for 1997 PM2.5 areas, and the May 15,
2009 proposed rule.
EPA believes that the no-greater-thanbaseline year interim emissions test is
an appropriate test for meeting section
176(c)(1)(B) (refer to footnote 1 in
Section II.A.) requirements in 2006
PM2.5 nonattainment areas. By
definition, the no-greater-than baseline
year test ensures that emissions from
on-road mobile sources are no greater
than they were during the baseline year
that will most likely be used for 2006
25 These areas include ozone areas classified as
moderate and above, CO areas classified as
moderate with design value greater than 12.7 ppm,
and CO areas classified as serious.
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PM2.5 NAAQS SIP planning purposes. If
future on-road emissions do not
increase above their base year levels,
applicable statutory requirements are
met.
The build/no-build test also allows a
2006 PM2.5 area to meet statutory
requirements. As described above, the
build/no-build test requires a regional
emissions analysis to demonstrate that
the emissions from the proposed
transportation system in future years
would be less than the emissions from
the built transportation system in future
years. Since for each analysis year, a
new transportation plan, TIP, or project
(the build scenario) could not result in
regional emissions that are higher than
those that would occur in the absence
of the proposed transportation activities
(the no-build scenario) for the system,
CAA section 176(c)(1)(B) requirements
are met. For these reasons, EPA believes
that the build/no-build test continues to
be an appropriate interim test prior to
SIP budgets being available.
Most commenters supported allowing
2006 PM2.5 areas to meet only one of the
interim emissions tests because it would
give areas the flexibility to use the test
they deem most appropriate, given the
available data and the unique
circumstances of individual areas.
However, one commenter objected,
arguing that the rule doesn’t promote
the CAA or the SIP process because it
doesn’t require reduction of PM2.5
emissions. The commenter also stated
that the case EPA cited in its proposal,
Environmental Defense v. EPA 467 F .3d
1329 (DC Cir. 2006), is not pertinent
because it did not consider climate
change factors in any way.
EPA disagrees. First, it has already
been clearly established in case law that
the conformity provisions of the CAA
do not require that transportation
projects achieve additional emission
reductions in PM2.5 areas before SIP
budgets are available. As discussed
above, allowing 2006 PM2.5 areas the
choice of interim emissions tests does
meet the CAA’s requirements. Today’s
rule is parallel to the current rule’s
requirements for 1997 PM2.5
nonattainment areas (69 FR 40028–
40031), which were upheld by an
October 2006 court decision.
Environmental Defense v. EPA, 467 F.3d
1329 (D.C. Cir. 2006).26 Contrary to the
26 Petitioners challenged several aspects of the
conformity regulations. In its decision, the U.S.
Court of Appeals for the District of Columbia
Circuit upheld EPA’s regulations at 40 CFR
93.119(b)(2), (d), and (e) ‘‘because the Act does not
require that activities involving transportation
actually reduce pollutants, but merely not frustrate
an implementation plan’s purpose to reduce overall
emissions.’’ The court also upheld EPA’s regulations
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commenter’s view, this court case is not
rendered irrelevant because it doesn’t
consider climate change factors;
conformity applies only to
nonattainment and maintenance areas
for transportation-related criteria
pollutants and their precursors.
The same commenter thought that the
2006 court case does not preclude EPA
from reasonably determining that more
stringent interim rules are required to
‘‘conform to a SIP’s purpose of reducing
overall emissions.’’ However, EPA
believes that the best interpretation of
the Act is that reflected in today’s rule,
which allows 2006 PM2.5 areas the
choice between the interim emissions
tests. This interpretation is also
consistent with past rulemakings for
interim emissions test requirements for
other pollutants, as described above.
Finally, one commenter asked EPA to
clarify whether an area that is currently
using one of the interim emissions tests
for the 1997 PM2.5 NAAQS could use
the results of that test for the 2006 PM2.5
NAAQS. When areas are determining
conformity for the 1997 and 2006 PM2.5
NAAQS at the same time, they could
apply some of the information
developed in the 1997 PM2.5 regional
emissions analysis in creating 2006
PM2.5 regional emissions analysis.
First, note that regardless of whether
the area is using the baseline year test
or build/no-build test, the same analysis
years can be used for 1997 PM2.5
conformity and 2006 PM2.5 conformity
when the analyses are done at the same
time (refer to 40 CFR 93.119(g) for
analysis year requirements).
In most 1997 PM2.5 areas, conformity
applies only for the annual NAAQS.27
While the results of an interim
emissions test for the 1997 annual PM2.5
NAAQS cannot be directly applied for
the 2006 24-hour PM2.5 NAAQS, the
option described below could save
implementers some effort when
conformity is being determined for both
of these NAAQS at the same time. This
option applies only when using
MOBILE6.2 for regional emissions
analyses.28
at 40 CFR 93.118(b), (d), and (e)(6). The court
vacated a narrow provision at 40 CFR
93.109(e)(2)(v) which had allowed 8-hour ozone
areas to avoid using their existing 1-hour budgets
under certain circumstances. This provision was
removed from the transportation conformity
regulation in the January 24, 2008 final rule (see 73
FR 4434).
27 There are two areas where conformity for both
the 1997 annual and 24-hour NAAQS applies. See
Section III.A. for more information.
28 Areas in California should use the interagency
consultation process to determine appropriate
methods. In all other 2006 PM2.5 areas, EPA expects
that MOBILE6.2 will be used for the first 2006 PM2.5
conformity determinations.
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Areas should develop the annual
emissions for the 1997 PM2.5 NAAQS by
estimating emissions in two seasons,
summer and winter; four seasons; or the
12 months of the year.29
To apply information from the
analysis done for the 1997 PM2.5
NAAQS to the 2006 PM2.5 analysis, for
each analysis year, areas should use the
emission factors developed in the 1997
PM2.5 NAAQS regional emissions
analysis for PM2.5 and NOX in a season
or month where violations of the 2006
PM2.5 NAAQS occurred, and multiply
these emission factors by the seasonallyadjusted average daily VMT for the area
of the analysis year.30 If violations
occurred in more than one season or
month, the interagency consultation
process should be used to choose the
season or month that would best ensure
that the CAA is met, for example by
choosing the season with the most
frequent or most severe violations, or
the season with the highest vehicle
miles traveled, or both.31 The choice of
season or seasons should be based on air
quality data from the three years used to
make designations (i.e., 2006–2008),
unless more recent air quality data
indicates that a different season should
be analyzed, as decided through
consultation.
Whatever season is chosen to estimate
the build scenario emissions, the same
season should be used for comparison
whether using the baseline year test or
build/no-build test. For example,
emissions for a build scenario
calculated using winter MOBILE6.2
inputs should be compared to emissions
in the winter of the baseline year, or
emissions in winter from the no-build
scenario.
29 This description reflects how analyses are to be
done for the 1997 PM2.5 NAAQS, which is covered
in ‘‘Guidance for Creating Annual On-Road Mobile
Source Emission Inventories for PM2.5
Nonattainment Areas for Use in SIPs and
Conformity,’’ EPA420–B–05–008, August 2005,
found on EPA’s Web site at: https://www.epa.gov/
otaq/stateresources/transconf/policy/
420b05008.pdf. In particular, Question 7 on pp.
5–8 of that guidance addresses how analyses are to
be done for the 1997 PM2.5 NAAQS.
30 If a 24-hour emissions estimate is available in
the appropriate season or month because this step
has been completed for 1997 PM2.5 NAAQS
conformity and conformity is being determined for
the 1997 PM2.5 NAAQS and the 2006 PM2.5 NAAQS
at the same time, it does not need to be redone but
can be applied in the regional emissions analysis
for 2006 PM2.5 conformity.
31 Note that this guidance regarding the choice of
season applies only when using MOBILE6.2 and not
MOVES because MOBILE6.2 PM2.5 emission factors
are not sensitive to changes in temperature. EPA
will provide guidance on this issue when MOVES
is released. See EPA’s Web site at: https://
www.epa.gov/otaq/models/moves/index.htm and
https://www.epa.gov/otaq/stateresources/transconf/
policy.htm for future MOVES guidance.
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Note that after the effective date of
today’s final rule, the baseline year for
the 2006 PM2.5 NAAQS will be 2008
while the baseline year for the 1997
PM2.5 NAAQS remains 2002. See
Section IV. for additional discussion of
the baseline year.
As stated above, once an area has
adequate or approved budgets for any
PM2.5 NAAQS, it must use the budget
test instead of an interim emissions test.
C. Implementation of Regional Tests
The existing conformity rule’s general
requirements for PM2.5 regional
emissions analyses apply to 2006 PM2.5
areas that do not have adequate or
approved SIP budgets for the 1997 PM2.5
NAAQS. EPA is including this
discussion of the existing regulation’s
requirements for clarity, to help readers
understand how the existing regulation
applies to areas designated
nonattainment for the 2006 PM2.5
NAAQS. The discussion below is
intended to illustrate how today’s final
rule is to be implemented in practice for
2006 PM2.5 areas without adequate or
approved 1997 PM2.5 SIP budgets.
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1. Decisions Made Through the
Interagency Consultation Process
The existing rule’s consultation
process must be used to determine the
test for completing any regional
emissions analysis for the 2006 PM2.5
NAAQS, as required by 40 CFR
93.105(c)(1)(i). The existing interagency
consultation process must also be used
to determine the latest assumptions and
models for generating motor vehicle
emissions regardless of the test used.
Refer to Section IV. of this preamble for
details about generating baseline year
emissions if that interim emissions test
is selected for a given conformity
determination.
In addition, the consultation process
must be used to determine which
analysis years should be selected for
regional emissions analyses. Before an
adequate or approved 2006 PM2.5 budget
is available, areas would be able to
choose, through interagency
consultation, either interim emissions
test for each conformity determination.
However, the same test must be used for
each analysis year for a given
determination. EPA believes that
sufficient flexibility exists without
mixing and matching interim emissions
tests for different analysis years within
one conformity determination, which is
unnecessarily complicated and may
indicate that an area would not conform
using one test consistently.
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2. How a Regional Emissions Analysis
Can Be Developed When Using An
Interim Emissions Test
Under the ‘‘Rationale and Response to
Comments’’ above, EPA described how
an area using an interim emissions test
for 1997 PM2.5 conformity could apply
it to 2006 PM2.5 conformity. This section
provides general guidance for creating a
2006 PM2.5 regional emissions analysis.
Because the 2006 PM2.5 NAAQS
designations were only for the 2006
24-hour PM2.5 NAAQS, the regional
emissions analysis will be based on
emissions for a 24-hour time period.
For either the baseline year test or the
build/no-build test, for each analysis
year, emissions must be estimated for
the build scenario according to 40 CFR
93.119(i) with a 24-hour emissions
inventory. (The build scenario is
referred to as the ‘‘Action’’ scenario at 40
CFR 93.119(i).)
This emissions inventory would
include direct PM2.5, NOX, and any
other relevant precursor emissions 32
that result from the build scenario using
MOBILE6.2 for a 24-hour period. For
each analysis year chosen, areas should
choose MOBILE6.2 inputs for the season
of the year where violations of the 2006
PM2.5 NAAQS occurred.33 If violations
occurred in more than one season,
implementers should use the
interagency consultation process to
choose the season (or seasons) that
would best ensure that the CAA is met,
for example by choosing the season with
the most frequent or most severe
violations, or the season with the
highest vehicle miles traveled, or
both.34 The choice of season or seasons
should be based on air quality data from
the three years used to make
designations (i.e., 2006–2008), unless
more recent air quality data indicates
that a different season should be
analyzed, as decided through
consultation.
For each analysis year, these emission
factors from MOBILE6.2 for direct PM2.5,
NOX, and any other relevant precursor
for the season chosen should be
32 Refer to 40 CFR 93.102(b) for which precursors
apply. To date, before they have adequate or
approved budgets from a PM2.5 SIP, PM2.5 areas
have determined conformity for only direct PM2.5
and NOX.
33 In California where EMFAC is used, areas
should use the interagency consultation process to
determine appropriate methods.
34 Note that this guidance regarding the choice of
season applies only when using MOBILE6.2 and not
MOVES because MOBILE6.2 PM2.5 emission factors
are not sensitive to changes in temperature. EPA
will provide guidance on this issue when MOVES
is released. See EPA’s Web site at: https://
www.epa.gov/otaq/models/moves/index.htm and
https://www.epa.gov/otaq/stateresources/transconf/
policy.htm for future MOVES guidance.
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14269
multiplied by the seasonally-adjusted
average daily VMT in that analysis year
to create an estimate of transportation
emissions in a 24-hour period. For
additional guidance on creating daily
emissions inventories, refer to EPA’s
existing guidance documents.35
Note that whatever season is chosen
to estimate the build scenario emissions,
the same season should be used for
comparison whether using the baseline
year test or build/no-build test. For
example, emissions for a build scenario
calculated using winter MOBILE6.2
inputs should be compared to emissions
in the winter of the baseline year (see
Section IV. for a discussion of the
baseline year in 2006 PM2.5 areas), or
emissions in winter from the no-build
scenario.
Refer to 40 CFR 93.119 for additional
information about conducting the build/
no-build and baseline year tests.
3. Conformity Test Requirements for All
Areas
Regional emissions analyses under
today’s final rule are to be implemented
through existing conformity
requirements such as 40 CFR 93.118,
93.119, and 93.122. For example, the
existing conformity rule requires that
certain years within the transportation
plan (or alternate timeframe) be
examined. Under 40 CFR 93.118(d), the
following years would be analyzed for
the budget test with 2006 PM2.5 SIP
budgets:
• The attainment year for the 2006
PM2.5 NAAQS (if it is within the
timeframe of the transportation plan and
conformity determination);
• The last year of the timeframe of the
conformity determination (40 CFR
93.106(d)); and
• Intermediate years as necessary so
that analysis years are no more than ten
years apart.
For the interim emissions tests, the
existing conformity rule (40 CFR
93.119(g)) requires the following
analysis years:
• A year no more than five years
beyond the year in which the
conformity determination is being
made;
• The last year of the timeframe of the
conformity determination (as described
in 40 CFR 93.106(d));
• Intermediate years as necessary so
that analysis years are no more than 10
years apart.
35 Specifically, see EPA’s ‘‘Technical Guidance on
the Use of MOBILE6.2 for Emission Inventory
Preparation,’’ EPA420–R–04–013, August 2004,
found on EPA’s Web site at: https://www.epa.
gov/otaq/models/mobile6/420r04013.pdf and
‘‘Procedures for Emission Inventory Preparation—
Vol IV: Mobile Sources,’’ found at: https://ntl.bts.gov/
DOCS/AQP.html.
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See the relevant regulatory sections of
the conformity rule and the July 1, 2004
final rule preamble for further
background on how tests have been
implemented for other pollutants and
NAAQS (69 FR 40020).
conformity tests for these areas are
found under a new section 93.109(k).
See Section V. of this preamble for
conformity tests in 2006 PM2.5 areas that
do not have an adequate or approved
1997 PM2.5 SIP budget.
4. Cases Involving Multi-Jurisdictional
Areas
A. Conformity After 2006 PM2.5 SIP
Budgets Are Adequate or Approved
In July 2004, EPA issued a guidance
document for implementing conformity
requirements in multi-jurisdictional
areas.36 Multi-jurisdictional areas are
nonattainment and maintenance areas
with multiple MPOs, one or more MPOs
and a donut area, or multi-state areas.
EPA believes that this guidance should
also apply to 2006 PM2.5 areas with
multiple jurisdictions.
There are two parts of this existing
guidance that are most relevant for
implementing conformity for multijurisdictional 2006 PM2.5 areas that do
not have adequate or approved 1997
PM2.5 SIP budgets. Part 2 of this
guidance describes how conformity
would be implemented in all 2006 PM2.5
areas before adequate or approved SIP
budgets are available for an applicable
NAAQS. Part 3 of this guidance is
relevant for meeting conformity
requirements once adequate or
approved 2006 PM2.5 SIP budgets are
available.
For example, Part 3 of this guidance
describes how a state or MPO in a multistate nonattainment area can operate
independently from other states/MPOs
for conformity purposes once adequate
or approved SIP budgets for a state are
established. This same conformity
guidance also applies for the 2006 PM2.5
NAAQS in these types of areas. Part 3
applies to the cases where subarea
budgets are established for a
nonattainment area within one state
with multiple MPOs. For further
information, please refer to EPA’s 2004
multi-jurisdictional conformity
guidance.
1. Description of Final Rule
Once a SIP for the 2006 PM2.5 NAAQS
is submitted with budget(s) that EPA
has found adequate or approved, the
budget test must be used in accordance
with 40 CFR 93.118 to complete all
applicable regional emissions analyses
for the 2006 PM2.5 NAAQS. Conformity
is demonstrated if the transportation
system emissions reflecting the
proposed transportation plan, TIP, or
project not from a conforming
transportation plan and TIP were less
than or equal to the motor vehicle
emissions budget level defined by the
SIP as being consistent with CAA
requirements.
The first submitted SIP for the 2006
PM2.5 NAAQS may be an attainment
demonstration or a maintenance plan.
Nonattainment areas for the 2006 PM2.5
NAAQS could also voluntarily choose
to submit an ‘‘early progress SIP’’ to
establish budgets for conformity
purposes prior to required SIPs. See
Section V. for further details on
requirements for early progress SIPs.
EPA has discussed this option in past
conformity rule preamble, e.g. the July
1, 2004 transportation conformity final
rule (69 FR 40028), and some states
have established early progress SIP
budgets for conformity purposes.
Whatever the case, interim emissions
tests and/or any existing 1997 PM2.5 SIP
budget would no longer be used for
conformity in 2006 PM2.5 areas for direct
PM2.5 or a relevant precursor once an
adequate or approved SIP budget for the
2006 PM2.5 NAAQS is established for
the pollutant or precursor. Once a SIP
budget for the 2006 PM2.5 NAAQS is
adequate or approved, the budget test
for 2006 PM2.5 conformity would be
done based on 24-hour emissions (i.e.,
tons per day). As noted earlier in
Section III.D., areas that were also
designated for the 1997 PM2.5 NAAQS
would continue to meet their existing
conformity requirements for the 1997
PM2.5 NAAQS, which would include a
regional emissions analysis based on
annual emissions (i.e., tons per year).
The conformity rule at 40 CFR 93.105
requires consultation on the
development of SIPs; EPA encourages
states to consult with MPOs, state and
local transportation agencies, and local
air quality agencies sufficiently early
VI. Regional Conformity Tests in 2006
PM2.5 Areas That Have Adequate or
Approved 1997 PM2.5 SIP Budgets
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This section describes the conformity
tests required for completing regional
emissions analyses in areas designated
for the 2006 PM2.5 NAAQS that have
adequate or approved SIP budgets for
the 1997 PM2.5 NAAQS that cover either
part or all of the 2006 PM2.5 area. The
36 ‘‘Companion Guidance for the July 1, 2004,
Final Transportation Conformity Rule: Conformity
Implementation in Multi-Jurisdictional
Nonattainment and Maintenance Areas for Existing
and New Air Quality Standard,’’ EPA420–B–04–
012, July 2004, found on EPA’s Web site at
https://www.epa.gov/otaq/stateresources/transconf/
policy/420b04012.pdf.
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when developing 2006 PM2.5 SIPs to
facilitate future conformity
determinations. Once EPA’s
nonattainment designations are
finalized, EPA Regions would be
available to assist states in developing
early progress SIPs for the 2006 PM2.5
NAAQS, if desired.
2. Rationale and Response to Comments
EPA’s rationale for the use of the
budget test once adequate or approved
SIP budgets addressing the 2006 PM2.5
NAAQS are available, and the summary
of comments received on this provision,
is found in Section V.A.2. of this
preamble. It is not repeated here.
B. Conformity Before 2006 PM2.5 SIP
Budgets Are Adequate or Approved
1. Description of the Final Rule
This portion of the final rule is for
completing conformity under the 2006
PM2.5 NAAQS before 2006 PM2.5 SIP
budgets are established. For areas
designated nonattainment for the 2006
PM2.5 NAAQS where all, or a portion, of
the area is covered by adequate or
approved 1997 PM2.5 SIP budgets, the
1997 PM2.5 SIP budgets serve as the
surrogate for budgets for the 2006 PM2.5
NAAQS until the point when 2006
PM2.5 SIP budgets are adequate or
approved. The interagency consultation
process should be used if there are
questions about what adequate or
approved budgets are established in an
area’s 1997 PM2.5 SIP. In addition, in the
case where the 1997 budget does not
cover the entire 2006 PM2.5 area, one of
the interim emissions tests must also be
used, as described below. Section IV. of
today’s rule covers the baseline year to
be used for the baseline year interim
emissions test and Section V. covers
interim emissions tests in 2006 PM2.5
areas before adequate or approved SIP
budgets for the 2006 PM2.5 NAAQS are
available.
Many nonattainment areas for the
1997 PM2.5 NAAQS may have adequate
or approved SIP budgets for the 1997
annual PM2.5 NAAQS. For areas that use
annual PM2.5 budgets to meet 2006
PM2.5 requirements, a regional
emissions analysis would be done based
on an analysis of annual, rather than 24hour, emissions (i.e., tons per year).
The final rule creates a new provision
in § 93.109(k) that covers the four
possible scenarios that could result
when areas are designated
nonattainment for the 2006 PM2.5
NAAQS:
• Scenario 1: the 2006 PM2.5 area
nonattainment boundary is the same as
the 1997 PM2.5 area boundary.
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• Scenario 2: the 2006 PM2.5 area is
smaller than (and completely within)
the 1997 PM2.5 area boundary.
• Scenario 3: the 2006 PM2.5 area is
larger than (and contains) the 1997
PM2.5 area boundary.
• Scenario 4: the 2006 PM2.5 area
boundary overlaps with a portion of the
1997 PM2.5 area boundary.
Most of the 2006 PM2.5 areas that are
also designated for the 1997 PM2.5
NAAQS are Scenario 1 areas; there are
areas that belong to Scenarios 2 and 3
as well. EPA is including rules for all
four scenarios for the sake of
completeness.37 The following
paragraphs describe today’s rule
provisions for each possible scenario for
2006 PM2.5 nonattainment areas.
Scenario 1: 2006 PM2.5 areas where
the nonattainment boundary is exactly
the same as the 1997 PM2.5 boundary. In
this case, the 2006 and 1997 PM2.5
nonattainment boundaries cover exactly
the same geographic area. Such areas
must meet the budget test for the 2006
PM2.5 NAAQS using existing adequate
or approved SIP budgets for the 1997
PM2.5 NAAQS.
Scenario 2: 2006 PM2.5 areas where
the boundary is smaller than and within
the 1997 PM2.5 boundary. In this case,
the 2006 PM2.5 nonattainment area is
smaller than and completely
encompassed by the 1997 PM2.5
nonattainment boundary. Such areas
must meet one of the following versions
of the budget test:
• The budget test using the subset or
portion of existing adequate or approved
1997 PM2.5 SIP budgets that applies to
the 2006 PM2.5 nonattainment area,
where such portion(s) can be
appropriately identified; or
• The budget test using the existing
adequate or approved 1997 PM2.5 SIP
budgets for the entire 1997 PM2.5
nonattainment area. In this case, any
additional reductions beyond those
addressed by control measures in the
1997 PM2.5 SIP would be required to
37 Today’s final rule is based on EPA’s experience
in establishing conformity requirements for areas
designated for the 1997 8-hour ozone NAAQS that
had SIP budgets for the 1-hour ozone NAAQS,
found in 40 CFR 93.109(e)(2). The four boundary
scenarios are the same as the four boundary
scenarios EPA described for the 1997 8-hour ozone
areas that had existing 1-hour ozone budgets. EPA’s
2004 guidance entitled, ‘‘Companion Guidance for
the July 1, 2004 Final Transportation Conformity
Rule, Conformity Implementation in MultiJurisdictional Nonattainment and Maintenance
Areas for Existing and New Air Quality Standards,’’
(EPA420–B–04–012), contains diagrams of the four
scenarios for 8-hour ozone areas. Readers may be
interested in reviewing these diagrams as they read
the following description of the regulation. This
document can be found on EPA’s transportation
conformity website at: https://www.epa.gov/otaq/
stateresources/transconf/policy/420b04012.pdf.
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come from the 2006 PM2.5
nonattainment area as described below.
Under today’s rule, areas could
choose either test each time they make
a conformity determination. For any
particular conformity determination,
however, the same choice would have to
be used for each analysis year. EPA
believes that to do otherwise would be
unnecessarily complicated and may
indicate that one test option used
consistently for all analysis years would
not demonstrate conformity. The
consultation process must be used to
determine whether using a portion of a
1997 PM2.5 SIP budget is appropriate
and feasible, and if so, how deriving
such a portion would be accomplished.
See the preamble of the July 1, 2004
final rule (69 FR 40022–40023) for a
description of a similar provision for the
1997 8-hour ozone NAAQS.
A conformity determination using the
entire 1997 PM2.5 budget would have to
include a comparison between the onroad regional emissions produced in the
entire 1997 PM2.5 area and the existing
1997 PM2.5 SIP budget(s). However, if
additional reductions are required to
meet conformity beyond those produced
by control measures in the 1997 PM2.5
SIP budgets, those reductions must be
obtained from within the 2006 PM2.5
nonattainment area only, since the
conformity determination is being made
for the 2006 PM2.5 NAAQS.
Scenario 3: 2006 PM2.5 areas where
the boundary is larger than the 1997
PM2.5 boundary. In this case, an entire
1997 PM2.5 nonattainment or
maintenance area would be within a
larger 2006 PM2.5 nonattainment area
and the 1997 PM2.5 budgets would not
cover the entire 2006 PM2.5
nonattainment area. Such areas are
required to meet one of the following:
• The budget test using the 1997
PM2.5 budget(s) for the 1997 PM2.5 area,
that is, the portion of the 2006 PM2.5
area that lies within the 1997 PM2.5 area
boundary, and one of the interim
emissions tests for either the remaining
portion of the 2006 PM2.5 nonattainment
area, the entire 2006 PM2.5 area, or the
entire portion of the 2006 PM2.5 area
within an individual state, if 1997 PM2.5
budgets are established in each state in
a multi-state area; or
• The budget test using the existing
adequate or approved 1997 PM2.5 SIP
budgets for the entire 2006 PM2.5
nonattainment area.38
The budget test must be completed
according to the requirements in 40 CFR
38 While the existing regulation for 8-hour ozone
areas does not explicitly contain this option, it was
addressed in the preamble to the final rule
addressing 8-hour ozone areas (July 1, 2004, 69 FR
40027).
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93.118, and the interim emissions test
must follow the requirements of 40 CFR
93.119.
Once an area selects a particular
interim emissions test and the
geographic area it will address, the same
test must be used consistently for all
analysis years. The consultation process
must be used to determine which
analysis years should be selected for
regional emissions analyses where the
budget test and interim emissions tests
are used. It may be possible to choose
analysis years that satisfy both the
budget and interim emissions test
requirements for areas using both tests
prior to adequate or approved 2006
PM2.5 SIP budgets being established.
Further information regarding the
implementation of these requirements is
illustrated later in this section.
Scenario 4: 2006 PM2.5 areas where
the boundary partially overlaps a
portion of the 1997 PM2.5 boundary. In
this case, the 1997 and 2006 PM2.5
nonattainment boundaries partially
overlap. As in the case with Scenario 3
areas, the 1997 PM2.5 budgets would not
cover the entire 2006 PM2.5
nonattainment area. However, unlike
Scenario 3 areas, the 2006 area does not
contain the entire 1997 PM2.5
nonattainment or maintenance area.
Therefore, 1997 PM2.5 budgets cannot be
the sole test of conformity for the 2006
PM2.5 NAAQS, since a conformity
determination must include a regional
emissions analysis that includes the
entire 2006 PM2.5 nonattainment area.
The 2006 PM2.5 areas covered under
this scenario must use the 1997 PM2.5
budget(s) to meet the budget test for the
portion of the 1997 PM2.5 area and
budgets that overlap with the 2006
PM2.5 area boundary, and one of the
interim emissions tests for either the
remaining portion of the 2006 PM2.5
nonattainment area, the entire 2006
PM2.5 area, or the entire portion of the
2006 PM2.5 area within an individual
state, if 1997 PM2.5 budgets are
established in each state in a multi-state
area. Under this final rule, the budget
test must be completed according to the
requirements in 40 CFR 93.118, and the
interim emissions test must follow the
requirements of 40 CFR 93.119.
Similar to Scenario 3 areas, once an
area selects a particular interim
emissions test and the geographic area
it will address, the same test must be
used consistently for all analysis years.
Further information regarding the
implementation of these requirements is
found in the discussion above for
Scenario 3, and illustrated later in this
section.
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2. Rationale and Response to Comments
General. EPA believes that using the
existing 1997 PM2.5 budgets as a
surrogate for the 2006 PM2.5 NAAQS is
required by the CAA. In Environmental
Defense v. EPA, 467 F.3d 1329 (D.C. Cir.
2006), the Court of Appeals for the
District of Columbia Circuit held that
where a motor vehicle emissions budget
developed for the revoked 1-hour ozone
NAAQS existed in an approved SIP, that
budget must be used to demonstrate
conformity to the 8-hour ozone NAAQS
until the SIP is revised to include
budgets for the new NAAQS. EPA
reflected the court’s decision for ozone
conformity tests in its January 24, 2008
final rule (73 FR 4434).
While the Environmental Defense
case concerned ozone, EPA believes the
court’s holding is relevant for other
pollutants for which conformity must be
demonstrated. Consequently, EPA
believes that 2006 PM2.5 areas that have
1997 PM2.5 budgets must use them for
2006 PM2.5 conformity before 2006
PM2.5 SIP budgets are established.
The use of the 1997 PM2.5 budgets as
a surrogate for the 2006 PM2.5 NAAQS
also would ensure that CAA
requirements are met. Section 176(c) of
the CAA requires that transportation
activities may not cause or contribute to
new violations, worsen existing
violations, or delay timely attainment or
any interim milestones. In these areas,
the budgets for the 1997 annual PM2.5
NAAQS have been the measure of PM2.5
conformity thus far, and have been
consistent with these areas’ PM2.5 air
quality progress to date. Therefore,
using budgets that address the 1997
annual PM2.5 NAAQS where no other
PM2.5 budgets are available ensures that
the requirements of CAA 176(c) are met.
Once 2006 PM2.5 budgets are found
adequate or approved, the budget test
for that NAAQS provides the best means
to determine whether transportation
plans, TIPs, or projects meet CAA
requirements.
The budget test is also a better
environmental measure than the interim
emissions tests when SIP budgets for a
pollutant or precursor are available. As
EPA reiterated in its July 1, 2004 final
rule (69 FR 40026), when motor vehicle
emissions budgets have been
established by SIPs, they provide a more
relevant basis for conformity
determinations than the interim
emissions tests. EPA believes this is true
even though in most cases the budgets
established for the 1997 PM2.5 NAAQS
would address an annual rather than a
24-hour NAAQS. A 1997 PM2.5 budget
represents the state’s best estimate of the
level of permissible PM2.5 emissions
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from the on-road transportation sector
for a particular area. Such a budget is
created based on local information for
that particular area—its population, its
estimated vehicle miles traveled and
other travel data, its transit availability,
its particular vehicle fleet, its local
controls, and so forth. Hence EPA
believes using budgets, designed for
specific areas and based on information
from those specific areas, is preferable
to using either of the more generic
interim emissions tests. The baseline
year and the build/no-build tests are
sufficient for demonstrating conformity
when an area does not have a budget for
a portion of a nonattainment area.
However, these interim emissions tests
usually do not ensure that
transportation emissions promote
progress for the NAAQS to the same
extent that the use of motor vehicle
emissions budgets do.
In addition, using the 1997 PM2.5
budgets for 2006 PM2.5 conformity
purposes may also streamline the
conformity process for areas designated
nonattainment for both the 1997 and
2006 PM2.5 NAAQS. These areas would
already be using 1997 PM2.5 budgets for
conformity of that NAAQS. In areas
where the 1997 and 2006 PM2.5
nonattainment boundaries are the same
(Scenario 1), today’s final rule requires
these areas to meet only one type of
test—the budget test—to demonstrate
conformity for both the 1997 and 2006
PM2.5 NAAQS, although the attainment
year, which is a required analysis year,
will be different for these two NAAQS.
For multi-state 2006 PM2.5
nonattainment areas, today’s final rule
preserves states’ ability to determine
conformity independently from one
another, if a state has already
established budgets for its own state
(and/or MPO(s)) for the 1997 PM2.5
NAAQS. Further explanation and
examples are given below in Section
VI.C.
While today’s final rule concerns the
2006 PM2.5 NAAQS, this same rationale
regarding conformity tests would apply
for future new or revised NAAQS of any
transportation-related criteria pollutant.
Therefore, EPA may amend the rule in
the future to apply the conformity test
language found in today’s § 93.109(j)
and (k) more generally. EPA is not doing
so in today’s final rule as such a
provision was not proposed, and EPA
intends to solicit and consider public
comments on applying this language to
future new or revised NAAQS before
adopting any such provision.
Scenario 1 and 2 areas. Today’s final
rule for conformity in 2006 PM2.5 areas
before budgets that address that NAAQS
are available is largely consistent with
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the process that EPA finalized for 8hour ozone areas designated under the
1997 ozone NAAQS where 1-hour ozone
budgets exist (69 FR 40021–40028).
Requirements for Scenario 1 and 2 areas
are identical to the final rule for these
8-hour ozone areas. Scenario 2 2006
PM2.5 areas also have the choice of
adjusting the existing 1997 PM2.5
budgets for the new geographical area.
As we indicated in the November 5,
2003 proposed rule for the 8-hour ozone
areas (68 FR 62702), using the relevant
portion of existing budgets for purposes
of conducting conformity
determinations for a different NAAQS of
the same pollutant is appropriate since
the budgets for the 1997 PM2.5 NAAQS
would only be used as a surrogate for
the 2006 PM2.5 NAAQS. These 1997
PM2.5 budgets still have to be met in the
1997 PM2.5 areas.
Scenario 3 and 4 areas. Some
Scenario 3 areas and all Scenario 4 areas
must also meet one of the interim
emissions tests, for either the portion of
the 2006 PM2.5 area not covered by the
1997 PM2.5 SIP budgets, the entire PM2.5
area, or the entire portion of the 2006
PM2.5 area within an individual state. As
explained in the November 2003
proposed rule for 8-hour ozone areas (68
FR 62702), in these cases budgets
cannot be the sole test of conformity
because a conformity determination
must include a regional emissions
analysis that covers the entire
nonattainment area.
However, some Scenario 3 areas may
be able to demonstrate conformity
without an interim emissions test.
Scenario 3 PM2.5 areas have an option
that similar 8-hour ozone areas also
have: The entire larger, newly
designated area could meet budgets
established for the smaller, existing
area. In the July 1, 2004 final rule, EPA
clarified that 8-hour ozone areas have
this option. In that final rule, EPA noted
that while this option was not explicitly
addressed by the regulatory text, it is
consistent with the requirements and is
available to interested 8-hour ozone
areas (69 FR 40027).
Finally, EPA believes that statutory
requirements are met under the
proposal to use either interim emissions
test when no adequate or approved
PM2.5 SIP budgets are available. See
further rationale regarding this
flexibility in today’s final rule in
Section V.
EPA did not receive any specific
comments on this portion of the
rulemaking, but one commenter
supported the use of EPA’s 2004 multijurisdictional guidance for 2006 PM2.5
areas. This guidance, discussed further
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below in C.2. of this section, reflects the
requirements finalized today.
2. Cases Involving Multi-Jurisdictional
Areas
C. General Implementation of Regional
Tests
As described earlier, EPA issued a
guidance document in 2004 for
implementing conformity requirements
in multi-jurisdictional areas. There are
two parts of this existing guidance that
are relevant for implementing
conformity for these areas. Part 3 of the
existing guidance describes how
conformity would be implemented in all
2006 PM2.5 areas once adequate or
approved SIP budgets for the 2006 PM2.5
NAAQS are established. Part 4 of this
guidance is relevant for meeting
conformity requirements when only
1997 PM2.5 budgets are available.39
This guidance is also applicable for
conformity purposes in multi-state and
multi-MPO areas. For example, in multistate 2006 PM2.5 nonattainment areas
where each state has its own 1997 PM2.5
SIP budgets, the states could determine
conformity for the 2006 NAAQS (as well
as the 1997 PM2.5 NAAQS)
independently of each other. In
addition, MPOs in areas that have
subarea budgets for the 1997 PM2.5
NAAQS could use these subarea
budgets for conformity to the 2006 PM2.5
NAAQS.
For further information, please refer
to Section V.C. and EPA’s 2004 multijurisdictional conformity guidance.
Today’s final rule applies the existing
conformity rule’s general requirements
for PM2.5 regional emissions analyses to
all 2006 PM2.5 areas. As described in
Section V.C., EPA is including this
discussion of the existing regulation’s
requirements for clarity, to help readers
understand how the existing regulation
would apply to areas designated
nonattainment for the 2006 PM2.5
NAAQS.
The discussion below is intended to
illustrate how today’s rule will be
implemented in practice for 2006 PM2.5
areas with adequate or approved 1997
PM2.5 SIP budgets.
1. Conformity Test Requirements for
Most Areas
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Regional emissions analyses under
today’s final rule must be implemented
through existing conformity
requirements such as 40 CFR 93.118,
93.119, and 93.122. For example, the
conformity rule requires that only
certain years within the transportation
plan (or alternate timeframe) be
examined.
The consultation process must be
used to determine which analysis years
should be selected for regional
emissions analyses for the budget test.
The conformity rule at 40 CFR
93.118(d)(2) requires the following
analysis years for this test:
• The attainment year for the 2006
PM2.5 NAAQS (if it is within the
timeframe of the transportation plan and
conformity determination);
• The last year of the timeframe of the
conformity determination (40 CFR
93.106(d)); and
• Intermediate years as necessary so
that analysis years are no more than ten
years apart.
Areas covered by § 93.109(k) of
today’s final rule will also be
determining conformity for the 1997
PM2.5 NAAQS, using adequate or
approved budgets established for that
NAAQS, although there will be some
differences in analysis years required for
the 2006 and 1997 PM2.5 NAAQS (e.g.,
the attainment year, which is a required
analysis year, will be different for these
two NAAQS).
See the relevant regulatory sections of
the conformity rule and the July 1, 2004
final rule preamble for further
background on how tests have been
implemented for other pollutants and
standards (69 FR 40020).
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VII. Other Conformity Requirements for
2006 PM2.5 Areas
The conformity regulations already
provide the remaining requirements that
are necessary for conformity under the
2006 PM2.5 NAAQS. Any existing
conformity requirements that are listed
for ‘‘PM2.5’’ areas that have not been
revised by today’s final rule apply to
2006 PM2.5 nonattainment or
maintenance areas as well. These
provisions have already been
promulgated, based on past rulemakings
and rationale, and are unchanged by
today’s rule. For example, a hot-spot
analysis is required for certain projects
in any PM2.5 nonattainment and
maintenance areas before such projects
can be found to conform. These
requirements are found in §§ 93.116(a)
and § 93.123(b) of the conformity rule,
although please note that EPA for other
reasons has clarified amendments to
section 93.116(a) in today’s final rule;
see Section IX. The hot-spot analysis
requirements that were promulgated for
‘‘PM2.5’’ areas in the conformity rule did
39 This section of the guidance covers how 8-hour
ozone areas that have 1-hour ozone budgets would
proceed with developing their regional emissions
analyses and making conformity determinations,
which is analogous to any 2006 PM2.5 areas that
have 1997 budgets in the interim.
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not need to be amended to apply to
2006 PM2.5 areas, because they already
apply for this NAAQS.
A hot-spot analysis in an area
designated for both the 1997 and 2006
PM2.5 NAAQS would have to
demonstrate that the project meets the
conformity rule’s hot-spot requirements
for all of the PM2.5 NAAQS for which
the area is designated nonattainment:
• If an area is designated
nonattainment for only the 2006 PM2.5
NAAQS, the analysis would have to
consider only this NAAQS;
• If an area is designated
nonattainment for the 1997 annual
NAAQS and the 2006 24-hour NAAQS,
the analysis would have to consider
both NAAQS;
• If an area is designated
nonattainment for both the 1997 annual
and 1997 24-hour NAAQS, as well as
the 2006 24-hour NAAQS, the analysis
would have to consider all of these
NAAQS.
Please refer to the March 10, 2006
final rule for additional information
regarding hot-spot analyses (47 FR
12468) and EPA and FHWA’s current
guidance for implementing this
requirement (Transportation Conformity
Guidance for Qualitative Hot-spot
Analyses in PM2.5 and PM10
Nonattainment and Maintenance Areas,
March 2006, EPA420–B–06–902). EPA
will also be releasing PM quantitative
hot-spot modeling guidance in the near
future. Please check EPA’s Web site at:
https://www.epa.gov/otaq/
stateresources/transconf/policy.htm.
Section 93.117 of the conformity rule,
which requires project-level conformity
determinations to comply with any
PM2.5 control measures in an approved
SIP, also applies for conformity under
the 2006 PM2.5 NAAQS. Again, EPA
promulgated this requirement in general
for nonattainment and maintenance
areas under the PM2.5 NAAQS. See
EPA’s July 2004 final rule for further
information on this requirement (69 FR
40036–40037).
EPA will work with PM2.5
nonattainment areas as needed to ensure
that state and local agencies can meet
existing and new conformity
requirements for the 2006 PM2.5 NAAQS
in a timely and efficient manner.
VIII. Transportation Conformity in
PM10 Nonattainment and Maintenance
Areas and the Revocation of the Annual
PM10 NAAQS
A. Background
On October 17, 2006, EPA issued a
final rule establishing changes to the
PM2.5 and PM10 NAAQS (71 FR 61144).
The October 2006 final rule retained the
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24-hour PM10 NAAQS of 150 μg/m3, and
revoked the annual PM10 NAAQS of 50
μg/m3. EPA made a commitment in the
October 2006 final rule to provide
information regarding how
transportation conformity will be
implemented under the revised PM10
NAAQS (71 FR 61215). To satisfy this
commitment, EPA described which
conformity tests would apply in PM10
nonattainment and maintenance areas
(‘‘PM10 areas’’) in a guidance
document.40 Today’s final rule updates
the conformity rule in response to this
commitment.
CAA section 176(c)(5) requires
conformity only in areas that are
designated nonattainment or
maintenance for a given pollutant and
NAAQS. Therefore, transportation
conformity has continued to apply to all
PM10 nonattainment and maintenance
areas because transportation conformity
applies based on an area’s status as a
nonattainment or maintenance area, and
PM10 designations were not affected by
the October 2006 final rule. As stated in
the October 2006 final rule, ‘‘both
transportation and general conformity
will continue to apply to all PM10
nonattainment and maintenance areas
since no designations are changing’’ (71
FR 61215).
As of the effective date of the October
2006 rule, conformity determinations in
PM10 areas have been required only for
the 24-hour PM10 NAAQS. The October
2006 final rule stated, ‘‘However,
because EPA is revoking the annual
PM10 NAAQS in this final rule, after the
effective date of this rule conformity
determinations in PM10 areas will only
be required for the 24-hour PM10
NAAQS; conformity to the annual PM10
NAAQS will no longer be required’’ (71
FR 61215). Please refer to the October
17, 2006 final rule for additional
information (71 FR 61144).
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B. Description of the Final Rule
EPA has added two new definitions to
40 CFR 93.101 of the conformity rule to
distinguish between the 24-hour PM10
NAAQS and the annual PM10 NAAQS.
EPA has also updated 40 CFR 93.109(g)
so that:
• PM10 areas that have adequate or
approved SIP budgets for both the 24hour and annual PM10 NAAQS are
required to use only the budgets
established for the 24-hour PM10
NAAQS. Conformity to the annual PM10
40 Transportation
Conformity in PM10
Nonattainment and Maintenance Areas and the
Revocation of the Annual PM10 Standard,
September 25, 2008, found on EPA’s Web site at:
https://www.epa.gov/otaq./stateresources/transconf/
policy.htm.
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budgets in such a case is no longer
required.
• PM10 areas that have adequate or
approved SIP budgets for only the
annual PM10 NAAQS are required to use
them for PM10 conformity
determinations until PM10 SIP budgets
for the 24-hour PM10 NAAQS are found
adequate or approved. For areas that use
annual PM10 budgets, a regional
emissions analysis must be done based
on an analysis of annual, rather than 24hour, emissions.
No other conformity requirements for
PM10 nonattainment and maintenance
areas have been changed by the final
rule. For example, the requirement for
project-level conformity determinations
in PM10 areas continues to apply,
including hot-spot analyses in some
cases (see §§ 93.116(a) and 93.123(b)).
Although project-level conformity
requirements and any required hot-spot
analyses apply only with respect to the
24-hour PM10 NAAQS, this requires no
revisions to the conformity rule to
implement.
Where an area has adequate or
approved PM10 budgets for both the
annual and 24-hour PM10 NAAQS, it is
not necessary to remove the annual
PM10 NAAQS budgets from the SIP.
Such annual budgets do not apply for
conformity purposes if an area has
budgets for the 24-hour PM10 NAAQS.
However, states can choose to revise
such SIPs to remove any annual PM10
budgets, since this NAAQS has been
revoked and remaining 24-hour PM10
budgets ensure that anti-backsliding SIP
requirements are met.
C. Rationale and Response to Comments
Today’s update to the rule for PM10
conformity tests results from the
revocation of the annual PM10 NAAQS.
In areas where annual PM10 budgets are
the only PM10 budgets that are adequate
or approved, EPA believes it is
necessary to use such budgets to
demonstrate conformity for the 24-hour
PM10 NAAQS to meet CAA
requirements. As discussed above in
Section VI.B.2., a 2006 decision by the
Court of Appeals for the DC Circuit
clarified this point. In this decision, the
court stated, ‘‘A current SIP, even one
tied to outdated NAAQS, remains in
force until replaced by another but laterapproved SIP. The CAA provides that
the current SIPs are legally sufficient
until they are replaced by new SIPs.’’
(Environmental Defense v. EPA, 467
F.3d 1329, 1335 (DC Cir. 2006)). Refer
to Section VI.B.2. for further
information about the decision. EPA
believes that today’s final rule is
consistent with this decision.
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Consequently, EPA believes that
annual PM10 budgets must be used to
demonstrate conformity for the 24-hour
PM10 NAAQS when adequate or
approved 24-hour PM10 budgets are not
yet established. In areas with PM10
budgets that address only the annual
PM10 NAAQS, these budgets have been
the measure of PM10 conformity thus
far, and have been consistent with these
areas’ PM10 air quality progress to date.
Therefore, using annual PM10 budgets
where no other PM10 SIP budgets are
available ensures that air quality
progress to date is maintained, air
quality will not be worsened and
attainment and any interim milestones
for the 24-hour PM10 NAAQS will not
be delayed because of emissions
increases. Once 24-hour PM10 budgets
are found adequate or approved, the
budget test using only the budgets for
the 24-hour PM10 NAAQS provides the
best means to determine whether
transportation plans, TIPs, or projects
meet CAA conformity requirements.
Most PM10 areas already have
adequate or approved budgets for only
the 24-hour PM10 NAAQS. However,
there are a limited number of PM10 areas
that have SIP budgets only for the
annual PM10 NAAQS. EPA believes that
the statute as interpreted by the court
requires such areas to continue to use
these adequate or approved annual PM10
SIP budgets, rather than use one of the
interim emissions tests in 40 CFR
93.119(d) which could be less
environmentally protective tests than
SIP budgets.
While EPA addressed how the
revocation affected PM10 transportation
conformity requirements in its
September 2008 guidance, updating the
regulation clarifies the requirements and
simplifies implementation. This final
rule also saves resources in some areas
with adequate or approved SIP budgets
for both the 24-hour and annual PM10
NAAQS because these areas are no
longer required to use budgets for the
annual PM10 NAAQS. As mentioned
above, today’s minor revision to the
conformity rule is consistent with what
is already required in the field for PM10
nonattainment and maintenance areas.
EPA received one comment
supporting this rule change and no
comments opposing it.
IX. Response to the December 2007 HotSpot Court Decision
A. Background
EPA promulgated a final rule on
March 10, 2006 (71 FR 12468) that
revised the previous PM10 conformity
hot-spot analysis requirements and
applied these revised requirements to
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PM2.5.41 A hot-spot analysis is defined
in 40 CFR 93.101 as an estimation of
likely future localized pollutant
concentrations and a comparison of
those concentrations to relevant
NAAQS. A hot-spot analysis assesses
the air quality impacts of an individual
transportation project on a scale smaller
than a regional emissions analysis for an
entire nonattainment or maintenance
area.
Prior to today, section 93.116(a) of the
conformity rule read: ‘‘* * * The
FHWA/FTA project must not cause or
contribute to any new localized CO,
PM10, and/or PM2.5 violations or
increase the frequency or severity of any
existing CO, PM10, and/or PM2.5
violations * * *.’’ These requirements
continue to apply in today’s rule, and
are satisfied for applicable projects 42 ‘‘if
it is demonstrated that during the time
frame of the transportation plan no new
local violations will be created and the
severity or number of existing violations
will not be increased as a result of the
project.’’ Sections 93.105(c)(1)(i) and
93.123 contain the consultation and
methodology requirements for
conducting hot-spot analyses.
A hot-spot analysis, when required, is
only one part of a project-level
conformity determination. In order to
meet all CAA requirements, an
individual project must also be included
in a conforming transportation plan and
TIP (and regional emissions analysis for
the entire nonattainment or
maintenance area) and meet any other
applicable requirements.
Environmental petitioners challenged
the March 2006 final rule, and raised
several issues related to it. First,
petitioners alleged that the final rule did
not ensure that transportation projects
complied with CAA section 176(c)(1)(A)
and (c)(1)(B)(iii). Second, petitioners
alleged that EPA had previously
approved its MOBILE6.2 on-road mobile
source emissions model for use in
quantitative PM2.5 and PM10 hot-spot
analyses, and withdrew such approval
in the March 2006 final rule without
providing adequate notice and
opportunity for public comment.43
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41 The
March 10, 2006 rule constituted final
action on EPA’s original proposal from November
5, 2003 (68 FR 62690, 62712) and a supplemental
proposal from December 13, 2004 (69 FR 72140,
72144–45, and 72149–50).
42 Section 93.123(b) contains the types of projects
for which a hot-spot analysis applies in PM2.5 and
PM10 areas. For additional discussion, please refer
to ‘‘V. Projects of Air Quality Concern and General
Requirements for PM2.5 and PM10 Hot-Spot
Analyses’’ in the preamble of the March 10, 2006
final rule at 71 FR 12490–12498.
43 EPA and petitioners settled a third issue that
was not raised to the court. The settlement was
finalized on June 22, 2007 (72 FR 34460), and
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On December 11, 2007, the D.C.
Circuit Court of Appeals issued its
decision, and upheld EPA’s March 2006
final rule and remanded one issue for
clarification. Environmental Defense v.
EPA, 509 F.3d. 553 (D.C. Cir. 2007). The
court agreed with EPA’s position that
CAA section 176(c)(1)(A) does not
require that an individual transportation
project reduce emissions, but only that
such a project not worsen air quality
compared to what would have
otherwise occurred if the project was
not implemented. The court held that,
assuming section 176(c)(1)(A) applies in
the local area surrounding an individual
project, EPA’s position that this
provision is met if a transportation
project conforms to the emissions
estimates and control requirements of
the SIP was a reasonable one. The court
also rejected petitioners’ arguments
regarding MOBILE6.2 and found that
EPA had in fact provided adequate
notice and comment on its decision not
to require quantitative PM hot-spot
analyses using MOBILE6.2 due to the
model’s technical limitations at the
project-level (71 FR 12498–12502).
However, the court remanded one
issue to EPA for further explanation of
the Agency’s interpretation of CAA
section 176(c)(1)(B)(iii). The court
instructed EPA on remand to interpret
how this provision of the Act is met
within the local area affected by an
individual project, or explain why this
statutory provision does not apply
within such an area. Today’s final rule
responds to this part of the court’s
decision.
B. Description of the Final Rule
EPA has made two changes to section
93.116(a) of the conformity rule to
address the court’s remand. First, EPA
is explicitly stating in this provision
that federally funded or approved
highway and transit projects in PM2.5
and PM10 nonattainment and
maintenance areas must meet the
requirements of CAA section
176(c)(1)(B)(iii) within the local area
affected by the project. That is,
§ 93.116(a) now expressly says that
project must not delay timely
attainment or any interim milestones.
EPA has also explicitly stated in
§ 93.116 the requirement that projects
must be included in a regional
emissions analysis under 40 CFR 93.118
or 93.119. Consistent with the court’s
decision, as explained below, EPA is not
requiring an individual project to
described a stakeholder process that EPA will use
to develop its future PM2.5 and PM10 quantitative
hot-spot modeling guidance.
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reduce emissions in the local project
area.
These revisions are intended to clarify
and make more explicit EPA’s
longstanding interpretation of the CAA
as it applies to hot-spot analyses, and do
not reflect any substantive changes to
existing requirements for project-level
conformity determinations. Under
today’s final rule, project-level
conformity determinations, including
any hot-spot analyses, will continue to
be performed in the same manner as
current practice. Projects will continue
to be required to be a part of a regional
emissions analysis that supports a
conforming transportation plan and TIP.
Hot-spot analyses will need to
demonstrate that during the time frame
of the transportation plan no new local
violations would be created and the
severity or number of existing violations
would not be increased as a result of a
new project. By making these
demonstrations, it can be assured that
the project would not delay timely
attainment or any required interim
reductions or milestones, as described
further below. In addition, project
sponsors must continue to document
the hot-spot analysis as part of the
project-level conformity determination,
and the public continues to be able to
comment on any aspects of the
conformity determination through
existing public involvement
requirements.
EPA notes that today’s final rule also
addresses new projects in CO
nonattainment and maintenance areas,
since the hot-spot analysis requirements
in section 93.116(a) also apply to such
areas. Although the March 2006 final
rule and the December 2007 court case
did not involve CO hot-spot
requirements, EPA believes it is
appropriate to clarify that CAA section
176(c)(1)(B)(iii) must also be met for
projects in CO nonattainment and
maintenance areas.
C. Rationale and Response to Comments
1. General
Project-level conformity
determinations must demonstrate that
all of the requirements in CAA section
176(c)(1)(B) are met. Section
176(c)(1)(B) defines conformity to a SIP
to mean ‘‘that such activities will not (i)
cause or contribute to any new violation
of any NAAQS in any area; (ii) increase
the frequency or severity of any existing
violation of any NAAQS in any area; or
(iii) delay timely attainment of any
NAAQS or any required interim
emission reductions or other milestones
in any area.’’
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In Environmental Defense, the court
held that EPA did not adequately
explain how it interpreted the language
of CAA section 176(c)(1)(B)(iii) in
conjunction with related language in
sections 176(c)(1)(B)(i) and (ii). The
court stated that, if ‘‘any area’’ in the first
two provisions refers to a ‘‘local area,’’
then EPA must either interpret the term
‘‘any area’’ in section 176(c)(1)(B)(iii) to
also mean ‘‘local area,’’ or explain why
a different interpretation is reasonable.
509 F.3d at 560–61. EPA believes that
‘‘any area’’ as used in the first two
provisions does include local areas, and
that the same interpretation should
apply to the third provision as well;
therefore all of section 176(c)(1)(B)
requirements must be met in the local
project area.
EPA believes that its conformity hotspot regulations, as well as other
conformity requirements, already
require that individual projects comply
with section 176(c)(1)(B)(iii) in the local
project area. EPA has always intended
the term ‘‘any area’’ in all three statutory
provisions of section 176(c)(1)(B) to
include the local area affected by the
emissions produced by a new project.
For example, as EPA stated in the March
2006 final hot-spot rule (71 FR 12483),
‘‘a regional emissions analysis for an
area’s entire planned transportation
system is not sufficient to ensure that
individual projects meet the
requirements of section 176(c)(1)(B)
where projects could have a localized
air quality impact.’’
To implement section 176(c)(1)(B)
requirements in PM2.5, PM10, and CO
nonattainment and maintenance areas
(40 CFR 93.109(b)), EPA’s conformity
rule has required and continues to
require project-level conformity
determinations to address the regional
and local emissions impacts from new
projects. Section 93.115(a) of the
conformity rule requires that an
individual project must be consistent
with the emissions projections and
control measures in the SIP, either by
inclusion in a conforming transportation
plan and TIP or through a separate
demonstration (and regional emissions
analysis developed under 40 CFR
93.118 or 93.119). In addition, section
93.116(a) requires that some projectlevel conformity determinations include
a hot-spot analysis that demonstrates
emissions from a single project do not
negatively impact air quality within the
area substantially affected by the
project.44 EPA concludes that through
44 Hot-spot analyses must be based on the latest
data and models under 40 CFR 93.109(b), 93.111,
and 93.123, and therefore any growth in other
emissions sources or the impact of new or existing
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meeting all of these requirements, it can
be assured that a project does not cause
or contribute to a new violation, worsen
a violation, or delay timely attainment
or any interim milestones.
However, in light of the court’s
request for further explanation, today’s
rule specifically clarifies that the term
‘‘any area’’ in CAA section 176(c)(1)(B)
applies to any portion of a
nonattainment or maintenance area,
including the local area affected by a
transportation project. Today’s final rule
thus ensures that transportation
planners address the requirement that
there be no delay in timely attainment
or any interim milestones in the local
project area.
EPA notes that CAA section
176(c)(1)(B)(iii) does not require that
transportation activities provide
additional emissions reductions in a
local project area in order to meet the
requirement not to delay timely
attainment or any interim milestones.
EPA explained this interpretation in the
preamble to its March 2006 hot-spot
regulations (71 FR 12482), and the court
upheld this interpretation in
Environmental Defense v. EPA (509 F.3d
553, 560 (D.C. Cir. 2007). See also
Environmental Defense v. EPA, 467 F.3d
1329, 1337 (DC Cir. 2006) (‘‘EPA argues,
and we agree, that conformity to a SIP
can be demonstrated by using the build/
no-build test, even if individual
transportation plans do not actively
reduce emissions’’). CAA section
176(c)(1)(B)(iii) does not require a new
project to mitigate new or worsened air
quality violations that it does not cause.
This statutory provision also does not
require a new project to contribute new
interim reductions beyond those that are
already required in the SIP. Rather, the
hot-spot determination must instead
conclude that the new project, in
conjunction with all other emissions
increases and decreases in the local
project area, is consistent with the
emissions budgets in the SIP and does
not produce any new or worsen any
existing violations.
The only case where Congress
specifically required individual projects
to provide emission reductions in hotspot analyses is for projects in certain
CO nonattainment areas. CAA section
176(c)(3)(B)(ii) requires individual
projects in CO nonattainment areas to
‘‘eliminate or reduce the severity and
number of violations of the carbon
monoxide NAAQS in areas substantially
emissions controls (including those in any required
SIP) would always be considered in a hot-spot
analysis prior to approving a project.
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affected by the project.’’ 45 Since
Congress did not establish such a
requirement for any project in PM2.5 and
PM10 areas under section
176(c)(3)(B)(ii), and for the reasons
described in today’s final rule, EPA does
not interpret such a requirement to
apply to projects in PM2.5 or PM10 areas
under section 176(c)(1)(B)(iii).
Some commenters supported EPA’s
interpretation, while others disagreed.
The other commenters believed that,
despite the court’s decision, a project
should not be allowed to proceed unless
it reduces emissions sufficient to offset
emissions from other sources that
negatively impact meeting the NAAQS.
Commenters thought today’s rule would
allow a project to conform even when
there are NAAQS violations after the
attainment date and that EPA’s rule
eliminates the opportunity to identify
and remedy violations.
The commenters’ argument—that
section 176(c)(1)(B)(iii) requires
transportation projects to reduce
emissions in the area affected by the
project—has been raised in earlier
transportation conformity rulemakings
and repeatedly rejected by the D.C.
Circuit Court of Appeals. In
Environmental Defense Fund v. EPA,
the court explained that ‘‘[a]lthough the
Act states that SIPs must reduce
violations, and therefore emissions, it is
notably silent on whether transportation
plans themselves, which are but one
part of the SIP, must reduce emissions.’’
467 F.3d 1329, 1338 (D.C. Cir. 2006)
(emphasis in original). The court went
on to uphold as reasonable EPA’s
interpretation that individual
transportation plans need not reduce
emissions to comply with the statutory
requirement to conform to the SIP. Id.
In the 2006 EDF decision, the court also
referred to its earlier decision in
Environmental Defense Fund v. EPA, 82
F.3d. 451 (D.C. Cir. 1996), in which it
rejected a challenge to EPA’s 1993
conformity regulations for similar
reasons. In the 2006 EDF decision, the
court noted that it had previously
decided a similar issue in the 1996 EDF
opinion, in which it ‘‘agreed with EPA
‘that plans and improvement programs
may contribute to emissions reductions
by avoiding or reducing increases in
emissions over the years,’ because
although the statute ‘require[d]
reductions in [several pollutants],’ it
‘d[id] not require that the emissions
come entirely from mobile sources’[.]’’
EDF v. EPA, 467 F.3d at 1338. Thus, the
2006 EDF decision was the second time
the D.C. Circuit rejected the same
45 This requirement is in section 93.116(b) of the
conformity rule.
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argument commenters raise here. The
fact that the 1996 and 2006 D.C. Circuit
decisions addressed transportation
plans and TIPs, rather than individual
projects, is not relevant because the
court’s analysis of what section
176(c)(1) requires applies equally to
transportation plans, TIPs, and
individual projects, since section 176(c)
imposes the same requirements for all
three, and contains no additional or
different requirements for individual
projects.
In its 2007 decision in Environmental
Defense v. EPA, the court for a third
time upheld EPA’s interpretation that a
transportation project that does not
increase violations of the NAAQS
conforms to the SIP’s purpose of
eliminating or reducing the severity and
number of NAAQS violations and
achieving expeditious attainment of the
NAAQS, even if the project does not
itself achieve emissions reductions. 509
F.3d 553, 560 (DC Cir. 2007). In that
decision, the court did remand to EPA
for further explanation the issue of
whether section 176(c)(1)(B)(iii) applies
to hot-spot analyses, and if it does, how
its conditions are to be met. Today’s
final rule responds to that remand. As
explained below, EPA interprets section
176(c)(1)(B)(iii) as applying to hot-spot
analyses, and the requirements of the
regulations as amended in today’s
action will ensure that transportation
projects do not interfere with timely
attainment of the NAAQS or any interim
milestones.
Section 176(c)(1) prohibits federal
agencies from supporting, providing
financial assistance for, licensing,
permitting, or approving any activity
that does not conform to an approved
SIP. This provision defines ‘‘conformity
to a SIP’’ to mean (1) conformity to the
SIP’s purpose of eliminating or reducing
the severity and number of NAAQS
violations and achieving expeditious
attainment of the NAAQS, (2) that the
activity will not cause or contribute to
any new violation of the NAAQS in any
area, (3) that the activity will not
increase the frequency or severity of any
existing NAAQS violation in any area,
and (4) that the activity will not delay
timely attainment of any NAAQS or
interim milestones. Commenters focus
on the fourth requirement above—that
an activity will not delay timely
attainment of any NAAQS or any
interim milestones—to support their
argument that EPA’s May 2009 proposal
is inconsistent with the CAA because it
would allow a new or expanded
transportation project to conform to the
SIP if the project does not achieve
attainment of the NAAQS. EPA
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disagrees with the commenters’
assertion.
EPA first notes that two of the four
elements in the statutory definition of
‘‘conformity to an implementation plan’’
contain some redundancy. Section
176(c)(1)(A) states that ‘‘conformity to an
implementation plan’’ means conformity
to the SIP’s purpose of eliminating or
reducing the severity and number of
NAAQS violations and achieving
expeditious attainment of the NAAQS.
Section 176(c)(1)(B)(iii) states that
conformity to the SIP means that the
transportation activity will not delay
timely attainment of the NAAQS or any
interim milestones. Both of these
criteria seek to ensure attainment of the
SIP in a timely manner—by requiring
that projects not delay timely attainment
or any interim milestones in any area
and thereby ensuring expeditious
attainment of the NAAQS. If a project
conforms to the SIP’s purpose of
achieving expeditious attainment of the
NAAQS, it cannot be delaying timely
attainment of the NAAQS, since
‘‘expeditious attainment’’ would require
attainment at least as early as would
‘‘timely attainment.’’ ‘‘Expeditious’’
means ‘‘characterized by speed and
efficiency,’’ whereas ‘‘timely’’ is defined
as ‘‘before a time limit expires’’ or ‘‘done
or happening at the appropriate or
proper time.’’ 46 Thus, EPA is not
reading section 176(c)(1)(B)(iii) out of
the statute, as commenters assert, but is
instead reading it in conjunction with a
closely related provision which also
addresses projects’ relationship to
attainment of the NAAQS.
Further, the regulatory requirements
for hot-spot analyses meet the
requirement that a project not delay
timely attainment of the NAAQS or any
interim milestones. See 40 CFR
93.123(c). The hot-spot analysis must
evaluate air quality concentrations
resulting from emissions from the
project and the future background
pollutant concentrations. Such
concentrations must be examined at
receptor locations in the localized area
substantially affected by the project.
Future background concentrations at the
project location are based on either
available monitoring data near the
project location, or when such
information is not available, the latest
information must be used as determined
through the interagency consultation
process (40 CFR 93.105(c)(1)(i)). Based
on a review of the available data, the
hot-spot analysis must include future
expected air quality concentrations at
the project location. The concentrations
46 Definitions from Webster’s On-line Dictionary,
see https://www.websters-online-dictionary.org/.
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must then be compared to the NAAQS
and the project will conform to the SIP
only if it can be shown that the project
does not cause or contribute to any new
localized violations, increase the
frequency or severity of any existing
violations, or delay timely attainment of
any NAAQS or any interim milestones.
See 40 CFR 93.116(a). The fact that the
regulations provide that these criteria
are met if, during the time frame of the
transportation plan, (1) no new local
violations will be created, (2) the
severity or number of existing violations
will not be increased as a result of the
project, and (3) the project has been
included in a regional emissions
analysis that meets applicable §§ 93.118
and/or 93.119 requirements does not
mean that the project may delay timely
attainment of the NAAQS and still be
found to conform.
Specifically, commenters assert that
the requirement that a project must be
included in a regional emissions
analysis does not suffice to ensure that
it will not delay timely attainment of the
NAAQS, because the regional emissions
analysis is based on the approved SIP,
and EPA’s SIP guidance does not
require states to model the incremental
impact of highway emissions in the
ambient air near highways or to develop
control strategies to remedy nearhighway NAAQS violations.
Commenters assert that only if EPA
were to modify its SIP guidance
accordingly would it be reasonable to
interpret section 176(c)(1)(B)(iii) as EPA
has done in the proposed rule.
Commenters also state that section
176(c)(1)(B)(iii) requires some remedial
action to be taken if a NAAQS violation
is projected after the attainment
deadline, even if the project itself does
not adversely affect emissions. EPA
disagrees. First, EPA notes that any
comments requesting that EPA revise its
regulations and/or policies regarding
establishment of the PM2.5 NAAQS,
designation of PM2.5 nonattainment
areas and development of PM2.5 SIPs are
beyond the scope of this rulemaking.
Further, the requirement that a project
is included in a regional emissions
analysis, in conjunction with the other
requirements of § 93.116(a) and the
requirements of § 93.123, is sufficient to
ensure that transportation projects do
not delay timely attainment of the
NAAQS as explained below. And
finally, as described above, the DC
Circuit has already held that a project
need not achieve additional emissions
reductions needed to attain the NAAQS
in order to conform to the SIP.
The approved SIP for a nonattainment
area contains the control measures and
emissions projections that demonstrate
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attainment of the NAAQS by the
required attainment date, including the
motor vehicle emissions budget that
defines the upper limit of transportation
sector emissions above which
attainment could be delayed. Therefore,
a project will not delay attainment
beyond the required date if its
transportation emissions (along with all
other transportation emissions) are
included in a conformity analysis that
meets the SIP budgets in the attainment
year and all other future years.
Commenters point to EPA’s statement in
the preamble to the 2006 PM2.5 hot-spot
rule that PM2.5 SIP modeling is unlikely
to be performed at the level of detail
necessary to identify PM2.5 hot-spots to
support their assertion that EPA cannot
rely on the regional emissions analysis
as part of the hot-spot analysis.
However, that statement in the 2006
preamble is taken out of context by
commenters. The original statement was
part of EPA’s explanation for not
finalizing a proposed option for which
projects need a PM10 or PM2.5 hot-spot
analysis (rather than how the analysis is
actually completed). In the 2006 rule,
EPA did not finalize the proposed
option to require hot-spot analyses only
in the cases where the SIP identifies
projects of local air quality concern.47
The 2006 statement was not, as
suggested by commenters, a judgment
on the value of the regional emissions
analysis that supports a conformity
determination. EPA continues to believe
that regional conformity analyses are
critical to meeting all of section
176(c)(1) requirements for project-level
conformity determinations, in
conjunction with hot-spot analyses of
emissions resulting from the project in
the local affected area along with other
future expected emissions in that area.
Rather, it only indicates EPA’s view that
SIP modeling is unlikely to identify all
locations that warrant a hot-spot
analysis.
Moreover, in addition to
demonstrating that the project is
consistent with the regional emissions
analysis (which supports the budget),
there can be no new local violations and
the severity or number of existing
violations cannot increase as a result of
the project. In practice, EPA’s
regulations will ensure that any project
that creates a new violation or worsens
an existing violation of the NAAQS in
the local area affected by the project
(either by increasing the number of
47 Under 40 CFR 93.123(b)(1), EPA has identified
projects of local air quality concern that require a
localized hot-spot analysis. These projects include
all new or expanded highway projects that have a
significant number of or a significant increase in
diesel vehicles).
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violations or the severity of an existing
violation) will not be found to conform.
A project will be found to conform only
if it is demonstrated that the project will
not adversely impact air quality
concentrations in the affected local area,
and has been included in a regional
emissions analysis that meets the rule’s
conformity test requirements. Therefore,
for the reasons explained above, EPA is
finalizing the proposed regulations,
which will ensure that project-level
conformity determinations will comply
with all the statutory criteria in section
176(c)(1)(A) and (B).
EPA has responded to other
comments related to the hot-spot
provisions at the end of this section,
below.
2. Requirement for No Delay in Timely
Attainment of the NAAQS
The provisions of today’s final rule
clarify that a project will meet CAA
section 176(c)(1)(B)(iii) requirements
not to delay timely attainment as long
as no new or worsened violations are
predicted to occur, which is already
required under the existing hot-spot
requirements. While overall emissions
can increase in a local area above those
expected without a new project’s
implementation, a project will not delay
timely attainment if air quality
concentrations continue to meet federal
air quality NAAQS or any violations of
the NAAQS are not worsened.
Furthermore, in the case where the
analysis shows that air quality
concentrations are above the NAAQS, a
project would not delay timely
attainment if air quality is improved or
unchanged from what would have
occurred without the new project’s
implementation. In other words, even
where air quality concentrations are
above the NAAQS, a project does not
delay timely attainment if it improves
air quality associated with a violation
that existed prior to completion of the
project, or does not increase such
violation. In this case, the project also
would still meet section 176(c)(1)(B)(i)
and (B)(ii), in that it does not cause or
worsen an existing violation.
For example, suppose a hot-spot
analysis is performed for a new highway
project that is predicted to significantly
increase the number of diesel trucks
from what is expected in the local area
without the project. A year is chosen in
this example to analyze when peak
emissions from the project are expected
and future air quality is most likely to
be impacted due to the cumulative
impacts of the project and background
emissions in the project area. Under the
conformity rule, both as it existed and
as it is amended today, the project
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would meet section 176(c)(1)(B)(iii)
requirements not to delay timely
attainment in the local project area as
long as the project’s new emissions do
not create new violations or worsen
existing violations in the local project
area. Such a demonstration would
examine the total impact of the project’s
new emissions in the context of the
future transportation system, any
expected growth in other emissions
sources, and any existing or new control
measures that are expected to impact
the local project area. If the hot-spot
analysis demonstrated that the proposed
project would improve or not impact air
quality, then timely attainment would
also not be delayed from what would
have occurred without the project. If a
violation still exists with the project, but
the project itself improves or does not
change air quality, it does not delay
timely attainment and it can conform. In
contrast, if such a project increased
emissions enough to cause a new
violation or worsen an existing violation
in the local project area, then the project
would delay timely attainment, since
worsening air quality above the NAAQS
would impede the ability to attain in the
local project area. In such a case, the
project could not be found to conform
until the new or worsened future
violation was mitigated.
3. Requirement for No Delay in Timely
Attainment of Any Required Interim
Reductions or Milestones
Today’s final rule also ensures that a
project would meet CAA section
176(c)(1)(B)(iii) requirements for no
delay in the timely attainment of any
required interim reductions or other
milestones. EPA interprets ‘‘any
required interim emission reductions or
other milestones’’ to refer to CAA
requirements associated with reductions
and milestones addressed by reasonable
further progress SIPs, rather than other
reductions required for other purposes.
However, EPA believes there is added
value in referencing in section 93.116(a)
the conformity requirement that a
project be consistent with the budgets
and control measures in any applicable
SIP, not just reasonable further progress
SIPs. Therefore, the provisions of
today’s final rule clarify that this
requirement is satisfied in the local
project area if a project is consistent
with the motor vehicle emissions
budget(s) and control measures in the
applicable SIP or interim emission
test(s) (in the absence of a SIP budget).
Although such a demonstration is
already required under the current rule,
EPA’s reference to the requirements in
40 CFR 93.118 and 93.119 clarify that a
project’s emissions—when combined
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with all other emissions from all other
existing and other proposed
transportation projects—must be
consistent with any applicable required
interim reductions and milestones.
Today’s final rule also supports the
implementation of control measures that
are relied upon in reasonable further
progress demonstrations and could
impact air quality in the local project
area. Under today’s final rule, control
measures that are relied upon for
reasonable further progress SIPs must
have sufficient state and local
commitments to be included in a
regional emissions analysis or a hot-spot
analysis. If the implementation of a
control measure is not assured, then
such reductions cannot be included in
the regional emissions analysis for the
entire nonattainment or maintenance
area (40 CFR 93.122(a)) or within the
local project area considered in a hotspot analysis (40 CFR 93.123(c)(3) and
(4)), and conformity may not be
demonstrated for a project. EPA believes
that these requirements also ensure that
‘‘any required interim emissions
reductions or other milestones’’ are not
delayed within a local project area as a
result of a single project’s emissions.
For example, a project may not meet
CAA section 176(c)(1)(B)(iii)
requirements if SIP control measures
were not being implemented as
expected and as a result, a project’s
emissions (when combined with
expected future emissions without the
SIP control measures) caused a new
violation or worsened an existing
violation in the local project area. In
such a case, additional control measures
as part of the conformity determination
may be required in order to offset any
emissions increases from a project.
Today’s final rule also clarifies that all
CAA section 176(c)(1)(B)(iii)
requirements are met when air quality
improves as a result of the project, e.g.,
an existing air quality violation that
would have occurred without the
project is estimated to be reduced or
eliminated if the new project were
implemented. EPA believes that all of
section 176(c)(1)(B) requirements would
be met in the local project area in such
a case since the Act requires that
individual projects do not worsen air
quality or affect an area’s ability to
attain or achieve interim requirements.
Certainly, if air quality improves in the
local project area with the
implementation of a new project, EPA
believes that timely attainment and
required reasonable further progress
interim requirements are not delayed. In
fact, the opposite would be true in such
a case, since future air quality would be
improved and attainment possibly
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expedited from what would have
occurred without the project’s
implementation.
4. Other Comments
EPA is including responses to other
relevant comments on this portion of
today’s rule below.
Comment: One commenter thought
that based on the statutory language in
CAA 176(c)(1)(A) and (B), promulgating
rules that require PM2.5 emission
reductions would be permissible and
reasonable. Another commenter
believed that EPA had not responded to
the court’s remand, since it was not
expanding on existing conformity rule
requirements for hot-spot analyses.
Response: As explained above, EPA
disagrees that section 176(c)(1) requires
projects to reduce emissions. As such,
EPA believes its interpretation of these
provisions is the most reasonable one.
Hot-spot analyses in PM2.5 (and PM10)
nonattainment and maintenance areas
are required for transportation projects
of local air quality concern. Such
projects are those highway and transit
projects that involve significant diesel
traffic, significant increases in diesel
traffic, or significant numbers of diesel
vehicles congregating in one location.
These types of projects are unlikely to
improve air quality in and of
themselves.
The structure of section 176(c)
supports EPA’s interpretation as the
most reasonable interpretation of the
statutory language. The conformity
provisions of the CAA in 176(c)(1)(A)
and (B) do not require that
transportation activities reduce
emissions, only that they be consistent
with the purpose of the SIP. Only in the
specific provision of 176(c)(3)(A)(iii)
does the statute require transportation
projects to ‘‘contribute to annual
emissions reductions,’’ and this
requirement applies to projects only in
certain CO areas before such areas have
a SIP, not generally to all projects. Had
Congress intended for projects subject to
sections 176(c)(1)(A) and (B) to
‘‘contribute to annual emissions
reductions,’’ it would have included
explicit language stating so, as it did in
section 176(c)(3). See further details in
our general rationale earlier in this
section.
Comment: One commenter requested
that EPA add language to the conformity
rule that prescribes procedures for
requesting assistance from the air
quality agency in developing offsetting
emissions reductions, to reduce air
quality concentrations at appropriate
receptor locations to levels that attain
the NAAQS on or after the attainment
deadline.
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Response: EPA does not believe
additional language is necessary
because existing requirements
adequately address the state air agency’s
involvement in developing offsetting
measures. First, the existing regulation
at 40 CFR 93.123(c)(4) states: ‘‘CO, PM10,
or PM2.5 mitigation or control measures
shall be assumed in the hot-spot
analysis only where there are written
commitments from the project sponsor
and/or operator to implement such
measures, as required by § 93.125(a).’’ 48
The air quality agency as well as EPA
has the opportunity to review any such
written commitments during
interagency consultation on the
conformity determination per 40 CFR
93.105(c). Second, if offsetting measures
are added to the SIP, then the state air
quality agency would have to agree on
these measures. In addition, the
development of offsetting emissions
reductions would be subject to the
public process required for a SIP
revision. Third, in the case where a new
transportation control measure (TCM) is
to be added to the SIP without a full SIP
revision, the CAA requires the TCM to
be developed through a collaborative
process that includes the state air
quality agency; in addition, the state air
quality agency as well as EPA must
concur before such a TCM is added to
the SIP. See EPA’s guidance, entitled,
‘‘Guidance for Implementing the Clean
Air Act Section 176(c)(8) Transportation
Control Measure Substitution and
Addition Provision,’’ found on EPA’s
Web site at: https://www.epa.gov/otaq/
stateresources/transconf/policy/
420b09002.pdf.
Comment: One commenter thought
the regulations at 40 CFR 93.116(a) and
93.123 are unclear regarding the
specifics of performing a PM hot-spot
analysis, including whether the
conformity rule requires a comparison
of emissions from the build case with
the emissions from the no-build case in
the same future year, or whether it
allows a comparison of the build case
with emissions in the current year as the
baseline. The commenter was concerned
that if the analysis is based on a
comparison of the build case for a future
48 In addition, the conformity rule at 40 CFR
93.101 defines ‘‘written commitment’’ as follows:
‘‘Written commitment for the purposes of this
subpart means a written commitment that includes
a description of the action to be taken; a schedule
for the completion of the action; a demonstration
that funding necessary to implement the action has
been authorized by the appropriating or authorizing
body; and an acknowledgement that the
commitment is an enforceable obligation under the
applicable implementation plan.’’ Since these
obligations are ‘‘an enforceable obligation under the
applicable implementation plan,’’ state air agencies
will have a role in ensuring that any necessary
measures are properly implemented and enforced.
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year with current emissions, a project
could conform even if it adds more
vehicle trips to the project location,
because the build analysis would
include the effect of new engine control
technologies and fleet turnover. The
commenter believes that the analysis
should examine the impacts of the
project itself. Therefore, the commenter
urged that the rule be clarified to require
an estimate of future peak year
emissions using a build/no-build
analysis, which the commenter asserted
would provide a lawful basis for
assessing the impact of emissions from
a proposed project.
Response: This comment is beyond
the scope of this rulemaking. For
purposes of EPA’s hot-spot regulations,
EPA is only addressing in today’s rule
the specific issue that was remanded by
the Court in December 2007, i.e.,
whether CAA section 176(c)(1)(B)(iii)
applies in the local area affected by a
project. As stated in the May 2009
proposal, EPA did not propose or seek
public comment on any other aspect of
EPA’s preexisting rules for performing
hot-spot analyses under 40 CFR 93.123
or any other parts of the conformity
rule.
In addition, EPA has already
addressed how hot-spot analyses are to
be conducted to avoid the situation
described by the commenter. In the
original conformity rule, EPA stated its
intentions for applying the hot-spot
requirement—‘‘that the hot-spot analysis
compare concentrations with and
without the project based on modeling
of conditions in the analysis year.’’ (58
FR 62212). The July 2004 final rule
clarified the horizon years for hot-spot
analyses. In this rule, EPA stated that
‘‘[t]o ensure that the requirement for hotspot analysis is being satisfied, areas
should examine the year(s) within the
transportation plan or regional
emissions analysis, as appropriate,
during which peak emissions from the
project are expected and a new violation
or worsening of an existing violation
would most likely occur due to the
cumulative impacts of the project and
background regional emissions in the
project area.’’ See 69 FR 40056–58 for
more details on this rulemaking.
Furthermore, EPA agrees that it would
be inappropriate to ignore the future air
quality impacts from building a
proposed project. As stated above,
EPA’s rule requires that in the future
year(s) where emissions are expected to
be the highest, the concentrations of the
pollutant that result from the project’s
emissions in combination with
background emissions from other
sources are compared to the NAAQS.
However, this analysis is performed by
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examining future air quality impacts
from a project, rather than comparing
emissions from the project in the future
to emissions in a baseline year. EPA
strongly disagrees that the current rule
can be interpreted in this way. An
analysis under the rule does provide a
lawful basis for assessing the impact of
emissions from a proposed project,
because it compares resulting air quality
concentrations to the NAAQS, which by
law are established by EPA through
rulemaking.
As stated above, in the case where the
analysis shows that the air quality
concentrations are greater than the
NAAQS, the project may still be able to
conform. If building the project leads to
improved air quality concentrations
over not building the project, then the
project could still be found to conform,
even if the concentrations are above the
NAAQS. In this case, a build/no-build
analysis would show that the project is
helping to reduce concentrations, and
improve air quality by reducing a future
violation. In this case, the project
neither creates a new violation nor
worsens an existing violation, nor does
it delay timely attainment.
Last, it is entirely appropriate that a
hot-spot analysis include the effects of
new technologies and fleet turnover that
is expected to occur in a future analysis
year. The conformity rule has always
allowed the future effects of federal
vehicle emissions standards, fleet
turnover, fuel programs, and other
control measures to be reflected in hotspot analyses when they are assured to
occur, because including such effects
provides a reasonable estimate of future
emissions that is more accurate than not
including such effects.
Comment: One commenter opined
that off-road emissions that result from
a transportation project being built
should be included in the hot-spot
analysis as part of the background
emissions, because the conformity
regulations at 40 CFR 93.123(c) require
them to be included: ‘‘[e]stimated
pollutant concentrations must be based
in the total emissions burden which
may result from the implementation of
the project.’’ The commenter asserted
that a highway project that facilitates
additional diesel vehicles such as
ocean-going vessels, locomotives,
harborcraft, and cargo-handling
equipment cannot ignore these
significant sources of emissions that
affect the air quality at the location of
the project.
Response: This comment is outside
the scope of today’s rulemaking for the
reasons discussed above. However, EPA
notes that it agrees with this comment.
As the commenter points out, the
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regulations at 40 CFR 93.123(c)(1) state:
‘‘Estimated pollutant concentrations
must be based on the total emissions
burden which may result from the
implementation of the project, summed
together with future background
concentrations.’’ EPA agrees that if a
highway project will facilitate
additional diesel ships or locomotives,
these additional non-road emissions
must be included as part of the
background concentrations in the hotspot analysis. The current conformity
rule also requires hot-spot analyses to
consider any emissions that are already
expected to occur from other sources in
the local project area, in addition to any
emissions created by the project being
built.
Comment: One commenter suggested
that hot-spot analyses should apply to
existing projects, not just new projects,
and that the language of CAA section
176(c) would support ‘‘an ongoing duty’’
to ensure compliance with the hot-spot
rule. To the extent that the federal
government ‘‘engage[s] in’’ or ‘‘supports’’
a facility, the commenter believed that
a hot-spot analysis is required. For
example, when the government
provides funds for maintenance and
repair of freight facilities, the
commenter believed there should be an
ongoing requirement to perform a hotspot analysis.
Response: This comment is outside
the scope of today’s action. EPA did not
propose or seek comment on any
revision to the hot-spot regulations
addressing when hot-spot analyses are
required. Since the original 1993
transportation conformity rule, EPA’s
hot-spot requirements have applied only
to those projects that require projectlevel conformity determinations under
40 CFR 93.102(a) and 93.104(d), which
are those new non-exempt highway and
transit projects that receive FHWA or
FTA funding or approval. After that
point, conformity of a project does not
need to be redetermined unless one of
three things occur: (1) The project’s
design concept and scope significantly
changes; (2) three years elapse since the
most recent major step to advance the
project; or (3) a supplemental
environmental document has been
initiated for air quality purposes (40
CFR 93.104(d)). EPA has previously
concluded that a new project-level
conformity determination is warranted
in these cases. Barring one of these
cases, it is reasonable to conclude that
conformity continues to be
demonstrated, based on both the initial
project-level conformity determination
as well as the periodic regional
conformity determination needed for
the transportation plan and TIP, which
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includes the project. Today’s final rule
addresses none of these requirements.
Comment: One commenter stated that
the proposed rule is inconsistent with
EPA’s definition for ‘‘hot-spot analysis’’
and the CAA because the proposed rule
fails to require a comparison of
localized PM2.5 concentrations to the
NAAQS. The commenter opines that
EPA’s regulatory definition is consistent
with the statutory text but the proposed
rule is not in that it fails to expressly
require that, where emissions from a
highway project subject to hot-spot
review would cause or contribute to
NAAQS violations after the attainment
deadline, approval of the project must
be prohibited unless some remedial
action is taken to avoid the NAAQS
violation after the attainment deadline.
The same commenter also stated that
EPA’s proposal is not consistent with
the CAA because it would allow a
project to conform even if emissions are
maintained at levels that will continue
to cause NAAQS violations after the
statutory deadline.
Response: EPA disagrees with this
commenter and the description of the
May 2009 proposal. Today’s final rule
does require a comparison of localized
pollutant concentrations to the NAAQS.
By requiring a demonstration that no
new local violations are created and no
existing violations are worsened, the
regulation does require a comparison to
the NAAQS. In addition, today’s final
rule would not result in the outcome in
the example provided by commenters.
As stated earlier, a project could not be
found to conform if its emissions caused
or contributed to a future NAAQS
violation.
In the commenter’s second example,
the project could be found to conform,
since the project’s emissions would not
have caused or worsened a NAAQS
violation. If a hot-spot analysis shows
that air quality concentration levels
would be the same with and without a
project, then such a project would not
be ‘maintaining’ any NAAQS violation,
as suggested by the commenter. Instead,
such a hot-spot analysis would show
that a project is not the cause or
contributor to the local area’s air quality
problem, and consequently, the project
would not be delaying timely
attainment. See other parts of today’s
final rule preamble for rationale on
similar comments.
Comment: One commenter requested
that EPA add a definition to the
conformity rule for the term ‘‘delay
timely attainment.’’ The commenter
requested that the term be defined as
follows: If emissions from a project are
expected to cause or contribute to
concentrations that are greater than the
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NAAQS at appropriate receptor
locations after the attainment deadline,
the project would fail to meet CAA
176(c)(1)(B)(iii).
Response: EPA does not believe it is
necessary to promulgate a separate
regulatory definition of the term ‘‘delay
timely attainment’’ in section 93.101 of
the conformity rule. Section 93.116(a) of
today’s final rule and section 93.123(c)
of the existing conformity rule include
this regulatory text, and the discussion
in this preamble and earlier preambles
to transportation conformity regulations
adequately explain the meaning of
‘‘delay timely attainment’’ in the context
of section 176(c)(1)(B)(iii), including
how the hot-spot analysis must comply
with that provision.
Comment: One commenter requested
that EPA define ‘‘local area’’ for hot-spot
analysis purposes, because neither the
proposed nor existing conformity rule
clearly defines it. The commenter
opined that depending upon the
definition, the results of the analysis
might be different. As an example, the
commenter indicated that a project such
as a bus terminal might result in
increased emissions in the immediate
area (although not enough to violate
other portions of section 176(c)(1)(B)),
but may be part of a larger group of
projects that would reduce emissions
overall in a larger area.
Response: EPA agrees that PM hotspot analyses under the conformity rule
must examine the air quality impacts of
the PM10 and PM2.5 NAAQS, including
the area immediately surrounding the
project. In developing the March 2006
final PM hot-spot rule, EPA completed
a thorough review of more than 70
studies representing a cross-section of
available studies looking at particle
concentrations near roadways and
transit projects (71 FR 12472–12474).
Many of these studies were completed
in the types of local communities cited
by the commenter.
However, EPA is not defining ‘‘local
area’’ in this final rule because the
existing conformity rule, along with
previous conformity preambles, provide
the necessary information for hot-spot
analyses. First, the rule’s ‘‘hot-spot
analysis’’ provisions are applied at a
local level to an individual ‘‘highway
project’’ or ‘‘transit project,’’ and the rule
defines all three of these terms in detail
(see 40 CFR 93.101). As a result, the hotspot requirements for individual
projects in conformity rule sections
93.116 and 93.123 are applied within
the local project area. Another example
is the rule’s definition of ‘‘cause or
contribute to a new violation,’’ which
includes the phrase about this
requirement being met ‘‘in an area
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substantially affected by the project.’’
EPA believes that all of the conformity
rule’s hot-spot provisions provide
adequate information regarding what is
a ‘‘local area,’’ and a separate ‘‘local area’’
definition is not necessary or required
by the December 2007 court remand.
EPA does not believe that ‘‘local area’’
can be more specifically defined and
still be appropriate for all projects,
because projects where a hot-spot
analysis is needed can differ in type,
location, scale, scope, and neighboring
populations. EPA believes that the
existing regulation allows the
appropriate local area to be determined
in a hot-spot analysis.
EPA also notes that in the
commenter’s example, a bus terminal
increases emissions in the immediate
area but does not violate other portions
of section 176(c)(1)(B), i.e., this project
increases emissions but would not
create a new violation or worsen an
existing NAAQS violation. Therefore,
this project could be found to conform
under the PM hot-spot conformity rules.
Comment: One commenter requested
that EPA define ‘‘appropriate receptor
location’’ in section 93.123(c)(1) of the
conformity rule to be ‘‘locations near the
project where the public has daily
access and where exposure risks will be
greatest with regard to the frequency or
severity.’’ The commenter stated that the
rule should clarify that receptor or
monitor locations should not be located
outside the zone of observed highway
impacts because at those distances no
difference would be detected regardless
of how many additional vehicles are
added. The commenter cited examples
of past PM hot-spot analyses where
emissions impacts were examined at
monitors or locations that were a mile
and a half or more from the highway or
from the residential and school facilities
adjacent to the proposed project. The
commenter stated that in both cases,
evidence was submitted showing that
highway emissions decrease to the level
of regional background within the first
300 meters.
In addition, this and another
commenter provided EPA with recent
studies and data illustrating the air
quality impacts of highways in the nearhighway environment, and with data
tallying the millions of people who live
within this range as well as the number
of schools located within it.
Response: EPA appreciates the data
that commenters provided, and agrees
with commenters that hot-spot analyses
are important to ensure that public
health is protected. As noted in the
previous response, EPA finalized the
PM10 and PM2.5 hot-spot requirements
based on the type of information
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submitted by commenters (71 FR
12472–12474). However, the location of
modeling receptors, which is addressed
in 40 CFR 93.123(c), is outside the scope
of today’s final rule.
EPA also notes that the U.S. District
Court in Maryland has upheld the
appropriateness of one of the PM
qualitative hot-spot analyses cited by
the commenter (Audubon Naturalist
Society of the Central Atlantic States,
Inc., et al v. USDOT, et al., 524
F.Supp.2d 642 (Md. 2007), appeal
dismissed without decision
Environmental Defense, et al. v.
USDOT, et al., No. 08–1107 (4th Cir.,
dismissed Nov. 17. 2008)).
EPA intends to describe appropriate
receptor locations in its forthcoming
quantitative PM hot-spot guidance,
which is required under 40 CFR
93.123(b)(4). Interested parties will have
an opportunity to comment on this
document before it is finalized.49
Comment: One commenter
recommended that EPA require projects
to reduce the severity and number of
local 2006 PM2.5 NAAQS violations as a
way to reduce black carbon. This
commenter noted that in EPA’s recent
proposed endangerment finding for
greenhouse gases, EPA explained that it
did not include black carbon because
EPA is addressing black carbon through
its review of the primary and secondary
PM NAAQS. This commenter cited a
large body of new science explaining
black carbon’s climate forcing effect and
impacts on sensitive ecosystems, and
believed that this rule should include
some specific requirements for black
carbon.
Response: Transportation conformity
applies only to transportation-related
criteria pollutants for which a NAAQS
is established and their precursor
pollutants as described in 40 CFR
93.102(b) of the regulation. There is no
NAAQS specifically for black carbon,
therefore EPA lacks authority to require
conformity analysis specifically for
black carbon. To the extent that black
carbon is a component of PM2.5 (as
defined by 40 CFR 93.102(b)(1) and
EPA’s rulemakings for the development
of any PM2.5 NAAQS), it is included as
part of any conformity analysis for
PM2.5.
49 EPA will provide opportunity for public
comment on the PM quantitative hot-spot guidance
according to the terms of a settlement agreement
with Environmental Defense, Natural Resources
Defense Council, and Sierra Club. Refer to the June
22, 2007 ‘‘Notice of proposed settlement agreement;
request for public comment’’ at 72 FR 34460.
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X. 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 EO.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden. The
information collection requirements of
EPA’s existing transportation
conformity regulations and the
proposed revisions in today’s action are
already covered by EPA information
collection request (ICR) entitled,
‘‘Transportation Conformity
Determinations for Federally Funded
and Approved Transportation Plans,
Programs and Projects.’’ The Office of
Management and Budget (OMB) has
previously approved the information
collection requirements contained in the
existing regulations at 40 CFR Part 93
under the provisions of the Paperwork
Reduction Act, 44 U.S.C. 3501 et seq.
and has assigned OMB control number
2060–0561. 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 rules
subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the Agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small not-forprofit organizations and small
government jurisdictions.
For purposes of assessing the impacts
of today’s rule on small entities, small
entity is defined as: (1) A small business
as defined by the Small Business
Administration’s (SBA) regulations at 13
CFR 121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise that is independently owned
and operated and is not dominant in its
field.
After considering the economic
impacts of today’s final rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
This regulation directly affects federal
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agencies and metropolitan planning
organizations that, by definition, are
designated under federal transportation
laws only for metropolitan areas with a
population of at least 50,000. These
organizations do not constitute small
entities within the meaning of the
Regulatory Flexibility Act.
D. Unfunded Mandates Reform Act
This rule does not contain a Federal
mandate that may result in expenditures
of $100 million or more for State, local,
and tribal governments, in the aggregate,
or the private sector in any one year.
The purpose of this final rule is to
amend the conformity rule to clarify
how certain highway and transit
projects meet statutory conformity
requirements for particulate matter in
response to a December 2007 court
ruling, and to update the regulation to
accommodate revisions to the PM10 and
PM2.5 NAAQS. This final rule merely
implements already established law that
imposes conformity requirements and
does not itself impose requirements that
may result in expenditures of $100
million or more in any year. Thus,
today’s final rule is not subject to the
requirements of sections 202 and 205 of
the UMRA.
This rule is also not subject to the
requirements of section 203 of UMRA
because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. This
rule will not significantly or uniquely
impact small governments because it
directly affects federal agencies and
metropolitan planning organizations
that, by definition, are designated under
federal transportation laws only for
metropolitan areas with a population of
at least 50,000.
E. Executive Order 13132: Federalism
This final rule does not have
federalism implications. It will not have
substantial direct effects on states, on
the relationship between the national
government and states, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. The CAA
requires conformity to apply in certain
nonattainment and maintenance areas
as a matter of law, and this action
merely establishes and revises
procedures for transportation planning
entities in subject areas to follow in
meeting their existing statutory
obligations. Thus, Executive Order
13132 does not apply to this rule.
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications, as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). The CAA requires transportation
conformity to apply in any area that is
designated nonattainment or
maintenance by EPA. This rule amends
the conformity rule to clarify how
certain highway and transit projects
meet statutory conformity requirements
for particulate matter in response to a
December 2007 court ruling, and
updates the conformity rule to
accommodate revisions to the PM10 and
PM2.5 NAAQS. Because today’s
amendments to the conformity rule do
not significantly or uniquely affect the
communities of Indian tribal
governments, Executive Order 13175
does not apply to this action.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
This final rule is not subject to
Executive Order 13045 62 FR 19885,
April 23, 1997) because it is not
economically significant as defined in
Executive Order 12866, and because the
Agency does not believe the
environmental health or safety risks
addressed by this action present a
disproportionate risk to children.
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H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not a ‘‘significant energy
action’’ as defined in Executive Order
13211 (66 FR 18355 (May 22, 2001)),
because it is not likely to have a
significant adverse effect on the supply,
distribution, or use of energy. It does not
create a serious inconsistency or
otherwise interfere with an action taken
or planned by another agency regarding
energy. Further, this rule is not likely to
have any adverse energy effects because
it does not raise novel legal or policy
issues adversely affecting the supply,
distribution or use of energy arising out
of legal mandates, the President’s
priorities, or the principles set forth in
Executive Orders 12866 and 13211.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, section 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
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otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., material 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 involve technical
standards. Therefore, EPA did not
consider the use of any voluntary
consensus standards.
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 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 Transportation
Conformity Rule PM2.5 and PM10
Amendments
Page 134 of 145 is not a ‘‘major rule’’
as defined by 5 U.S.C. 804(2). This rule
will be effective April 23, 2010.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order (EO) 12898 (59 FR
7629 (Feb. 16, 1994)) establishes federal
executive policy on environmental
justice. Its main provision directs
federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the 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
increases the level of environmental
protection for all affected populations
without having any disproportionately
high and adverse human health or
environmental effects on any
population, including any minority or
low-income population. This final rule
simply amends the conformity rule to
clarify how certain highway and transit
projects meet statutory requirements for
particulate matter in response to a
December 2007 court ruling, and
updates the conformity rule to
accommodate revisions to the PM10 and
PM2.5 NAAQS.
List of Subjects in 40 CFR Part 93
Administrative practice and
procedure, Air pollution control, Carbon
monoxide, Clean Air Act,
Environmental protection, Highways
and roads, Intergovernmental relations,
Mass transportation, Nitrogen dioxide,
Ozone, Particulate matter,
Transportation, Volatile organic
compounds.
K. Determination Under Section 307(d)
Pursuant to CAA Section 307(d)(1)(U),
the Administrator determines that this
action is subject to the provisions of
section 307(d). Section 307(d)(1)(U)
provides that the provisions of section
307(d) apply to ‘‘such other actions as
the Administrator may determine.’’
L. 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
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Dated: March 10, 2010.
Lisa P. Jackson,
Administrator.
For the reasons set out in the
preamble, 40 CFR part 93 is amended as
follows:
■
PART 93—[AMENDED]
1. The authority citation for part 93
continues to read as follows:
■
Authority: 42 U.S.C. 7401–7671q.
2. Section 93.101 is amended as
follows:
■ a. By removing the definitions for
‘‘1-hour ozone NAAQS’’ and ‘‘8-hour
ozone NAAQS’’; and
■ b. By revising the definition of
‘‘National ambient air quality standards
(NAAQS)’’.
■
§ 93.101
Definitions.
*
*
*
*
*
National ambient air quality
standards (NAAQS) are those standards
established pursuant to section 109 of
the CAA.
(1) 1-hour ozone NAAQS means the 1hour ozone national ambient air quality
standard codified at 40 CFR 50.9.
(2) 8-hour ozone NAAQS means the 8hour ozone national ambient air quality
standard codified at 40 CFR 50.10.
(3) 24-hour PM10 NAAQS means the
24-hour PM10 national ambient air
quality standard codified at 40 CFR
50.6.
(4) 1997 PM2.5 NAAQS means the
PM2.5 national ambient air quality
standards codified at 40 CFR 50.7.
(5) 2006 PM2.5 NAAQS means the 24hour PM2.5 national ambient air quality
standard codified at 40 CFR 50.13.
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(6) Annual PM10 NAAQS means the
annual PM10 national ambient air
quality standard that EPA revoked on
December 18, 2006.
*
*
*
*
*
§ 93.105
[Amended]
3. Section 93.105 is amended in
paragraph (c)(1)(vi) by
removing the citation
‘‘§ 93.109(l)(2)(iii)’’ and adding in its
place ‘‘§ 93.109(n)(2)(iii)’’.
■ 4. Section 93.109 is amended as
follows:
■ a. In paragraph (b):
■ i. By removing the citation ‘‘(c)
through (i)’’ and adding in its place the
citation ‘‘(c) through (k)’’;
■ ii. By removing the reference ‘‘(j)’’ and
adding in its place ‘‘(l)’’;
■ iii. By removing the reference ‘‘(k)’’
from the fourth sentence and adding in
its place ‘‘(m)’’;
■ iv. By removing the reference ‘‘(l)’’
from the fifth sentence and adding in its
place ‘‘(n)’’;
■ b. By revising paragraph (g)(2)
introductory text;
■ c. By redesignating paragraph (g)(3) as
(g)(4);
■ d. By adding new paragraph (g)(3);
■ e. By revising the heading of
paragraph (i);
■ f. By adding the words ‘‘such 1997’’
before the words ‘‘PM2.5 nonattainment
or maintenance areas’’ in
paragraph(i)(1);
■ g. By adding the words ‘‘such 1997’’
before the words ‘‘PM2.5 nonattainment
and maintenance areas’’ in paragraph (i)
introductory text and paragraph (i)(2)
introductory text;
■ h. By adding the words ‘‘such 1997’’
before the words ‘‘PM2.5 nonattainment
areas’’ in paragraph (i)(3);
■ i. By redesignating paragraphs (j), (k),
and (l) as (l), (m), and (n), respectively;
■ j. In newly designated paragraph
(n)(2) introductory text by removing the
citation ‘‘(c) through (k)’’ and adding in
its place the citation ‘‘(c) through (m)’’;
■ k. In newly designated paragraph
(n)(2)(iii):
■ i. By removing the citation ‘‘(l)(2)(ii)’’
and adding in its place the citation
‘‘(n)(2)(ii)’’;
■ ii. By removing the citation
‘‘(l)(2)(ii)(C)’’ and adding in its place the
citation ‘‘(n)(2)(ii)(C)’’;
■ l. By adding new paragraphs (j) and
(k).
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■
§ 93.109 Criteria and procedures for
determining conformity of transportation
plans, programs, and projects: General.
*
*
*
*
*
(g) * * *
(2) In PM10 nonattainment and
maintenance areas where a budget is
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submitted for the 24-hour PM10 NAAQS,
the budget test must be satisfied as
required by § 93.118 for conformity
determinations made on or after:
*
*
*
*
*
(3) Prior to paragraph (g)(2) of this
section applying, the budget test must
be satisfied as required by § 93.118
using the approved or adequate motor
vehicle emissions budget established for
the revoked annual PM10 NAAQS, if
such a budget exists.
*
*
*
*
*
(i) 1997 PM2.5 NAAQS nonattainment
and maintenance areas. * * *
(j) 2006 PM2.5 NAAQS nonattainment
and maintenance areas without 1997
PM2.5 NAAQS motor vehicle emissions
budgets for any portion of the 2006
PM2.5 NAAQS area. In addition to the
criteria listed in Table 1 in paragraph (b)
of this section that are required to be
satisfied at all times, in such 2006 PM2.5
nonattainment and maintenance areas
conformity determinations must include
a demonstration that the budget and/or
interim emissions tests are satisfied as
described in the following:
(1) FHWA/FTA projects in such PM2.5
nonattainment and maintenance areas
must satisfy the appropriate hot-spot
test required by § 93.116(a).
(2) In such PM2.5 nonattainment and
maintenance areas the budget test must
be satisfied as required by § 93.118 for
conformity determinations made on or
after:
(i) The effective date of EPA’s finding
that a motor vehicle emissions budget in
a submitted control strategy
implementation plan revision or
maintenance plan for the 2006 PM2.5
NAAQS is adequate for transportation
conformity purposes;
(ii) The publication date of EPA’s
approval of such a budget in the Federal
Register; or
(iii) The effective date of EPA’s
approval of such a budget in the Federal
Register, if such approval is completed
through direct final rulemaking.
(3) In such PM2.5 nonattainment areas
the interim emissions tests must be
satisfied as required by § 93.119 for
conformity determinations made if there
is no approved motor vehicle emissions
budget from an applicable
implementation plan for the 2006 PM2.5
NAAQS and no adequate motor vehicle
emissions budget from a submitted
control strategy implementation plan
revision or maintenance plan for the
2006 PM2.5 NAAQS.
(k) 2006 PM2.5 NAAQS nonattainment
and maintenance areas with motor
vehicle emissions budgets for the 1997
PM2.5 NAAQS that cover all or a portion
of the 2006 PM2.5 nonattainment area.
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In addition to the criteria listed in Table
1 in paragraph (b) of this section that are
required to be satisfied at all times, in
such 2006 PM2.5 nonattainment and
maintenance areas conformity
determinations must include a
demonstration that the budget and/or
interim emissions tests are satisfied as
described in the following:
(1) FHWA/FTA projects in such PM2.5
nonattainment and maintenance areas
must satisfy the appropriate hot-spot
test required by § 93.116(a).
(2) In such PM2.5 nonattainment and
maintenance areas the budget test must
be satisfied as required by § 93.118 for
conformity determinations made on or
after:
(i) The effective date of EPA’s finding
that a motor vehicle emissions budget in
a submitted control strategy
implementation plan revision or
maintenance plan for the 2006 PM2.5
NAAQS is adequate for transportation
conformity purposes;
(ii) The publication date of EPA’s
approval of such a budget in the Federal
Register; or
(iii) The effective date of EPA’s
approval of such a budget in the Federal
Register, if such approval is completed
through direct final rulemaking.
(3) Prior to paragraph (k)(2) of this
section applying, the following test(s)
must be satisfied:
(i) If the 2006 PM2.5 nonattainment
area covers the same geographic area as
the 1997 PM2.5 nonattainment or
maintenance area(s), the budget test as
required by § 93.118 using the approved
or adequate motor vehicle emissions
budgets in the 1997 PM2.5 applicable
implementation plan or implementation
plan submission;
(ii) If the 2006 PM2.5 nonattainment
area covers a smaller geographic area
within the 1997 PM2.5 nonattainment or
maintenance area(s), the budget test as
required by § 93.118 for either:
(A) The 2006 PM2.5 nonattainment
area using corresponding portion(s) of
the approved or adequate motor vehicle
emissions budgets in the 1997 PM2.5
applicable implementation plan or
implementation plan submission where
such portion(s) can reasonably be
identified through the interagency
consultation process required by
§ 93.105; or
(B) The 1997 PM2.5 nonattainment
area using the approved or adequate
motor vehicle emissions budgets in the
1997 PM2.5 applicable implementation
plan or implementation plan
submission. If additional emissions
reductions are necessary to meet the
budget test for the 2006 PM2.5 NAAQS
in such cases, these emissions
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reductions must come from within the
2006 PM2.5 nonattainment area;
(iii) If the 2006 PM2.5 nonattainment
area covers a larger geographic area and
encompasses the entire 1997 PM2.5
nonattainment or maintenance area(s):
(A) The budget test as required by
§ 93.118 for the portion of the 2006
PM2.5 nonattainment area covered by the
approved or adequate motor vehicle
emissions budgets in the 1997 PM2.5
applicable implementation plan or
implementation plan submission; and
the interim emissions tests as required
by § 93.119 for either: the portion of the
2006 PM2.5 nonattainment area not
covered by the approved or adequate
budgets in the 1997 PM2.5
implementation plan, the entire 2006
PM2.5 nonattainment area, or the entire
portion of the 2006 PM2.5 nonattainment
area within an individual state, in the
case where separate 1997 PM2.5 SIP
budgets are established for each state of
a multi-state 1997 PM2.5 nonattainment
or maintenance area; or
(B) The budget test as required by
§ 93.118 for the entire 2006 PM2.5
nonattainment area using the approved
or adequate motor vehicle emissions
budgets in the applicable 1997 PM2.5
implementation plan or implementation
plan submission.
(iv) If the 2006 PM2.5 nonattainment
area partially covers a 1997 PM2.5
nonattainment or maintenance area(s):
(A) The budget test as required by
§ 93.118 for the portion of the 2006
PM2.5 nonattainment area covered by the
corresponding portion of the approved
or adequate motor vehicle emissions
budgets in the 1997 PM2.5 applicable
implementation plan or implementation
plan submission where they can be
reasonably identified through the
interagency consultation process
required by § 93.105; and
(B) The interim emissions tests as
required by § 93.119, when applicable,
for either: The portion of the 2006 PM2.5
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nonattainment area not covered by the
approved or adequate budgets in the
1997 PM2.5 implementation plan, the
entire 2006 PM2.5 nonattainment area, or
the entire portion of the 2006 PM2.5
nonattainment area within an
individual state, in the case where
separate 1997 PM2.5 SIP budgets are
established for each state in a multistate 1997 PM2.5 nonattainment or
maintenance area.
*
*
*
*
*
5. Section 93.116 is amended by
revising paragraph (a) to read as follows:
■
§ 93.116 Criteria and procedures:
Localized CO, PM10, and PM2.5 violations
(hot-spots).
(a) This paragraph applies at all times.
The FHWA/FTA project must not cause
or contribute to any new localized CO,
PM10, and/or PM2.5 violations, increase
the frequency or severity of any existing
CO, PM10, and/or PM2.5 violations, or
delay timely attainment of any NAAQS
or any required interim emission
reductions or other milestones in CO,
PM10, and PM2.5 nonattainment and
maintenance areas. This criterion is
satisfied without a hot-spot analysis in
PM10 and PM2.5 nonattainment and
maintenance areas for FHWA/FTA
projects that are not identified in
§ 93.123(b)(1). This criterion is satisfied
for all other FHWA/FTA projects in CO,
PM10 and PM2.5 nonattainment and
maintenance areas if it is demonstrated
that during the time frame of the
transportation plan no new local
violations will be created and the
severity or number of existing violations
will not be increased as a result of the
project, and the project has been
included in a regional emissions
analysis that meets applicable §§ 93.118
and/or 93.119 requirements. The
demonstration must be performed
according to the consultation
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requirements of § 93.105(c)(1)(i) and the
methodology requirements of § 93.123.
*
*
*
*
*
§ 93.118
[Amended]
6. Section 93.118 is amended in
paragraph (a) by removing the citation
‘‘§ 93.109(c) through (l)’’ and adding in
its place ‘‘§ 93.109(c) through (n)’’.
■ 7. Section 93.119 is amended as
follows:
■ a. In paragraph (a), by removing the
citation ‘‘§ 93.109(c) through (l)’’ and
adding in its place ‘‘§ 93.109(c) through
(n)’’; and
■ b. By revising paragraph (e)(2).
■
§ 93.119 Criteria and procedures: Interim
emissions in areas without motor vehicle
emissions budgets.
*
*
*
*
*
(e) * * *
(2) The emissions predicted in the
‘‘Action’’ scenario are not greater than:
(i) 2002 emissions, in areas designated
nonattainment for the 1997 PM2.5
NAAQS; or
(ii) Emissions in the most recent year
for which EPA’s Air Emissions
Reporting Requirements (40 CFR Part
51, Subpart A) requires submission of
on-road mobile source emissions
inventories, as of the effective date of
nonattainment designations for any
PM2.5 NAAQS other than the 1997 PM2.5
NAAQS.
*
*
*
*
*
§ 93.121
[Amended]
8. Section 93.121 is amended:
a. In paragraph (b) introductory text
by removing the citation ‘‘§ 93.109(l)’’
and adding in its place ‘‘§ 93.109(n)’’;
■ b. In paragraph (c) introductory text
by removing the citation ‘‘§ 93.109(j) or
(k)’’ and adding in its place ‘‘§ 93.109(l)
or (m)’’.
■
■
[FR Doc. 2010–5703 Filed 3–23–10; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 75, Number 56 (Wednesday, March 24, 2010)]
[Rules and Regulations]
[Pages 14260-14285]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-5703]
[[Page 14259]]
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Part II
Environmental Protection Agency
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40 CFR Part 93
Transportation Conformity Rule PM2.5 and PM10 Amendments; Final Rule
Federal Register / Vol. 75, No. 56 / Wednesday, March 24, 2010 /
Rules and Regulations
[[Page 14260]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 93
[EPA-HQ-OAR-2008-0540; FRL-9127-7]
RIN 2060-AP29
Transportation Conformity Rule PM2.5 and
PM10 Amendments
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: In this action, EPA is amending the transportation conformity
rule to finalize provisions that were proposed on May 15, 2009. These
amendments primarily affect conformity's implementation in
PM2.5 and PM10 nonattainment and maintenance
areas. EPA is updating the transportation conformity regulation in
light of an October 17, 2006 final rule that strengthened the 24-hour
PM2.5 national ambient air quality standard (NAAQS) and
revoked the annual PM10 NAAQS. In addition, EPA is
clarifying the regulations concerning hot-spot analyses to address a
December 2007 remand from the Court of Appeals for the District of
Columbia Circuit. This portion of the final rule applies to
PM2.5 and PM10 nonattainment and maintenance
areas as well as carbon monoxide nonattainment and maintenance areas.
The Clean Air Act (CAA) requires federally supported transportation
plans, transportation improvement programs, and projects to be
consistent with (``conform to'') the purpose of the state air quality
implementation plan. The U.S. Department of Transportation (DOT) is
EPA's federal partner in implementing the transportation conformity
regulation. EPA has consulted with DOT, and they concur with this final
rule.
DATES: This final rule is effective on April 23, 2010.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. EPA-HQ-OAR-2008-0540. All documents in the docket are listed on the
https://www.regulations.gov Web site. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically through https://www.regulations.gov or in hard copy at the Air and Radiation Docket,
EPA/DC, EPA West, Room 3334, 1301 Constitution Ave., NW., Washington,
DC. The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal holidays. The telephone number for the
Public Reading Room is (202) 566-1744 and the telephone number for the
Air and Radiation Docket is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Laura Berry, State Measures and
Conformity Group, Transportation and Regional Programs Division,
Environmental Protection Agency, 2000 Traverwood Drive, Ann Arbor, MI
48105, e-mail address: berry.laura@epa.gov, telephone number: (734)
214-4858, fax number: (734) 214-4052; or Patty Klavon, State Measures
and Conformity Group, Transportation and Regional Programs Division,
Environmental Protection Agency, 2000 Traverwood Drive, Ann Arbor, MI
48105, e-mail address: klavon.patty@epa.gov, telephone number: (734)
214-4476, fax number: (734) 214-4052.
SUPPLEMENTARY INFORMATION: The contents of this preamble are listed in
the following outline:
I. General Information
II. Background on the Transportation Conformity Rule
III. General Overview of Transportation Conformity for the 2006
PM2.5 NAAQS
IV. Baseline Year for Certain 2006 PM2.5 Nonattainment
Areas
V. Regional Conformity Tests in 2006 PM2.5 Nonattainment
Areas That Do Not Have Adequate or Approved SIP Budgets for the 1997
PM2.5 NAAQS
VI. Regional Conformity Tests in 2006 PM2.5 Areas That
Have 1997 PM2.5 SIP Budgets
VII. Other Conformity Requirements for 2006 PM2.5 Areas
VIII. Transportation Conformity in PM10 Nonattainment and
Maintenance Areas and the Revocation of the Annual PM10
NAAQS
IX. Response to the December 2007 Hot-Spot Court Decision
X. Statutory and Executive Order Reviews
I. General Information
A. Does This Action Apply to Me?
Entities potentially regulated by the conformity rule are those
that adopt, approve, or fund transportation plans, programs, or
projects under title 23 U.S.C. or title 49 U.S.C. Regulated categories
and entities affected by today's action include:
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Category Examples of regulated entities
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Local government................................................. Local transportation and air quality
agencies, including metropolitan planning
organizations (MPOs).
State government................................................. State transportation and air quality
agencies.
Federal government............................................... Department of Transportation (Federal Highway
Administration (FHWA) and Federal Transit
Administration (FTA)).
----------------------------------------------------------------------------------------------------------------
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be affected by this
final rule. This table lists the types of entities of which EPA is
aware that potentially could be regulated by the transportation
conformity rule. Other types of entities not listed in the table could
also be regulated. To determine whether your organization is regulated
by this action, you should carefully examine the applicability
requirements in 40 CFR 93.102. If you have questions regarding the
applicability of this action to a particular entity, consult the
persons listed in the preceding FOR FURTHER INFORMATION CONTACT
section.
B. How Can I Get Copies of This Document?
1. Docket
EPA has established an official public docket for this action under
Docket ID No. EPA-HQ-OAR-2008-0540. You can get a paper copy of this
Federal Register document, as well as the documents specifically
referenced in this action, any public comments received, and other
information related to this action at the official public docket. See
the ADDRESSES section for its location.
2. Electronic Access
You may access this Federal Register document electronically
through EPA's Transportation Conformity Web site at https://www.epa.gov/otaq/stateresources/transconf/index.htm. You may also access this
document electronically under the Federal Register listings at https://www.epa.gov/fedrgstr/.
An electronic version of the official public docket is available
through https://www.regulations.gov. You may use https://www.regulations.gov to view public comments, access the index listing
of the contents of the official
[[Page 14261]]
public docket, and access those documents in the public docket that are
available electronically. Once in the system, select ``search,'' then
key in the appropriate docket identification number.
Certain types of information will not be placed in the electronic
public docket. Information claimed as CBI and other information for
which disclosure is restricted by statute is not available for public
viewing in the electronic public docket. EPA's policy is that
copyrighted material is not placed in the electronic public docket but
is available only in printed, paper form in the official public docket.
To the extent feasible, publicly available docket materials will be
made available in the electronic public docket. When a document is
selected from the index list in EPA Dockets, the system will identify
whether the document is available for viewing in the electronic public
docket. Although not all docket materials may be available
electronically, you may still access any of the publicly available
docket materials through the docket facility identified in the
ADDRESSES section. EPA intends to provide electronic access in the
future to all of the publicly available docket materials through the
electronic public docket.
For additional information about the electronic public docket,
visit the EPA Docket Center homepage at https://www.epa.gov/epahome/dockets.htm.
II. Background on the Transportation Conformity Rule
A. What Is Transportation Conformity?
Transportation conformity is required under CAA section 176(c) (42
U.S.C. 7506(c)) to ensure that transportation plans, transportation
improvement programs (TIPs) and federally supported highway and transit
project activities are consistent with (``conform to'') the purpose of
the state air quality implementation plan (SIP). Conformity to the
purpose of the SIP means that transportation activities will not cause
new air quality violations, worsen existing violations, or delay timely
attainment of the relevant national ambient air quality standards
(NAAQS) or any interim milestones.\1\ Transportation conformity applies
to areas that are designated nonattainment, and those areas
redesignated to attainment after 1990 (``maintenance areas'') for
transportation-related criteria pollutants: Carbon monoxide (CO),
ozone, nitrogen dioxide (NO2) and particulate matter
(PM2.5, and PM10).\2\
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\1\ These requirements are found in Clean Air Act section
176(c)(B)(i), (ii), and (iii): ``That such activities will not cause
or contribute to any new violation of any standard in any area;
increase the frequency or severity of any existing violation of any
standard in any area; or delay timely attainment of any standard or
any required interim emissions reductions or other milestones in any
area.''
\2\ 40 CFR 93.102(b)(1) defines PM2.5 and
PM10 as particles with an aerodynamic diameter less than
or equal to a nominal 2.5 and 10 micrometers, respectively.
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EPA's transportation conformity rule (40 CFR Parts 51 and 93)
establishes the criteria and procedures for determining whether
transportation activities conform to the SIP. EPA first promulgated the
transportation conformity rule on November 24, 1993 (58 FR 62188), and
subsequently published several other amendments. DOT is EPA's federal
partner in implementing the transportation conformity regulation. EPA
has consulted with DOT, which concurs with this final rule.
A few recent amendments to the transportation conformity rule are
useful background for today's final rule. In a final rule EPA published
on July 1, 2004 (69 FR 40004), EPA provided conformity procedures for
state and local agencies under the 1997 8-hour ozone and
PM2.5 national ambient air quality standards (NAAQS). EPA's
nonattainment area designations for the 1997 8-hour ozone and
PM2.5 NAAQS were effective in June 2004 and April 2005,
respectively. The July 2004 update provided rules for implementing
conformity for these NAAQS. In addition, on May 6, 2005, EPA
promulgated a final rule entitled, ``Transportation Conformity Rule
Amendments for the New PM2.5 National Ambient Air Quality
Standard: PM2.5 Precursors'' (70 FR 24280). This final rule
specified transportation-related PM2.5 precursors and when
they must be considered in transportation conformity determinations in
PM2.5 nonattainment and maintenance areas.
On March 10, 2006, EPA promulgated a final rule (71 FR 12468)
entitled, ``PM2.5 and PM10 Hot-Spot Analyses in
Project-Level Transportation Conformity Determinations for the New
PM2.5 and Existing PM10 National Ambient Air
Quality Standards.'' This rule established the criteria and procedures
for determining which transportation projects must be analyzed for
local air quality impacts--or ``hot-spots''--in PM2.5 and
PM10 nonattainment and maintenance areas. See Section IX. of
today's preamble for more information regarding the March 2006 rule;
see EPA's Web site at https://www.epa.gov/otaq/stateresources/transconf/index.htm for further information about any of EPA's transportation
conformity rulemakings.\3\
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\3\ At this website, click on ``Regulations'' to find all of
EPA's proposed and final rules as well as the current transportation
conformity regulations.
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B. Why Are We Issuing This Final Rule?
Today's action is necessary because EPA promulgated a final rule on
October 17, 2006 that changed the PM2.5 and PM10
NAAQS, as described further below. Today's action provides rules for
implementing conformity for these revisions to the PM2.5 and
PM10 NAAQS. Sections III. through VIII. describe the changes
to the transportation conformity rule that are a result of the October
2006 revisions to the PM2.5 and PM10 NAAQS.
Today's final rule is the second transportation conformity
rulemaking undertaken primarily for the purpose of addressing a new or
revised NAAQS. Due to other statutory requirements, EPA will continue
to establish new or revised NAAQS in the future. Therefore, EPA may
consider restructuring certain sections of the conformity rule in a
future rulemaking so that existing rule requirements would clearly
apply to areas designated for future new or revised NAAQS, without
having to update the rule each time a new or revised NAAQS is
established.
Note that in 2009, EPA issued an interim conformity guidance for
areas designated nonattainment for the 2006 PM2.5 NAAQS \4\
(``2006 PM2.5 areas'').\5\ EPA issued this interim guidance
to help new nonattainment areas meet conformity requirements by the end
of the one-year grace period. While this interim guidance is superseded
by today's final rule, conformity determinations done according to the
interim guidance are consistent with the CAA, and with the
transportation conformity rule.\6\ Therefore, conformity determinations
based on the interim guidance and the transportation conformity rule in
effect at the time of the conformity determination will remain valid.
Conformity determinations completed on or after the effective date of
this final rule must meet all the requirements in the final rule. EPA
will work with the 2006 PM2.5
[[Page 14262]]
areas to ensure they can meet conformity requirements on time.
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\4\ ``2006 PM2.5 NAAQS'' refers to the 24-hour
PM2.5 NAAQS promulgated in 2006.
\5\ ``Interim Transportation Conformity Guidance for 2006
PM2.5 Nonattainment Areas,'' EPA-420-B-09-036, November
2009, available on EPA's Web site at: https://www.epa.gov/otaq/stateresources/transconf/policy/420b09036.pdf.
\6\ Today's final rule changes the baseline year used to
demonstrate conformity for the 2006 PM2.5 NAAQS prior to
having an adequate or approved PM2.5 SIP budget; the
interim guidance addressed this change. Refer to Section IV. for
further discussion of the baseline year for conformity purposes.
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Today's final rule also responds to a court decision regarding the
March 2006 hot-spot rulemaking. Section IX. of this preamble describes
the issue, the court's decision, and EPA's response.
III. General Overview of Transportation Conformity for the 2006
PM2.5 NAAQS
A. Background on 2006 PM2.5 NAAQS Development
EPA issued a final rule on October 17, 2006, effective December 18,
2006, that strengthened the 24-hour PM2.5 NAAQS and revoked
the annual PM10 NAAQS (71 FR 61144). In that final rule, EPA
strengthened the 24-hour PM2.5 NAAQS from the 1997 level of
65 micrograms per cubic meter ([mu]g/m\3\) (average of 98th percentile
values for three consecutive years) to 35 [mu]g/m\3\, while the level
of the annual PM2.5 NAAQS remained unchanged at 15.0
[micro]g/m\3\ (average of three consecutive annual average values). EPA
selected levels for the final NAAQS after completing an extensive
review of thousands of scientific studies on the impact of fine and
coarse particles on public health and welfare. For additional
information about the October 17, 2006 rulemaking, the final rule and
EPA outreach materials can be found at: https://www.epa.gov/pmdesignations/.
The October 2006 rule establishing the 2006 PM2.5 NAAQS
did not revoke the 1997 annual or 24-hour PM2.5 NAAQS. See
Section III.D. below for details on how today's final rule interacts
with conformity requirements for those areas designated nonattainment
for the 1997 PM2.5 NAAQS.\7\
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\7\ ``1997 PM2.5 NAAQS'' includes both the annual and
the 24-hour 1997 PM2.5 NAAQS unless noted otherwise.
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EPA signed the final rule designating areas for the 2006
PM2.5 NAAQS on October 8, 2009.\8\ This final rule was
published in the Federal Register on November 13, 2009, and became
effective December 14, 2009. The designations for the 2006
PM2.5 NAAQS are separate from the existing designations for
the 1997 PM2.5 NAAQS.
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\8\ A Federal Register notice designating areas for the 2006
PM2.5 NAAQS had been signed in late December 2008 by
then-Administrator Johnson, where the designations were based on air
quality data from 2005-2007. The December 2008 notice was awaiting
publication in January 2009 when the newly elected Administration
identified the notice as one that should receive additional review
before publication. However, this notice was never published in the
Federal Register and, therefore, designations were not officially
promulgated. CAA section 107(d)(2)(A) requires EPA to publish the
notice in the Federal Register in order to promulgate designations.
Since January 2009, monitoring data for 2008 has become available
for areas across the U.S. Therefore, the final designations in the
final rule signed by Administrator Jackson on October 8, 2009 are
based on air quality monitoring data from Federal Reference Method
monitors for calendar years 2006-2008.
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However, in the final rule designating areas for the 2006
PM2.5 NAAQS, EPA has also clarified that all 39 areas
designated nonattainment for the 1997 PM2.5 NAAQS were
violating the annual PM2.5 NAAQS, and two of those were also
violating the 24-hour PM2.5 NAAQS.\9\ That is, EPA's
designations rule clarifies that only two areas were designated
nonattainment for the 1997 24-hour PM2.5 NAAQS, and that all
39 nonattainment areas were designated nonattainment for the 1997
annual PM2.5 NAAQS.
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\9\ The two areas designated as nonattainment for both the
annual and 24-hour 1997 PM2.5 NAAQS are the Los Angeles-
South Coast Air Basin, CA nonattainment area and the San Joaquin
Valley, CA nonattainment area.
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Transportation conformity applies for the NAAQS for which an area
is designated nonattainment.\10\ Therefore, in two of the 1997
PM2.5 areas, conformity applies for both the 1997 annual and
24-hour NAAQS. In the other 37 1997 PM2.5 areas, conformity
applies for the 1997 annual NAAQS, and not the 1997 24-hour
PM2.5 NAAQS.
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\10\ Clean Air Act section 176(c)(5) and 40 CFR 93.102(b).
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Refer to EPA's Web site at: https://www.epa.gov/pmdesignations/2006standards/index.htm for additional information about the
nonattainment designations.
B. When Does Conformity Apply for the 2006 PM2.5 NAAQS?
Transportation conformity for the 2006 PM2.5 NAAQS does
not apply until December 14, 2010, which is one year after the
effective date of nonattainment designations for this NAAQS. CAA
section 176(c)(6) and 40 CFR 93.102(d) provide a one-year grace period
from the effective date of designations before transportation
conformity applies in areas newly designated nonattainment for a
particular NAAQS.\11\
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\11\ EPA began the process of notifying state and local
agencies, via the EPA regional offices, of the timing of conformity
under the 2006 PM2.5 NAAQS in its April 16, 2007
memorandum entitled, ``Transportation Conformity and the Revised 24-
hour PM2.5 Standard,'' from Merrylin Zaw-Mon, Director,
Transportation and Regional Programs Division, EPA Office of
Transportation and Air Quality, to EPA Regional Air Directors,
Regions I-X.
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The following discussion provides more details on the application
of the one-year grace period in different types of newly designated
nonattainment areas for the 2006 PM2.5 NAAQS. This
information is consistent with how conformity for new NAAQS has been
implemented in the past.\12\ The conformity grace period will be
available to all newly designated nonattainment areas for the 2006
PM2.5 NAAQS.
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\12\ See EPA's July 1, 2004 final rule for further background on
how EPA has implemented this conformity grace period for the 1997
PM2.5 NAAQS (69 FR 40004).
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Metropolitan areas are urbanized areas that have a population
greater than 50,000 and a designated metropolitan planning organization
(MPO) responsible for transportation planning per 23 U.S.C. 134. Within
one year after the effective date of the initial nonattainment
designation for the 2006 PM2.5 NAAQS, a conformity
determination for this NAAQS must be made by the MPO and DOT for the
MPO's transportation plan and TIP. MPOs must continue to meet
conformity requirements for any other applicable NAAQS, including the
1997 PM2.5 NAAQS, if the area is designated nonattainment or
maintenance for such NAAQS as well.
In nonattainment and maintenance areas with a donut portion,\13\
adjacent MPOs must meet conformity requirements for the 2006
PM2.5 NAAQS. The MPO must also continue to ensure that
conformity is met for any other applicable NAAQS, including any 1997
PM2.5 NAAQS for which the donut area is designated
nonattainment.\14\ The interagency consultation partners for each newly
designated nonattainment area that includes a donut portion should
determine how best to consider the donut area transportation system and
new donut area projects in the MPO's regional emissions analyses and
transportation plan and TIP conformity determinations.
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\13\ For the purposes of transportation conformity, a ``donut''
area is the geographic area outside a metropolitan planning area
boundary, but inside a designated nonattainment or maintenance area
boundary that includes an MPO (40 CFR 93.101). For more discussion
on how conformity determinations should be made for donut areas, see
the preamble to the July 1, 2004 conformity rule (69 FR 40013).
\14\ Determining conformity for these other NAAQS during the
one-year grace period is not necessary unless required by 40 CFR
93.104 (for example, a new or amended transportation plan and TIP
are to be adopted).
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If, at the end of the one-year grace period, the MPO and DOT have
not made a transportation plan and TIP conformity determination for the
2006 PM2.5 NAAQS, the entire area, including any donut area,
would be in a conformity ``lapse.'' \15\ During a
[[Page 14263]]
conformity lapse, only certain projects can receive additional federal
funding or approvals to proceed (e.g. exempt projects, project phases
that were approved before the lapse).\16\ The practical impact of a
conformity lapse will vary on an area-by-area basis.
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\15\ The lapse grace period provision in CAA section 176(c)(9)
does not apply to the deadline for newly designated nonattainment
areas to make the initial transportation plan/TIP conformity
determination within 12 months of the effective date of the
nonattainment designation. For additional details on the conformity
lapse grace period, see the preamble to the January 24, 2008
conformity rule (73 FR 4423-4425).
\16\ For additional information on projects that can proceed
during a conformity lapse, refer to the final rule of July 1, 2004
(69 FR 40005-40006), which addressed the March 2, 1999 U.S. Court of
Appeals decision that affected related provisions of the conformity
rule (Environmental Defense Fund v. EPA, 167 F.3d 641 (D.C. Cir.
1999). See also the following guidance memoranda that address this
court decision: DOT's January 2, 2002 guidance, published in the
Federal Register on February 7, 2002 (67 FR 5882); DOT's May 20,
2003 and FTA's April 9, 2003 supplemental guidance documents; and,
EPA's May 14, 1999 guidance memorandum.
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The one-year grace period for conformity also applies to project-
level conformity determinations (including hot-spot analyses in certain
cases) in newly designated 2006 PM2.5 nonattainment areas.
At the end of the one-year grace period for conformity, requirements
for project-level conformity determinations must be met for the 2006
PM2.5 NAAQS (including hot-spot analyses in certain cases)
before any new federal approvals for such projects can occur. See Table
1 in 40 CFR 93.109 for the conformity criteria that apply for project-
level conformity determinations.
Isolated rural nonattainment and maintenance areas are areas that
do not contain or are not part of any metropolitan planning area as
designated by 23 U.S.C. 134 and 49 U.S.C. 5303 (40 CFR 93.101). As in
other newly designated nonattainment areas, the one-year conformity
grace period for the 2006 PM2.5 NAAQS will begin on the
effective date of an isolated rural area's initial nonattainment
designation. However, because these areas do not have federally
required metropolitan transportation plans and TIPs, they are not
subject to the frequency requirements for conformity determinations on
transportation plans and TIPs (40 CFR 93.104(b),(c), and (e)). Instead,
conformity determinations in isolated rural areas are required only
when a non-exempt FHWA/FTA project(s) needs approval.
Therefore, although the one-year conformity grace period is
available to isolated rural areas, most likely no conformity
consequences would occur upon the expiration date of the one-year grace
period because these areas most likely would not have any projects that
require federal funding or approval at that time. Once the conformity
grace period has expired, a conformity determination would only be
required in such areas when a non-exempt FHWA/FTA project needs
approval. Conformity requirements for isolated rural areas can be found
at 40 CFR 93.109(n).\17\
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\17\ Prior to today's rulemaking, the requirements for isolated
rural areas were found at Sec. 93.109(l). This section has been
renamed as Sec. 93.109(n), as a result of other revisions and
additions in this regulatory section. This is merely an
administrative change and the conformity requirements for isolated
rural areas remain unchanged.
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Response to comments about the grace period. Some commenters
believed that the one-year grace period would not allow enough time for
some areas to meet the conformity requirements. These same commenters
questioned whether a year would be enough time to adequately prepare
attainment SIPs, learn EPA's new emissions factor model (called the
Motor Vehicle Emissions Simulator, or MOVES model) when final, and
complete their conformity determinations. To address these concerns,
these commenters suggested lengthening the conformity grace period for
newly designated nonattainment areas from one to two years.
EPA understands that some areas, such as areas that have never done
conformity before and multi-jurisdictional nonattainment areas (e.g.,
areas with multiple states and/or multiple MPOs) may have additional
challenges in conducting their initial conformity determinations.
However, the CAA as amended on October 27, 2000 specifically provides
newly designated nonattainment areas with only a one-year grace period,
after which conformity applies as a matter of law under the statute.
Therefore, we believe that the statutory language precludes EPA from
extending the conformity grace period beyond one year for new
nonattainment areas.
In accordance with the CAA, states were initially required to
submit their recommendations for nonattainment areas based on monitored
data by December 18, 2007, well before designations became
effective.\18\ Additionally, EPA began the process of notifying state
and local agencies, via the EPA regional offices, of the timing of
conformity under the 2006 PM2.5 NAAQS in the April 16, 2007
memorandum cited earlier.\19\ As mentioned, EPA provided interim
guidance for the 2006 PM2.5 areas to assist in meeting
conformity requirements by the end of the one-year grace period.
Finally, EPA will be working with 2006 PM2.5 areas to
provide technical assistance in an expeditious manner, such as helping
each area determine which test applies for the first 2006
PM2.5 conformity determination.
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\18\ Information on 2006 PM2.5 nonattainment
designations, including copies of EPA's designation letters, can be
accessed from EPA's Web site at https://www.epa.gov/pmdesignations/2006standards/state.htm.
\19\ Memorandum entitled, ``Transportation Conformity and the
Revised 24-hour PM2.5 Standard,'' from Merrylin Zaw-Mon,
then-Director, Transportation and Regional Programs Division, EPA
Office of Transportation and Air Quality, to EPA Regional Air
Directors, Regions I- X, found on EPA's Web site at: https://www.epa.gov/otaq/stateresources/transconf/generalinfo/rev24hr-pm25.pdf.
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We also want to clarify that while areas will have to complete a
conformity determination for their transportation plans and TIPs within
one year, they are not required to complete their attainment
demonstration SIPs for the 2006 PM2.5 NAAQS in that same
time period as the commenter suggested. Instead, they will have three
years from the effective date of designations to submit their
attainment demonstrations, per CAA section 172(b).
Also, implementers will have additional time before MOVES is
required for conformity determinations, as a different grace period
will apply for MOVES once it is released. The conformity rule at 40 CFR
93.111 provides a grace period before a new emissions model is required
for conformity. This grace period can be anywhere from three months to
two years depending on the degree of change from one model to another
(40 CFR 93.111(b)(2)); EPA is intending to provide the maximum length
two-year grace period for the transition to MOVES. Therefore, MOVES
will not be required for the first transportation plan and TIP
conformity determination done for the 2006 PM2.5 NAAQS. EPA
will provide specific guidance regarding the MOVES grace period and
when MOVES will be required to be used for SIPs and conformity. This
guidance will be available on EPA's Web site at: https://www.epa.gov/otaq/stateresources/transconf/policy.htm#models.
EPA and DOT understand the concern that the commenter notes with
respect to learning the new MOVES model, and therefore have devoted
significant staff time and resources to training state and local air
quality and transportation planners in using MOVES. During 2009, 20
MOVES training sessions were held at locations across the U.S. Once
MOVES is final, EPA intends to offer web-based training, and EPA and
DOT are planning to hold additional in-person training sessions as
well. See EPA's Web site: https://www.epa.gov/
[[Page 14264]]
otaq/models/moves/trainingsessions.htm for information about upcoming
training sessions. Also note that other MOVES related guidance,
including user guides and other technical information is available on
EPA's Web site at: https://www.epa.gov/otaq/models/moves/index.htm and
https://www.epa.gov/otaq/stateresources/transconf/policy.htm
C. Definitions for PM2.5 NAAQS
EPA is adding two new definitions to Sec. 93.101 of the conformity
rule to distinguish between the 1997 PM2.5 NAAQS and the
2006 PM2.5 NAAQS. These definitions will help implement
certain conformity requirements in areas that have been designated
nonattainment for 1997 PM2.5 NAAQS and/or 2006
PM2.5 NAAQS. Some areas designated nonattainment for the
2006 PM2.5 NAAQS also are designated nonattainment for the
1997 PM2.5 NAAQS. In addition, some areas are designated for
only the 2006 PM2.5 NAAQS.
These definitions are similar to the rule's definitions in 40 CFR
93.101 for the 1-hour ozone NAAQS and 8-hour ozone NAAQS, and are
generally consistent with how EPA is defining both kinds of
PM2.5 areas for air quality planning purposes. EPA also
notes that any provision of the conformity rule that references only
``PM2.5'' and does not specify which PM2.5 NAAQS
applies to any area designated nonattainment for a PM2.5
NAAQS. EPA received no comments regarding these definitions.
D. How Does This Final Rule Interact With Conformity Requirements for
the 1997 PM2.5 NAAQS?
Sections IV. through VI. of today's final rule describe conformity
requirements for areas designated nonattainment for the 2006
PM2.5 NAAQS. No changes have been made to the existing
transportation conformity requirements for areas designated
nonattainment for the 1997 PM2.5 NAAQS.
Nonattainment designations for the 1997 and 2006 PM2.5
NAAQS are different designations with separate SIP requirements,
different attainment dates, etc. As a result, CAA section 176(c)(5)
requires conformity requirements to be met in both 1997 and 2006
PM2.5 nonattainment and maintenance areas, as applicable.
Some areas designated nonattainment for the 2006 PM2.5
NAAQS have never been subject to PM2.5 conformity
requirements. Under today's final rule and CAA section 176(c)(5), these
areas must meet conformity requirements only for the 2006
PM2.5 NAAQS, and not for the 1997 PM2.5 NAAQS,
because these areas are not designated nonattainment for the 1997
PM2.5 NAAQS.
Other areas designated nonattainment for the 2006 PM2.5
NAAQS have been designated also, in whole or in part, for the 1997
PM2.5 NAAQS. (See Section III.A. for the clarification that
EPA has made in designations for the 1997 PM2.5 NAAQS
areas.) These areas must continue to meet their existing conformity
requirements for the 1997 PM2.5 NAAQS as well as those that
apply for the 2006 PM2.5 NAAQS.
One commenter was concerned that, given identical boundaries, an
area could potentially be required to prepare conformity determinations
for three different PM NAAQS (i.e., the 24-hr PM10 NAAQS,
1997 PM2.5 NAAQS, and 2006 PM2.5 NAAQS), and
believed that this could mean three separate analyses would be
required. This commenter recommended that an area should only have to
model to the most restrictive NAAQS.
As described in the May 2009 proposal, nonattainment designations
for these NAAQS are different designations with separate SIP
requirements, different attainment dates, etc. As a result, CAA section
176(c)(5) requires conformity to be met for all of the NAAQS for which
an area has been designated. However, MPOs subject to more than one PM
NAAQS will be able to use existing transportation models and data for
regional emissions analyses, especially where nonattainment area
boundaries are the same. Some analysis years for the regional emissions
analyses will be the same, such as the last year of the transportation
plan. In addition, MPOs in areas designated for more than one PM NAAQS
will be able to meet consultation and other conformity requirements
through the existing processes.
Furthermore, if an area is designated nonattainment for both the
1997 and 2006 PM2.5 NAAQS and it has no adequate or approved
PM2.5 budgets, it could use the same interim emissions test
for both NAAQS (see Section V.; note that the baseline year for these
two NAAQS are different, see Section IV.) If such an area has budgets
only for the 1997 PM2.5 NAAQS, conformity determinations for
the 2006 PM2.5 NAAQS will be based on the same conformity
test--i.e., the budget test--that is being used for the 1997
PM2.5 NAAQS (note that the attainment year for each of these
NAAQS, which is a required analysis year for the budget test, will
differ). As described in Section VI., MPOs must use any adequate or
approved SIP budgets for the 1997 PM2.5 NAAQS for conformity
determinations that are made prior to SIP budgets for the 2006
PM2.5 NAAQS being found adequate or approved.
Today's final rule does not impact project-level conformity
requirements for the 1997 PM2.5 NAAQS. For example, this
rule does not substantively change the PM2.5 hot-spot
analysis requirements, and EPA and FHWA's existing qualitative guidance
for such analyses continues to be available.\20\ For the purposes of
PM2.5 conformity, a hot-spot analysis must address the
PM2.5 NAAQS for which the area has been designated
nonattainment.\21\ See Section VII. for further information regarding
project-level conformity requirements for the 2006 PM2.5
NAAQS.
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\20\ ``Transportation Conformity Guidance for Qualitative Hot-
spot Analyses in PM2.5 and PM10 Nonattainment
and Maintenance Areas,'' EPA420-B-06-902, March 2006.
\21\ EPA notes that today's final rule does not address project
requirements for the National Environmental Policy Act or other
environmental programs.
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EPA will work with PM2.5 nonattainment areas as needed
to ensure that state and local agencies can meet conformity
requirements for both the applicable 1997 and 2006 PM2.5
NAAQS in a timely and efficient manner.
E. Precursors That Apply for 2006 PM2.5 Conformity
The existing transportation conformity rule at 40 CFR 93.102(b)
describes the pollutants and precursors that must be examined in a
regional emissions analysis in PM2.5 areas, and these
provisions apply to 2006 PM2.5 areas as well as 1997
PM2.5 areas. Direct PM2.5 must be analyzed per 40
CFR 93.102(b)(1). Before SIP budgets are adequate or approved,
NOX must also be analyzed, unless both EPA and the state air
quality agency find that transportation-related emissions of
NOX are not a significant contributor to the
PM2.5 nonattainment problem and notify the MPO and DOT (40
CFR 93.102(b)(iv)).\22\ Before SIP budgets are adequate or approved,
VOCs, sulfur dioxide, and ammonia do not have to be analyzed unless
either EPA or the state air quality agency finds that such a precursor
is a significant contributor, and notifies the MPO and DOT (40 CFR
93.102(b)(v)). Similarly, before SIP budgets are adequate or approved,
road dust does not have to be included in the regional emission
analysis of directly
[[Page 14265]]
emitted PM2.5 unless EPA or the state air agency find that
re-entrained road dust emissions are a significant contributor, and
notifies the MPO and DOT (40 CFR 93.102(b)(3)).
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\22\ Note that instead of establishing a budget for direct
PM2.5 or NOX, a SIP could demonstrate that the
pollutant or precursor is insignificant based on 40 CFR 93.109(k).
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Once budgets from a submitted PM2.5 SIP have been found
adequate or approved, a conformity determination for the 2006
PM2.5 NAAQS must include any precursors for which budgets
are established (40 CFR 93.102(b)(iv) and (v)). If road dust is
included in the direct PM2.5 budget, it must also be
included in a regional emissions analysis (40 CFR 93.102(b)(3)).
Please use the interagency consultation process if there are
questions regarding whether a regional emissions analysis for the 2006
PM2.5 NAAQS must include specific precursors or road dust.
IV. Baseline Year for Certain 2006 PM2.5 Nonattainment Areas
A. Background
Conformity determinations for transportation plans, TIPs, and
projects not from a conforming transportation plan and TIP must include
a regional emissions analysis that fulfills CAA provisions. The
conformity rule provides for several different regional emissions
analysis tests that satisfy CAA requirements in different situations.
Once a SIP with a motor vehicle emissions budget (``budget'') is
submitted for an air quality NAAQS and EPA finds the budget adequate
for conformity purposes or approves it as part of the SIP, conformity
is demonstrated using the budget test for that pollutant or precursor,
as described in 40 CFR 93.118.
Before an adequate or approved SIP budget is available, conformity
of the transportation plan, TIP, or project not from a conforming
transportation plan and TIP is demonstrated using the interim emissions
test(s), as described in 40 CFR 93.119. The interim emissions tests
include different forms of the ``build/no-build'' test and ``baseline
year'' test. In general, for the baseline year test, emissions from the
planned transportation system are compared to emissions that occurred
in the baseline year. Today's rule updates section 93.119 of the
conformity rule for the 2006 PM2.5 NAAQS. The baseline year
for nonattainment areas under the 1997 PM2.5 NAAQS is 2002
(40 CFR 93.119(e)(2)). Sections V. and VI. of today's final rule go
into further detail about how the baseline year will be applied in 2006
PM2.5 areas.
B. Baseline Year for 2006 PM2.5 Areas
1. Description of Final Rule
In today's final rule, EPA is defining the baseline year as the
most recent year for which EPA's Air Emissions Reporting Requirements
(AERR) (40 CFR Part 51) requires submission of on-road mobile source
emissions inventories,\23\ as of the effective date of EPA's
nonattainment designations for any PM2.5 NAAQS other than
the 1997 PM2.5 NAAQS. EPA had proposed this definition under
``Option 2'' in the proposed rule. AERR requires on-road mobile source
emission inventories to be submitted every three years, for example,
2002, 2005, 2008, 2011, etc. See Sec. 93.119(e)(2)(B) for the
regulatory text.
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\23\ 40 CFR 51.30(b).
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Today's final rule results in a baseline year of 2008 for the 2006
PM2.5 areas. The year 2008 is the most recent year as of the
effective date of the 2006 PM2.5 designations, December 14,
2009, for which AERR requires submission of on-road mobile source
emissions inventories. In other words, the designations were effective
on December 14, 2009, and the most recent year for which an on-road
mobile source inventory was required as of that date was 2008.
Therefore, 2008 is the baseline year for 2006 PM2.5 areas.
This final rule would also govern the baseline year for conformity
purposes for any areas designated for a PM2.5 NAAQS that EPA
promulgates in the future. EPA will clarify the relevant baseline year
under today's regulation for each such future NAAQS for conformity
implementers in guidance and maintain a list of baseline years that
result from today's final rule on EPA's Web site.\24\
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\24\ See https://www.epa.gov/otaq/stateresources/transconf/index.htm.
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Today's action does not change the 2002 baseline year for areas
designated nonattainment for the 1997 PM2.5 NAAQS and the
conformity rule now clarifies that 2002 applies as the baseline year
only to areas designated nonattainment for the 1997 PM2.5
NAAQS. The baseline year for 1997 PM2.5 NAAQS areas is found
in Sec. 93.119(e)(2)(A).
The existing interagency consultation process (40 CFR
93.105(c)(1)(i)) must be used to determine the latest assumptions and
models for generating baseline year motor vehicle emissions to complete
any baseline year test. The baseline year emissions level that is used
in conformity must be based on the latest planning assumptions
available, the latest emissions model, and appropriate methods for
estimating travel and speeds as required by 40 CFR 93.110, 93.111, and
93.122 of the current conformity rule. The baseline year test can be
completed with a submitted or draft baseline year motor vehicle
emissions SIP inventory, if the SIP reflects the latest information and
models. If such a SIP baseline is not available, an MPO, in
consultation with state and local air agencies, could also develop
baseline year emissions as part of the conformity analysis.
2. Rationale and Response to Comments
General overview. EPA believes that today's definition for the
baseline year results in an environmentally protective and legal
baseline year for conformity under the 2006 PM2.5 NAAQS and
any future PM2.5 NAAQS revisions, and best accomplishes
several important goals.
First, as EPA discussed in the preamble to the proposed rule, EPA
believes that a more recent year than 2002 (the baseline year for 1997
PM2.5 areas) is appropriate for meeting CAA conformity
requirements for 2006 PM2.5 nonattainment areas. EPA also
believes that using a more recent year is more environmentally
protective than 2002, and more relevant for the 2006 PM2.5
NAAQS. Several commenters agreed with these points. Because the AERR
requires submission of inventories every three years, today's final
rule results in a baseline year that is recent for any PM2.5
NAAQS established after 1997. The baseline year will always be either
the same year as the year in which designations are effective, or one
or two years prior to the effective date of designations. For example,
in the case of the 2006 PM2.5 NAAQS, the baseline year,
2008, is the year before the year in which designations are effective,
2009.
EPA had also proposed 2005 as a baseline year as it is also more
recent than 2002. One commenter preferred a 2005 baseline year because
the introduction of Tier 2 and improved fuel and engine technologies
since then would allow transportation plans and TIPs to meet conformity
more easily. However, because of the implementation of EPA's Tier 2
Vehicle and Gasoline Program as well as other federal programs, motor
vehicle emissions in the year 2005 were higher than emissions in the
year 2008. Thus today's rule, which results in a baseline year of 2008,
provides more protection for the environment than would a baseline year
of 2005, in the time before an area has adequate or approved motor
vehicle emissions budgets from a SIP that addresses PM2.5.
Second, today's baseline year definition coordinates the conformity
[[Page 14266]]
baseline year with other air quality planning requirements, which
allows state and local governments to use their resources more
efficiently. Coordinating the conformity baseline year with the year
used for SIP planning and an emission inventory year was EPA's
rationale for using 2002 as the baseline year for conformity tests in
existing PM2.5 nonattainment areas for the 1997 NAAQS.
Today's regulatory text results in a conformity baseline year that is
consistent with emission inventory requirements, and most likely will
be consistent with the baseline year used for SIP planning as well.
Several commenters voiced support for coordinating the conformity
baseline year with these other air quality planning requirements.
Third, today's final rule provides transportation planners with
knowledge of the baseline year for any future PM2.5 NAAQS
upon the effective date of designations for that NAAQS, without having
to wait either for EPA to amend the transportation conformity rule or
select a SIP planning baseline year. As a result, MPOs and other
transportation planners would understand conformity requirements for
future PM2.5 NAAQS revisions more quickly, which may, in
turn, also allow more time to prepare and complete necessary conformity
determinations. Several commenters agreed that not having to wait for a
rule revision would be a benefit of defining the baseline year as in
today's rule, rather than choosing a specific year. Some commenters
preferred defining the baseline year in terms of the year used as the
baseline year for SIP planning. Today's final rule addresses these
concerns since it will most likely result in a conformity baseline year
that is consistent with the SIP baseline year, and in the future will
give transportation planners the advantage of knowing the baseline year
at the beginning of the grace period for newly designated areas.
Last, given that the CAA requires EPA to review the NAAQS for
possible revision once every five years, today's baseline year
provision potentially reduces the need for future rule revisions for
any future PM2.5 NAAQS.
While today's final rule establishes a baseline year for any
PM2.5 NAAQS other than the 1997 PM2.5 NAAQS, the
same rationale would apply for establishing the same type of baseline
year definition for any future new or revised NAAQS of a
transportation-related criteria pollutant. Therefore, EPA may amend the
rule in the future to apply the baseline year language found in today's
Sec. 93.119(e)(2)(B) more generally. However, EPA did not propose such
an amendment, and intends to solicit and consider public comment before
it would adopt any such provision.
Specific comments. EPA is responding today to several comments
regarding the baseline year. A couple of commenters indicated that they
thought proposed Option 2 would create a ``rolling'' baseline year,
that is, one that would be updated every three years. One commenter did
not support such a rolling baseline; another did support it as long as
motor vehicle emissions in an inventory year were less than the prior
reporting year. However, today's final rule does not establish a
rolling baseline year for any PM2.5 NAAQS. It establishes a
single baseline year for each PM2.5 NAAQS that does not
change over time. For example, for the 2006 PM2.5 NAAQS, the
definition results in a baseline year of 2008. The year 2008 will
remain the baseline year for 2006 PM2.5 areas until it's no
longer needed, i.e., until adequate or approved budgets are available
in a given area.
One commenter who supported the option finalized in today's rule
expressed concern that final emissions data would not be available for
2008 for some time. However, if a final AERR inventory for 2008 is not
available in a particular area, there are other options for generating
the motor vehicle emissions in the baseline year, discussed above under
``IV.B.1. Description of Final Rule.''
Another commenter expressed concern that MOVES would not be
available in time for the year 2008 for the first conformity
determination for the 2006 PM2.5 NAAQS. At this time, the
current emissions model, MOBILE6.2, applies for conformity in all areas
except California, where EMFAC2007 applies. Therefore, if the MOVES
model is not available to generate a 2008 baseline estimate for use in
conformity, the MOBILE6.2 model must be used. Once MOVES is available,
areas can create a new baseline emissions estimate for use in
conformity using MOVES along with other interim analysis years. EPA
will provide a policy guidance document for using MOVES in conformity
determinations that will include more details about when MOVES must be
used. When available, this guidance will be found on EPA's Web site at:
https://www.epa.gov/otaq/stateresources/transconf/policy.htm#models. For
more information on MOVES, please see EPA's Web site at: https://www.epa.gov/otaq/models/moves/index.htm.
One commenter thought that the baseline year should be determined
through interagency consultation. This was not a proposed option.
However, EPA believes that details for the baseline year test must be
determined through rulemaking, as EPA has done for other NAAQS since
1993. Today's rule better accomplishes the purposes of meeting the
CAA's requirements, coordinating with SIP and inventory planning, and
providing certainty to transportation planners. Furthermore, today's
rule ensures consistency across the nation, whereas allowing each area
to determine its own baseline year through interagency consultation
could result in different baseline years in different areas.
V. Regional Conformity Tests in 2006 PM2.5 Nonattainment
Areas That Do Not Have Adequate or Approved SIP Budgets for the 1997
PM2.5 NAAQS
This section of the preamble discusses regional conformity tests
for nonattainment areas for the 2006 PM2.5 NAAQS that do not
have adequate or approved PM2.5 SIP budgets for the 1997
NAAQS. This part of the final rule applies to 2006 PM2.5
nonattainment areas that were not covered by the 1997 PM2.5
NAAQS, as well as nonattainment areas for both PM2.5 NAAQS
that do not have an adequate or approved 1997 PM2.5 SIP
budget. EPA has addressed conformity tests for these areas under
section 93.109(j) of the conformity rule. See Section VI. of today's
final rule for conformity tests in 2006 PM2.5 areas that
have adequate or approved SIP budgets for the 1997 PM2.5
NAAQS.
Note that the rule finalizes new requirements for conformity only
under the 2006 PM2.5 NAAQS. Today's final rule does not
address or change the requirements for demonstrating conformity for the
1997 PM2.5 NAAQS.
A. Conformity After 2006 PM2.5 SIP Budgets Are Adequate or Approved
1. Description of Final Rule
Once a SIP for the 2006 PM2.5 NAAQS is submitted with a
budget(s) that EPA has found adequate or approved, the budget test must
be used in accordance with 40 CFR 93.118 to complete all applicable
regional emissions analyses for the 2006 PM2.5 NAAQS. This
requirement is found at Sec. 93.109(j)(2). Conformity is demonstrated
if the transportation system emissions reflecting the proposed
transportation plan, TIP, or project not from a conforming
transportation plan and TIP are less than or equal to the motor vehicle
emissions budget level defined by the SIP as being consistent with CAA
requirements.
The first SIP for the 2006 PM2.5 NAAQS could be a
control strategy SIP
[[Page 14267]]
required by the CAA (i.e., reasonable further progress SIP or
attainment demonstration) or a maintenance plan. States could also
voluntarily choose to submit an ``early progress SIP'' prior to
required SIP submissions. Early progress SIPs must demonstrate a
significant level of future emissions reductions from a previous year's
emissions. For example, an area could submit an early progress SIP for
the 2006 PM2.5 NAAQS that demonstrates a specific percentage
of emissions reductions (e.g. 5-10%) in an area's attainment year from
the baseline year emissions (e.g., 2008). An early progress SIP would
include emissions inventories for all emissions sources for the entire
2006 PM2.5 nonattainment area and would meet applicable
requirements for reasonable further progress SIPs. EPA has discussed
this option in past conformity rule preambles, e.g. the July 1, 2004
transportation conformity final rule (69 FR 40028), and many states
have established early progress SIP budgets for conformity purposes.
Whatever the case, the interim emissions test(s) would no longer be
used for direct PM2.5 or a relevant precursor once an
adequate or approved SIP budget for the 2006 PM2.5 NAAQS is
established and effective for the pollutant or precursor. States are
required to develop their future 2006 PM2.5 SIPs in
consultation with MPOs, state and local transportation agencies, and
local air quality agencies in an effort to facilitate future conformity
determinations. EPA Regions will be available to assist states in the
development of early progress SIPs for the 2006 PM2.5 NAAQS,
if desired.
2. Rationale and Response to Comments
EPA believes that this provision meets statutory requirements for
conformity determinations that occur after SIP budgets are available
for the 2006 PM2.5 NAAQS. Section 176(c) of the CAA states
that transportation activities must ``conform to an implementation
plan[hellip]'' (SIP) and states further that conformity to an
implementation plan means conformity to the SIP's purpose. Once EPA
finds a budget for the 2006 PM2.5 NAAQS adequate or approves
the SIP that includes it, the budget test provides the best means to
determine whether transportation plans and TIPs meet the statutory
obligations in CAA sections 176(c)(1)(A) and (B) for that NAAQS. That
is, the budget test best shows that transportation plans and TIPs
conform to the SIP's purpose of eliminating or reducing the severity
and number of violations of the NAAQS and achieving expeditious
attainment of the NAAQS (176(c)(1)(A)); and best confirms the
requirement that transportation plans and TIPs not cause or contribute
to any new violation, worsen an existing violation, or delay timely
attainment or any interim milestones (176(c)(1)(B)). The budget test
also best demonstrates that transportation plans and TIPs comply with
the statutory obligation to be consistent with the emissions estimates
in SIPs, according to CAA section 176(c)(2)(A). By being consistent
with the on-road mobile source emissions levels in the SIP,
transportation planners can ensure that their activities remain
consistent with state and local air quality goals to protect public
health. EPA received no comments on this aspect of today's rule.
B. Conformity Before 2006 PM2.5 SIP Budgets Are Adequate or Approved
1. Description of Final Rule
The 2006 PM2.5 nonattainment areas that do not have
existing adequate or approved PM2.5 budgets for the 1997
PM2.5 NAAQS must meet one of the following interim emissions
tests for conformity determinations conducted before adequate or
approved 2006 24-hour PM2.5 SIP budgets are established:
The build-no-greater-than-no-build test (``build/no-build
test''), or
The no-greater-than-baseline year emissions test
(``baseline year test'').
This aspect of today's final rule is similar to the transportation
conformity rule at 40 CFR 93.119(e) for nonattainment areas for the
1997 PM2.5 NAAQS. Today's final rule allows 2006
PM2.5 nonattainment areas without SIP budgets to choose
between the two interim emissions tests, rather than require that one
specific test or both tests be completed. Conformity is demonstrated
if, for each analysis year, the transportation emissions reflecting the
proposed transportation plan or TIP (build) are less than or equal to
either the emissions from the existing transportation system (no-
build), or the level of motor vehicle emissions in the baseline year,
as described in 40 CFR 93.119. For the discussion of the baseline year
for the 2006 PM2.5 NAAQS, please refer to Section IV. of
today's notice.
2. Rationale and Response to Comments
EPA believes that this provision of today's rule meets statutory
requirements for conformity determinations that occur before SIP
budgets are available for the 2006 PM2.5 NAAQS. EPA believes
it is appropriate to provide flexibility and allow 2006
PM2.5 areas to meet only one interim emissions test bef