Approval and Promulgation of Air Quality Implementation Plans; District of Columbia, Maryland, Virginia; 1-Hour Ozone Attainment Plans, Rate-of-Progress Plans, Contingency Measures, Transportation Control Measures, VMT Offset, and 1990 Base Year Inventory, 25688-25719 [05-9401]
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[RME NO. R03–OAR–2004–DC–0009, R03–
OAR–2004–DC–0010; FRL–7910–3]
Approval and Promulgation of Air
Quality Implementation Plans; District
of Columbia, Maryland, Virginia; 1Hour Ozone Attainment Plans, Rate-ofProgress Plans, Contingency
Measures, Transportation Control
Measures, VMT Offset, and 1990 Base
Year Inventory
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: EPA is approving State
Implementation Plan (SIP) revisions
submitted by the District of Columbia
(the District), the State of Maryland and
the Commonwealth of Virginia. These
revisions include the 1996–1999 and
1999–2005 rate-of-progress (ROP) plans,
changes to the 1990 base year inventory,
a contingency measures plan, certain
transportation control measures (TCMs),
and a demonstration that each SIP
contains any necessary transportation
control measures to offset any growth in
emissions from growth in vehicle miles
traveled (VMT) and to demonstrate ROP
and attainment of the 1-hour national
ambient air quality standard (NAAQS)
for ozone. These revisions also include
the District’s and Virginia’s attainment
plan for the Washington, DC severe 1hour ozone nonattainment area (the
Washington area). The intended effect of
this action with respect to the following
SIP revisions, all of which were
submitted to satisfy the SIP
requirements of 1-hour ozone
nonattainment areas classified as severe,
is to: approve the District’s, Maryland’s
and Virginia’s modeling demonstration,
which includes the analysis based upon
photochemical grid modeling, that the
Washington area will attain the 1-hour
ozone NAAQS; approve the District’s,
Maryland’s and Virginia’s post-1996
ROP plans, 1990 base year inventory
revisions, TCMs, VMT offset and
contingency measures SIP revisions;
approve the District’s and Virginia’s
attainment plans for the Washington
area; and, determine that Maryland’s
SIP for the Washington area contains
adopted control measures and
determine that these measures fully
satisfy the emission reductions relevant
to attainment of the 1-hour ozone
NAAQS.
Effective Date: This final rule is
effective on June 13, 2005.
ADDRESSES: EPA has established a
docket for this action under Regional
Material in EDocket (RME) ID Number
R03–OAR–2004–DC–0010. All
documents in the docket are listed in
the RME index at https://
www.docket.epa.gov/rmepub/. Once in
the system, select ‘‘quick search,’’ then
key in the appropriate RME
identification number. Although listed
in the electronic docket, some
information is not publicly available,
i.e., confidential business information
(CBI) or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically in RME or
DATES:
in hard copy for public inspection
during normal business hours at the Air
Protection Division, U.S. Environmental
Protection Agency, Region III, 1650
Arch Street, Philadelphia, Pennsylvania
19103. Copies of the State submittal are
available at the District of Columbia
Department of Public Health, Air
Quality Division, 51 N Street, NE.,
Washington, DC 20002; the Maryland
Department of the Environment, 1800
Washington Boulevard, Suite 705,
Baltimore, Maryland 21230; and the
Virginia Department of Environmental
Quality, 629 East Main Street,
Richmond, Virginia 23219.
FOR FURTHER INFORMATION CONTACT:
Christopher Cripps, (215) 814–2179, or
by e-mail at cripps.christopher@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
A. Summary
On January 12, 2005 (70 FR 2085),
EPA published a notice of proposed
rulemaking (NPR) for the District, the
State of Maryland and the
Commonwealth of Virginia (the States).
The NPR proposed approval of the
1996–1999 and 1999–2005 ROP plans,
changes to the 1990 base year inventory,
a contingency measures plan, certain
TCMs, and a demonstration that each
SIP contains sufficient transportation
control measures to offset any growth in
emissions from growth in VMT as
necessary to demonstrate ROP and
attainment of the 1-hour NAAQS for
ozone.
Tables 1 and 2 identify the initial
submittal dates and the dates on which
the States’s submitted amendments for
these plans and measures covered by
our January 12, 2005 NPR:
TABLE 1.—POST 1996–1999 ROP PLANS FROM THE STATES
DC
Initial submittal dates .......................................................
Amended submittal dates ................................................
The post 1996–1999 ROP Plan SIP
revisions also include certain TCMs,
MD 1
November 10, 1997 ...........
May 25, 1999 ....................
December 24, 1997 ...........
May 20, 1999 ....................
VA
December 19, 1997.
May 25, 1999.
specifically those TCMs identified in
Appendix H of the States submittals.
TABLE 2.—ATTAINMENT PLAN, 1999–2005 ROP PLANS, CONTINGENCY MEASURES PLAN, AMENDMENTS TO THE 1990
BASE YEAR INVENTORY, AND VMT OFFSET PLANS
DC
Initial submittal dates .......................................................
Amended submittal dates ................................................
1 Maryland SIP revision submittals labeled as 97–
04 and 99–12.
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MD 2
September 5, 2003 ............
February 25, 2004 .............
September 2, 2003 ............
February 24, 2004 .............
VA
2 Maryland’s identifiers for these SIP revision
submittals are SIP revisions numbers 03–05 and 04–
01.
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August 19, 2003.
February 25, 2004.
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Hereafter, the SIP revisions listed in
Table 2 of this document will be called
the ‘‘February 2004 SIP revisions.’’ The
States’’ February 2004 SIP revisions
include the post 1999–2005 ROP plans,
the VMT Offset SIPs, revisions to the
1990 base year emissions inventory, and
the contingency measures plans for ROP
and attainment for the Washington
area.3 The February 2004 SIP revisions
additionally include certain TCMs,
namely those TCMs identified in
Appendix J of the SIP revision
submittals.
The February 2004 SIP revisions also
included the States’ revised attainment
plans for the Washington area. The
States had initially submitted an
attainment plan for the Washington area
in 1998 with later supplements. These
initial attainment plans were the subject
of two earlier rulemaking actions, 66 FR
586, January 3, 2001, and 68 FR 19106,
April 17, 2003. The dates of submittal
are shown in Table 3 which repeats the
information found in Table 2 of both the
January 3, 2001 and April 17, 2003 final
rules.
TABLE 3.—PREVIOUS ATTAINMENT DEMONSTRATIONS SUBMISSIONS
DC
Initial submittal dates .......................................................
Amendment dates ...........................................................
Supplemental dates .........................................................
Supplemental dates .........................................................
MD 4
April 24, 1998 ....................
October 27, 1998 ..............
February 16, 2000 .............
March 22, 2000 .................
April 29, 1998 ....................
August 17, 1998 ................
February 14, 2000 .............
March 31, 2000 .................
Hereafter those revisions listed in
Table 3 will be called the ‘‘pre-2001 SIP
revisions’’ attainment plan.’’ 5 Hereafter
we refer to the collective grouping of
those SIP revisions listed in Tables 1
and 3 of this document as the ‘‘pre-2001
SIP revisions.’’
In their February 2004 SIP revisions,
each of the States resubmitted to EPA
the attainment plan contained in its
prior SIP revisions’ attainment plan
along with additional elements required
for a severe area attainment plan, such
as a post-1999 ROP plan and the VMT
offset SIPs, a contingency measures plan
to augment the previously submitted
1996–1999 ROP plan and contingency
measures plan, respectively, as well as
other SIP elements not included in the
previous SIP revisions’ attainment plan.
We proposed action on these
attainment plans in a separate NPR
published in the Federal Register on
February 9, 2005 (70 FR 6796). In our
February 9, 2005, NPR, we also
proposed approval of the attainment
plan SIP revisions submitted by the
District and Virginia.
In our February 9, 2005, NPR, with
respect to the State of Maryland’s
attainment plan for the Washington
area, we proposed approval contingent
upon the State submitting an approvable
SIP revision for certain penalty fees,
required by the Clean Air Act (the Act),
prior to the time EPA would issue a
final rule on Maryland’s attainment
plan. In the alternative, we proposed to
disapprove the attainment plan SIP
revision submitted by the State of
Maryland for the Washington area and
to issue a protective finding for the
attainment plan which would allow the
motor vehicle emissions budgets
(MVEBs) identified in the attainment
plan SIP to be used for demonstrating
transportation conformity purposes.
EPA has taken a final action on the
Maryland’s attainment plan for the
Washington area in a separate final rule
which is published elsewhere in today’s
Federal Register. In that final rule, EPA
is disapproving the Maryland’s
attainment plan for the Washington area
because Maryland failed to submit the
required fee program, and, pursuant to
40 CFR 93.120(a), and issuing a
protective finding to the February 2004
SIP revisions’ attainment plan. As we
explain in that rule, the protective
finding will allow Maryland to use the
MVEBs contained in the disapproved
SIP for transportation conformity
purposes pursuant to 40 CFR 93.120. In
this rule we are approving the modeling
demonstration, which includes an
analysis based upon photochemical grid
modeling (the modeled demonstration
of attainment and adjunct weight-ofevidence (WOE) analysis), contained in
the District’s, Maryland’s and Virginia’s
February 2004 SIP revisions. We also
determine that based upon this modeled
demonstration of attainment and
adjunct WOE analysis Maryland’s
submitted SIP for the Washington area
contains adopted control measures that
fully satisfy the emission reduction
requirements relevant to the
Washington area attaining the 1-hour
ozone NAAQS by November 15, 2005.
This determination supports issuance of
the protective finding for transportation
3 In this document a SIP revision which
demonstrates the state’s SIP contains any necessary
transportation control measures to offset any growth
in emissions from growth in VMT needed to
demonstrate ROP and attainment of the 1-hour
NAAQS for ozone is termed a ‘‘VMT offset SIP.’’
4 Maryland’s identifiers for the February 14, 2000
and March 31, 2002 submittals are SIP revisions
numbers 00–01 and No. 00–02.
5 Only a commitment to revise the motor vehicle
emissions budgets (MVEBs) found in the March
2000 SIP revisions listed in Table 3 of this
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VA
April 29, 1998.
August 18, 1998.
February 9, 2000.
March 31, 2000.
conformity purposes pursuant to 40 CFR
93.120.
B. Relationship to Past SIP Revisions
and Litigation
1. Prior SIP Revisions
During 1998, the States submitted an
attainment plan for the Washington area
and supplemented these submittals on
the dates listed in Table 3 of this
document. These 1998 and 2000
calendar year revisions cumulatively
constituted the attainment plan for the
Washington area which at the time was
classified as being in ‘‘serious’’
nonattainment of the 1-hour ozone
NAAQS. In the aggregate these
attainment plans consisted of a
photochemical modeling demonstration
and adjunct WOE analyses that
demonstrated attainment of the ozone
NAAQS; projected emissions
inventories showing that the States
collectively had adopted sufficient
measures to support the demonstration
of attainment; attainment year MVEBs;
and a commitment to conduct and
submit a mid-course review to EPA by
a date certain. As noted previously, the
March 2000 SIP revisions consisted of a
commitment to revise the MVEBs oneyear after EPA released the MOBILE6
model and the outyear budgets. These
pre-2001 SIP revisions’ attainment plans
were submitted to demonstrate that the
Washington area would attain the 1hour ozone NAAQS by no later than
November 15, 2005. On January 3, 2001,
EPA approved the pre-2001 SIP
revisions and extended the attainment
date for the Washington area (then a
document were subject to the January 3, 2001 and
April 17, 2003 final rules. The portion of these SIP
revisions related to MVEBs for years after 2005
(‘‘outyear budgets’’) was not subject to these
actions.
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serious nonattainment area) until
November 15, 2005.
2. January 3, 2001 Final Rule Vacated
A petition for review challenging the
January 3, 2001 final approval was filed
by the Sierra Club. The petition alleged,
among other things, that EPA could not
lawfully extend the attainment date of a
serious ozone nonattainment area past
November 15, 1999 without
reclassifying the area as severe
nonattainment, could not approve a SIP
for an area with a 2005 attainment date
unless the plan provides for ROP
reductions after 1999 and could not
approve a SIP that does not include
contingency measures. On July 2, 2002,
the U.S. Court of Appeals for the District
of Columbia Circuit (the Court of
Appeals) issued an opinion to vacate
our rule extending the attainment date
and approving the attainment plans and
1996–1999 ROP plans. Among other
things, the Court of Appeals found that
EPA had no authority to extend the
attainment date of a serious ozone
nonattainment area without
reclassifying the area as severe
nonattainment, and could not approve a
SIP for an area with a 2005 attainment
date unless the plan provides for ROP
reductions until the attainment date.
See Sierra Club v. Whitman, 294 F.3d
155, 160–163 (D.C. Cir. 2002). The Court
of Appeals also found that EPA could
not approve the pre-2001 SIP revisions
because a contingency measures plan,
which is required under section
172(c)(9) of the Act, is one of the
elements listed under section 172(c) as
a requirement for a revised SIP for an
area in nonattainment. See Id. at 164.
3. Nonattainment Area Plan
Requirements
Under section 172(c) of the Act, a
revised SIP for an area in nonattainment
must also include elements such as an
attainment demonstration and all
reasonably available control measures
(RACM), reasonable further progress
toward attainment, an emissions
inventory, and new source permitting
programs. Under section 182(d), a
revised SIP for an area in severe ozone
nonattainment must include reasonably
available control technology (RACT) on,
and new source review (NSR)
permitting of, major stationary sources
of nitrogen oxides (NOX) emissions and
volatile organic compound (VOC)
emissions with a potential to emit of 25
tons per year (TPY) or greater; new
source permitting offset ratios of 1.3 to
1 or greater; a VMT Offset SIP; a ROP
plan to achieve a 15 percent reduction
in VOC emissions by 1996; plans for
achieving an average of a 3 percent per
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year ROP reductions after 1996 through
the attainment date; and a SIP revision
to impose the penalty fees specified in
section 185 of the Act.
EPA believes Sierra Club v. Whitman,
294 F.3d 155, can be read to require that
before we can approve the overall
revised SIP for the nonattainment area
we must approve all of the elements
applicable to the area under sections
172(c) and 182 of the Act. In this
document, the overall SIP for the
nonattainment area will be termed the
‘‘attainment plan.’’
Under section 182 of the Act, a
demonstration that the SIPs for a
nonattainment area, as revised, will
provide for attainment of the 1-hour
ozone NAAQS by November 15, 2005 is
a separate component of the overall
attainment plan. See 42 U.S.C.
7511a(c)(2)(A). Such a demonstration
for a severe ozone nonattainment area
must be based upon photochemical grid
modeling (or similarly effective method)
and must show that the submitted
demonstration relies upon or contains
adopted control measures that fully
satisfy the emission reduction
requirements relevant to demonstrating
attainment of the 1-hour ozone NAAQS
by November 15, 2005. Id.
4. Washington Area Reclassified to
Severe Nonattainment
On January 24, 2003 (68 FR 3410),
EPA reclassified the Washington area to
severe nonattainment because the area
failed to attain 1-hour ozone NAAQS by
the November 15, 1999 statutory
attainment date for serious areas. This
action made the area subject to the
additional requirements applicable to
severe areas under section 182(d) of the
Act. On April 17, 2003 (68 FR at 19107),
EPA conditionally approved the pre2001 SIP revisions (the history of
litigation on the April 17, 2003
conditional approval will be discussed
in a later paragraph of this document
titled ‘‘April 17, 2003 Final Rule
Vacated and Withdrawn’’).
5. Recent SIP Revision Actions
In the months that followed the
January 24, 2003 reclassification of the
Washington area to severe
nonattainment and the April 17, 2003
conditional approval, the States
submitted the SIP revisions necessary to
satisfy the requirements of section
182(d) of the Act for severe areas and
EPA’s conditional approval, with the
exception of Maryland which failed to
submit a SIP revision for the section 185
penalty fee program. These SIP
revisions included February 2004 SIP
revisions. The February 2004 SIP
revisions contained the attainment plan
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which consists of: (1) A photochemical
modeling demonstration and adjunct
WOE analyses to demonstrate
attainment of the ozone NAAQS by no
later than November 15, 2005; (2)
projected emissions inventories
showing that the States, including
Maryland, collectively had adopted
sufficient measures to support the
demonstration of attainment; (3)
attainment year MVEBs; and (4) a
commitment to conduct and submit a
mid-course review to EPA by a date
certain.6 In their February 2004 SIP
revisions, each of the States resubmitted
to EPA the attainment plan contained in
the State’s pre-2001 SIP revisions’
attainment plan along with additional
elements required for a severe area
attainment plan, such as a 1999–2005
ROP plan, and a contingency measures
plan to augment the previously
submitted 1996–1999 ROP plan and
contingency measures plan,
respectively, as well as other SIP
elements not included in the pre-2001
SIP revisions’ attainment plan.
6. April 17, 2003 Final Rule Vacated
and Withdrawn
A petition for review challenging the
April 17, 2003 final conditional
approval was filed by the Sierra Club.
The petition alleged, among other
things, that EPA could not lawfully
conditionally approve the SIPs due to a
lack of specificity in the States’
commitment letters, that EPA should
require the 1996–1999 ROP to be
revised to use the latest mobile sources
emission factor model and that the
photochemical grid modeling
supporting the attainment plan did not
meet the requirements of the Act. On
February 3, 2004, the Court of Appeals
issued an opinion to vacate our rule
conditionally approving the attainment
plans and 1996–1999 ROP plans insofar
as that Court found that our grant of
conditional approval was defective. The
Court of Appeals denied the petition for
review in all other respects. See Sierra
Club v. EPA, 356 F.3d 296, 301–07 (D.C.
Cir. 2004). On April 23, 2004, the Court
of Appeals issued its mandate thereby
relinquishing jurisdiction over the
1996–1999 ROP plans and the
attainment plan SIP revisions, and
remanding them back to EPA.7
6 The February 2004 SIP revisions did not need
to contain a commitment to revise the MVEBs oneyear after EPA released the MOBILE6 model
because the MVEBs in these plans were developed
using MOBILE6.
7 On April 16, 2004, the Court of Appeals issued
an order revising the February 3, 2004, opinion to
address a petition for rehearing filed by the Sierra
Club, but otherwise leaving its decision to vacate
and remand the conditional approval to EPA intact.
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Effective as of the April 23, 2004 date
the Court of Appeals issued its mandate
for its February 3, 2004 ruling, all three
States withdrew their pre-2001 SIP
revisions’ attainment plan which had
been submitted during 1998 and 2000,
specifically the SIP revisions listed in
Table 2 of the April 17, 2003, final rule
(68 FR 19107). By the time the three
States withdrew the pre-2001 SIP
revisions’ attainment plan, they had
already submitted revised attainment
plan SIP revisions with an analysis that
the SIPs contained all RACM, post-1999
ROP plans demonstrating ROP for 2002
and 2005, VMT offset plans and
contingency measures plans that
superceded the earlier submissions. The
States, in their February 2004 SIP
submissions, submitted not only this
new material, but resubmitted all of the
previously withdrawn pre-2001 SIP
revisions’ attainment plan.8 The newly
submitted materials along with the
resubmitted pre-2001 SIP revisions’
attainment plan, form a single
comprehensive package. EPA is taking
final action today on both the newly
submitted and resubmitted materials,
which we collectively refer to as the
February 2004 SIP revisions.
7. District Court Action
The Sierra Club filed a complaint in
the United States District Court for the
District of Columbia (District Court)
claiming that because the Court of
Appeals vacated and remanded the
conditional approval of the pre-2001 SIP
revisions’ attainment demonstration and
the 1996–1999 ROP plans, EPA had an
unfulfilled nondiscretionary duty to
complete final action on those SIP
revisions. On April 7, 2005, the District
Court issued an order enjoining EPA to
‘‘complete final approval and
disapproval action, in accordance with
42 U.S.C. 7410(k)(2), (3), on the state
implementation plan submittals for the
Washington area identified at 66 FR
586, 586 (January 3, 2001).’’ Sierra Club
v. Johnson, C.A. No. 04–2163 (JR) (April
7, 2005). The District Court’s decision
took note ‘‘that the states formally
withdrew their pre-2001 submissions
(except for the [ROP plans]) after the
D.C. Circuit’s Sierra Club III remand,’’
Id., slip op. at 7, but disputed that
‘‘these withdrawals removed EPA’s duty
to act,’’ stating that ‘‘ ‘withdrawal’ of
pre-2001 SIPs could [not] push back the
deadlines established by Congress.’’
Sierra Club v. EPA, No. 03–1084, 2004 WL 877850
(DC Cir. Apr. 16, 2004).
8 With one exception: the ‘‘outyear budgets,’’
which were contained in the March 31, 2002 SIP
revision on which EPA had never proposed to take
action, were not resubmitted.
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EPA does not dispute that withdrawal
of a SIP cannot push back a statutory
deadline established by Congress.
However, EPA disagrees that it can act
on a SIP submittal formally withdrawn
by a state. We note, however, that such
a withdrawal is not without
consequence, as withdrawal of required
SIP revision puts a state in jeopardy of
sanctions predicated upon a failure to
submit the required SIP. However in
this case, as described in this document,
the States resubmitted the materials
comprising their withdrawn pre-2001
SIP revisions’ attainment plan as part of
the February 2004 SIP submissions. EPA
therefore will take action on what the
District Court termed the ‘‘pre-2001
submissions,’’ 9 as follows:
(1) In this final rule which
(a) approves all of the control
measures and other constituents needed
to approve Maryland’s severe area
attainment plan (except for a Section
185 fee program), including all control
measures need to fully satisfy the
emissions reductions relevant to
attainment of the 1-hour ozone NAAQS;
(b) approves all of the control
measures and other constituents needed
to approve the District’s and Virginia’s
severe area attainment plan;
(c) approves the 1996–1999 ROP plan
for the District, Maryland and Virginia;
(d) approves Maryland’s modeled
demonstration of attainment and
adjunct weight of evidence analyses;
and
(e) approves the District’s and
Virginia’s modeled demonstrations of
attainment and adjunct weight of
evidence analyses and the District’s and
Virginia’s attainment plans, which
include their pre-2001 SIP revisions’
attainment plan, as resubmitted and
subsumed by their February 2004 SIP
revisions;
(2) Another final rule, which is
published elsewhere in today’s Federal
Register, which disapproves Maryland’s
pre-2001 SIP revisions’ attainment plan
as resubmitted and subsumed by
Maryland’s February 2004 SIP revisions’
attainment plan based upon Maryland’s
failure to submit the required 185 fee
program, and issues a protective finding
on the SIP, based upon our
determination that the SIP contains all
of the control measures necessary to
demonstrate attainment. That protective
finding will allow Maryland to use the
MVEBs contained in the disapproved
SIP for transportation conformity
purposes pursuant to 40 CFR 93.120.
9 The District Court used the term ‘‘pre-2001
submissions’’ and ‘‘pre-2001 SIPs’’ which consists
of what in this document we call ‘‘the pre-2001 SIP
revisions’ attainment demonstration’’ and ‘‘the
1996–1999 ROP plan.’’
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II. The Relationship of Past SIP
Revisions, February 2004 SIP Revisions
and the April 17, 2003 Conditional
Approval
A. The Twelve Conditions for Approval
On April 17, 2003, EPA had
conditionally approved the pre-2001 SIP
revisions subject to the following 12
conditions:
(1) Revise the 1996–1999 portion of
the ROP plans to include a contingency
plan containing adopted measures;
(2) Revise the contingency plan
containing those adopted measures
implemented for the failure of the
Washington area to attain the one-hour
ozone standard for serious areas by
November 15, 1999;
(3) Revise the ROP plans to include a
contingency plan containing adopted
measures for the post-1999 ROP plans;
(4) Revise the attainment
demonstration to include a contingency
plan containing adopted measures to be
implemented if the Washington area
does not attain the one-hour ozone
standard by November 15, 2005;
(5) Revise the ROP plans to
demonstrate emission reductions of
ozone precursors of an average of 3
percent per year from November 15,
1999 to the November 15, 2005;
(6) Revise the attainment
demonstration to include a revised
RACM analysis;
(7) Revise the major stationary source
threshold to 25 tons per year;
(8) Revise RACT rules to include the
lower major source applicability
threshold;
(9) Revise new source review offset
requirements to require an offset ratio of
at least 1.3 to 1.
(10) Submit a SIP revision that
identifies and adopts specific
enforceable transportation control
strategies and transportation control
measures to offset any growth in
emissions from growth in vehicle miles
traveled or number of vehicle trips if
required under section 182(d)(1) of the
Act;
(11) Submit the section 185 penalty
fee SIP consisting of the penalty fee
requirement of Act sections 182(d)(3)
and 185 for major sources of VOC and
NOX should the area fail to attain by
November 15, 2005;
(12) Update the Washington area
severe attainment demonstration to
reflect revised MOBILE6-based motor
vehicle emissions budgets, including
revisions to the attainment modeling/
weight of evidence demonstration and
adopted control measures, as necessary,
to show that the SIP continues to
demonstrate attainment by November
15, 2005.
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In the February 3, 2003 (68 FR 5246)
proposed rule for the April 17, 2003
final conditional approval, we proposed
conditional approval of the pre-2001 SIP
revisions if the State committed to
correct condition numbers (1) through
(3), (6) and (12). EPA revised the
conditional approval to include
condition numbers (4), (5), and (7)
through (11) in response to comment
which stated that EPA could not fully
approve the pre-2001 SIP revisions
because the pre-2001 SIP revisions did
not cover all of the required severe area
SIP components. EPA agreed with the
comment to the extent that condition
numbers (4), (5), and (7) through (11)
were applicable severe area
requirements that precluded full
approval. See 68 FR at 19121, April 17,
2003.
Conditions (1) and (2) were elements
needed to correct deficiencies in the SIP
required for a serious nonattainment
area.
Conditions (4) through (11) are SIP
elements required as a consequence of
the reclassification of the Washington
area to severe nonattainment.
Conditions (3) through (6) were
required to correct deficiencies in the
pre-2001 SIP revisions because the pre2001 SIP revisions included a
demonstration that the Washington area
would attain the 1-hour ozone standard
by November 15, 2005.
We conditioned approval on item (12)
under EPA’s policy related to the
transition from our prior mobile source
emissions factor model, MOBILE5, to
the newer model, MOBILE6.
B. How the States Have Addressed the
Twelve Conditions
In this section we will discuss how
the States have addressed the twelve
conditions. EPA had already approved
many of the States’ SIP revisions for the
control measures needed to support the
attainment plan, the ROP plans and the
contingency measure plan by the time
we published the NPRs on January 12,
2005 (70 FR 2085) and February 9, 2005
NPR (70 FR 6796) for the States’ 1996–
1999 ROP plans and the February 2004
SIP revisions including the resubmitted
pre-2001 SIP revisions’ attainment plan.
In this document we will not reiterate
the specifics of such approvals but will
provide details on the approval of
control measures which were not
approved at the time of the January 12,
2005 and February 9, 2005 NPRs.
1. Conditions 1 to 4—Contingency
Measures
At the time of the January 12, 2005
NPR for the contingency measures plan,
EPA had approved all the contingency
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measures except each of the States’
architectural and industrial
maintenance coatings rules (AIM
coatings rules), and the District’s motor
vehicle refinishing, consumer products,
solvent cleaning and portable fuels
container rules.
On May 2, 2005, the Regional
Administrator signed final rules
approving the District’s, Maryland’s and
Virginia’s AIM coatings rules. Those
final actions have been published in a
recent Federal Register or shortly will
be published in the Federal Register.
On December 23, 2004 (69 FR 76855),
December 28, 2004 (69 FR 77642),
December 29, 2004 (69 FR 77906) and
December 29, 2004 (69 FR 77903), EPA
approved, respectively, the District’s
motor vehicle refinishing, consumer
products, solvent cleaning and portable
fuels container rules.
In this final rule, EPA is approving
the States’s contingency measures plans
for the Washington area. These
contingency measure plans provide
sufficient contingency measures to meet
our 3 percent (relative to baseline
emissions for the Washington area)
reduction for all of the relevant years for
which the States need contingency
measures. Our basis for determining that
the States’ contingency measures plans
get the required reductions is discussed
in detail in section V. ‘‘Contingency
Measures Plans’’ of the January 12, 2005
NPR (70 FR at 2087–2095) and in our
response to comments under sections
III. D. ‘‘Comment on the Contingency
Measures Plans’’ of this document.
EPA finds that the actions cited in the
preceding four paragraphs fulfilled
conditions (1) through (4).
2. Condition 5—Post-1999 ROP
At the time of the January 12, 2005
NPR for the ROP plans and the February
9, 2005 NPR on the attainment
demonstration, EPA had approved all
the control measures except each of the
States’ AIM coatings rules, the District’s
portable fuels container rule, the TCMs
submitted with the 1996–1999 and post1999 ROP plans and Maryland’s and
Virginia’s nonregulatory measures SIP
revisions.
As noted previously, EPA has
approved the States’ AIM coatings rules
and the District’s portable fuel
containers rule. In this action, EPA is
approving the TCMs submitted with the
1996–1999 and post-1999 ROP plans.
On May 2, 2005, the Regional
Administrator signed a final rule
approving Maryland’s and Virginia’s
nonregulatory measures SIP revision.
That final action has been published in
a recent Federal Register or shortly will
be published in the Federal Register.
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In this final rule EPA is approving the
States’ 1996–1999 and post-1999 ROP
plans. Our basis for determining that the
States’ ROP plans get the required post1996 ROP reductions of 3 percent per
year (averaged over consecutive 3-year
periods) is discussed in detail in section
IV. ‘‘Post 1996–1999 and Post 1999–
2005 ROP Plans’’ of the January 12,
2005 NPR (70 FR at 2087–2095) and in
our response to comments under
sections III. A. ‘‘Comment on the ROP
Plans and NOX Substitution’’ and B.
‘‘Comment on the Transportation
Demand Model (TDM) Used in the
Plans’’ of this document.
EPA finds that the actions cited in the
preceding four paragraphs fulfilled
condition (5).
3. Condition 6—RACM
For the reasons cited in our February
9, 2005 NPR, EPA believes that the
States’ attainment demonstration in the
February 2004 SIP revisions
demonstrated that no remaining RACM
remain to be adopted for the
Washington area. We received no
adverse comment on this aspect of the
proposal and find that the States have
fulfilled condition 5 by adoption of all
the measures necessary to demonstrate
attainment as expeditiously as
practicable.
4. Conditions 7 to 9—New Source
Review and RACT Thresholds
EPA has approved a SIP revision to
implement the severe area NSR
requirements in the Washington area for
both VOC and NOX including an offset
ratio of 1.3:1 and a major source
applicability definition of 25 tons/year.
See 69 FR 77647, December 28, 2004; 69
FR 56170, September 20, 2004; and 69
FR 48150, August 9, 2004, for the
District, Maryland, and Virginia,
respectively. For each of the three
States, EPA has fully approved a SIP
revision to implement RACT for major
sources of VOC and NOX with major
source size definition of 25 tons/year.
See 69 FR 77647, December 28, 2004; 69
FR 56170, September 20, 2004; and 69
FR 48150, August 9, 2004, for the
District, Maryland, and Virginia,
respectively. EPA finds that the States
have fulfilled conditions (7) through (9).
5. Condition 10—VMT Offset SIP
In this final rule EPA is approving the
States’ VMT Offset SIP revisions which
fulfills condition (10). Our basis for
determining that the States’ VMT Offset
SIP meets the Act’s requirements is
discussed in detail in section VI.
‘‘Vehicle Miles Traveled (VMT) Offset
SIP and Transportation Control
Measures (TCMs)’’ of the January 12,
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2005 NPR (70 FR at 2098) and in our
response to comments under section III.
C. ‘‘Comment on the VMT Offset SIP’’
of this document.
6. Condition 11—the Section 185
Penalty Fee SIP
On December 28, 2004 (69 FR 77639)
and on December 29, 2004 (69 FR
77909), EPA approved the District’s and
Virginia’s section 185 penalty fee SIP
revisions, respectively, and thus,
believes that the District and Virginia
have fulfilled condition (11). To date,
Maryland has not submitted a section
185 penalty fee SIP revision. For the
lack of a section 185 penalty fee SIP
revision, EPA is disapproving
Maryland’s attainment plan with a
protective finding which will allow the
MVEBs contained in Maryland’s 2004
SIP revisions to be used for
transportation conformity purposes
pursuant to 40 CFR 93.120. That
disapproval is published elsewhere in
today’s Federal Register.
7. Condition 12—MOBILE6-Based
Attainment Plan Budgets
In their February 2004 SIP revisions,
the States adopted MOBILE6-based 2005
attainment year MVEBs. The final
version of the 2005 attainment year
MVEBs was contained in the February
2004 SIP revisions identified in Table 2
of this document. These MVEBs are
area-wide MVEBs which cover the
entire Washington area.
In this final rule EPA is approving the
District’s and Virginia’s attainment plan
for the Washington area, namely the
attainment plans contained in the
February 2004 SIP revisions which
subsumes the resubmitted pre-2001 SIP
revisions’ attainment plan. We are also
approving the final revision of the 2005
attainment year MVEBs for the District
and Virginia found in the February 2004
SIP revisions identified in Table 2 of
this document. EPA would have been
able to approve Maryland’s attainment
plan for the Washington area had
Maryland submitted a section 185
penalty fee program. We could not
approve the District’s and Virginia’s
attainment plan without determining
that the three States collectively have
adopted enough measures in their SIPs
to demonstrate that the area as a whole
will attain the 1-hour ozone NAAQS by
no later than November 15, 2005. Such
a finding is necessary because this is an
interstate area and any potential
emissions shortfall would have to be
addressed collectively before any State’s
attainment plan could be approved.
For the reasons stated in our February
9, 2005 NPR, the recently approved
control measures discussed previously
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in this final action and given in our
responses in this final action to
comments received on that proposed
rule, EPA believes that the States
collectively have adopted enough
measures in their SIPs to demonstrate
that the area will attain the 1-hour
ozone NAAQS by no later than
November 15, 2005 with the MVEBs
found in the February 2004 SIP
revisions identified in Table 2 of this
document. EPA believes that Maryland,
in combination with the District and
Virginia, adopted sufficient measures
and have fully satisfied the emissions
reduction requirements necessary to
ensure that attainment of the 1-hour
ozone NAAQS will be attained by no
later than November 15, 2005. EPA
believes that the States, including
Maryland, have satisfied condition (12)
since they have demonstrated that the
attainment plans have been revised to
reflect MOBILE6-based MVEBS and
have included the necessary revisions to
the modeled demonstration of
attainment and adjunct WOE analyses
and have adopted control measures
showing that the SIP continues to
demonstrate attainment by November
15, 2005.
Therefore, in this final rule, EPA is
approving the District’s, Maryland’s,
and Virginia’s modeled demonstrations
of attainment and adjunct WOE analyses
and the District’s and Virginia’s
attainment plans. EPA is also
determining that the attainment plan for
Maryland contains adopted control
measures that fully satisfy the emission
reduction requirement relevant to
attainment of the 1-hour ozone NAAQS.
EPA is therefore approving the modeled
demonstration of attainment and
adjunct WOE analyses contained in
Maryland’s February 2004 SIP revisions
which includes the analysis based upon
photochemical grid modeling
demonstrating timely attainment of the
1-hour ozone standard. In addition, EPA
is therefore issuing Maryland’s 2004 SIP
revisions’ attainment plan—a protective
finding which will allow the MVEBs
contained in Maryland’s 2004 SIP
revisions to be used for transportation
conformity purposes pursuant to 40 CFR
93.120.
EPA concludes that once we issue our
approval of the District’s and Virginia’s
February 2004 SIP revisions the District
and Virginia will have cured the
deficiencies we identified in their pre2001 SIP revisions through the various
SIP revisions that they have submitted
since April 17, 2003. In the case of
Maryland, EPA concludes that all of the
deficiencies except the section 185
penalty fee SIP revision will have been
cured for Maryland’s pre-2001 SIP
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25693
revisions by the various SIP revisions
submitted since April 17, 2003 once we
issue our approval of:
(1) Maryland’s 1996–1999 and 1999–
2005 ROP plans,
(2) the changes to the 1990 base year
inventory, the contingency measures
plan, TCMs,
(3) the modeled demonstration of
attainment which includes the analysis
based upon photochemical grid
modeling and adjunct WOE analyses
that Maryland’s submitted SIP for the
Washington area contains adopted
control measures that fully satisfy the
emission reduction requirements to
provide for attainment of the 1-hour
ozone NAAQS in the Washington area
by November 15, 2005.
III. Comment Received on the ROP
plans, VMT Offset SIP and Contingency
Measures Plan and EPA’s Response
We received comments adverse to the
proposed approval of the ROP, VMT
offset, contingency measures, and
attainment plans. A summary of these
adverse comments, and our responses,
follows.
A. Comment on the ROP plans and NOX
Substitution
Comment: We received a comment
asserting that the ROP plans do not meet
the requirement of demonstrating a nine
percent reduction in VOC emissions
from 1999 to 2002 and a further nine
percent from 2002 to 2005 because the
NOX substitution in the ROP plans is
impermissible. The comment asserts
that the ROP plans do not meet section
182(c)(2)(c) of the Act because they do
not show that a nine percent reduction
in NOX emissions will result in the
same reduction in ozone concentration
as a nine percent reduction in VOC
emissions. The comment claims that
EPA’s own guidance requires
photochemical grid modeling to show
equivalent changes in ozone
concentrations.
The comment also asserts that EPA’s
reliance on our December 1993 NOX
Substitution Guidance is flawed because
the plain language of the Act requires
proof of equivalent benefits of NOX
substitution. The comment also asserts
that because the 1999–2005 ROP plan
relies solely upon NOX reductions the
plans do not meet the requirement of
section 182(c)(2)(C) because the plan
does not provide for some percentage of
VOC reduction during each period. The
comment claims that the Act requires
some non-zero percentage reduction in
VOC emissions for any ROP period.
The comment asserts that the Act
requires the ROP plans to have VOC
reductions by November 15, 2002 to
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prevent a net increase in VOC emissions
by the 2002 milestone date, which
would offset the progress achieved by
the nine percent NOX reductions. The
comment asserts that while the ROP
plans do provide for such reductions,
EPA cannot approve the 1999–2005
ROP plans because they do not provide
for all of these reductions by the 2002
milestone date.
Response: NOX Substitution in
General. The EPA believes States have
the opportunity to substitute NOX
reductions for required VOC reductions
under certain circumstances. The
opportunity for NOX substitution
originates in section 182(c)(2)(C) of the
Act which specifically allows NOX
emissions reductions to be substituted
for VOC reductions required under
section 182(c)(2)(B) for reasonable
further progress (RFP), sometimes called
ROP.
EPA issued guidance to the States on
how to implement the NOX substitution
provisions for the post-1996 ROP plans
in December 1993 (the December 1993
NOX Substitution Guidance). The
guidance allows States to substitute
NOX emission reductions for VOC
emission reductions if that substitution
is consistent with the demonstration of
attainment in the SIP. The modeled
demonstration of attainment in the SIP
establishes the overall reductions of
VOC and/or NOX reductions required
for attainment in the attainment year.
The ROP plan is a tool to phase in
emission reductions between the time
the plan is prepared and the attainment
date. When substituting NOX for VOC in
post-1996 ROP plans, we are mindful
that if too many NOX reductions are
substituted for VOC reductions, the
modeled demonstration of attainment
may no longer be valid. Our December
1993 NOX Substitution Guidance allows
substitution on a percentage basis (i.e.,
one percent of NOX emissions
reductions can be substituted for one
percent of VOC emissions reductions).
Results of the Application of EPA’s
December 1993 NOX Substitution
Guidance in the Washington Area. EPA
believes that NOX substitution as
applied to the Washington area based on
our December 1993 NOX Substitution
Guidance yields ROP plans that result
in reductions in ozone concentrations
that are better than those which would
have resulted from ROP plans relying
upon an equal percent of VOC
reductions.
Applying our December 1993 NOX
Substitution Guidance to the
Washington area we substitute one
percent of VOC ROP reductions with
one percent of NOX reductions. One
percent of NOX represents a larger
quantity of emissions reduction than
does one percent of VOC. This is the
case because ROP reductions are
computed from baseline emissions,
which are defined in section
182(b)(2)(B) of the Clean Air Act to be
‘‘the total amount of actual VOC or NOX
emissions from all anthropogenic
sources in the area during the calendar
year 1990,’’ excluding the emissions
that would be eliminated by the
programs specified in sections
182(b)(1)(C) and (D) of the Act. The
reduction of baseline emissions by the
programs specified in sections
182(b)(1)(C) and (D) yields the adjusted
1990 base year inventory for each
milestone year (which is discussed
further in the January 5, 2005 technical
support document (TSD) 10). The
adjusted 1990 base year inventory is the
baseline from which the necessary ROP
reductions are computed. Section
182(c)(2) of the Act requires that a set
percentage of reductions in baseline
emissions be achieved every three years
after 1996 until the area’s attainment
date. To determine the reductions in
tons required for any given ROP
milestone year, the percentage is
multiplied by the adjusted 1990 base
year inventory for that milestone year.
For example, in the case of the
Washington area, the ‘‘Adjusted 1990
Base Year Inventory for 2005’’ for VOC
is 412.1 tons per day (TPD), and, thus,
a one percent ROP reduction equates to
4.1 TPD. For NOX emissions the
‘‘Adjusted 1990 Base Year Inventory for
2005’’ is 735.6 TPD, and, thus, a one
percent ROP reduction equates to 7.4
TPD.
The States only modeled changes in
anthropogenic (man-made) emissions to
see how sensitive the Washington area
was to changes in VOC and to NOX
emission reductions. They did not
model changes in biogenic emissions
which are VOC emissions from plants.
The air quality model responds to
changes in emission between the 1990
base year inventory and the emissions
resulting from the control strategy to be
modeled.11
The States used the results of this
sensitivity modeling to determine that a
one ton reduction in NOX emissions
within the Washington area would
result in a peak ozone concentration
reduction of 0.114 parts per billion
(ppb) (0.114 ppb/ton of NOX); a similar
analysis for VOC emissions indicated
that a one ton reduction in VOC
emissions would result in a peak ozone
concentration reduction of 0.029 ppb
(0.029 ppb/ton of VOC reduced). The
States concluded that emissions
reductions of 34.0 tons/day of VOC or
8.8 tons/day NOX would have to be
required within the Washington area
would reduce ozone concentrations by 1
ppb. That is, NOX reductions in the
Washington area have greater ozone
reducing potential than an equivalent
amount of VOC reductions. Therefore,
substituting a percentage of VOC
reductions with an equal percentage of
NOX reductions should result in greater
ozone concentration reduction than if
the substitution were not done.
The 1990 base year VOC inventory for
the Washington area is comprised of
578.7 TPD of anthropogenic emissions
and of 376.5 TPD biogenic emissions for
a total of 955.2 TPD of VOC. The 1990
base year NOX inventory (all of which
is anthropogenic) for the Washington
area is 869.3 TPD of NOX. Given that 39
percent (376.5/955.2) of the VOC
emissions inventory is biogenic
emissions, it is not surprising that
reductions in anthropogenic VOC
emissions would show less ozone
response than an equal percentage
reduction in anthropogenic NOX
emissions. The NOX emissions are all
anthropogenic, and, a one percent
reduction in NOX emissions equates to
more tons of emission reduction than
does one percent reduction of the
anthropogenic VOC emissions.
This is not to say VOC reductions are
not beneficial towards attainment, but
rather that reductions in anthropogenic
VOC emissions are not as effective on a
TPD or ROP percentage basis as NOX
reductions. However, the States are free
to fashion their attainment
demonstrations and ROP plans to
include whatever mix of VOC and NOX
reductions they choose, so long as the
plans demonstrate timely attainment
and timely ROP in accordance with the
requirements of the Clean Air Act.
The following table compares a 9
percent reduction in baseline VOC
emissions by each post-1996 milestone
year to the chosen levels of NOX
substitution in the ROP plans in terms
10 Technical Support Document for Approval and
Promulgation of Air Quality Implementation Plans;
District of Columbia, Maryland, and Virginia; Post1996 Rate-of-Progress Plan, Contingency Measures,
Transportation Control Measures, 1990 Base Year
Inventory Changes, and VMT Offset SIP for the
Metropolitan Washington, DC Nonattainment Area,
January 5, 2005
11 For a summary of the photochemical grid
modeling for the Washington area refer to the
February 9, 2005 (70 FR 6796) NPR, and, for a
discussion in depth, see Technical Support
Document for Approval and Promulgation of Air
Quality Implementation Plans; District of Columbia,
Maryland, and Virginia; Attainment Demonstration
for the Metropolitan Washington, DC
Nonattainment Area, dated January 31, 2005.
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of TPD reductions and of ozone
25695
concentration decreases resulting from
these reductions.
TABLE 4.—RESULTS OF NOX SUBSTITUTION IN THE WASHINGTON AREA
Milestone year
1999
9 percent reduction in VOC baseline emissions (TPD) ..............................................................
Ozone Concentration Change to 9 percent VOC (at 0.029 ppb/ton rounded to nearest tenth)
Percent NOX reduction Substituted (percent of baseline NOX emissions) .................................
Substituted NOX Reductions (TPD) ............................................................................................
Ozone Concentration Change to Substituted NOX Reductions (0.114 ppb/ton rounded to
nearest tenth) ...........................................................................................................................
Technical and Practical Reasons for
our December 1993 NOX Substitution
Guidance. The modeling performed for
demonstration of attainment basically
establishes the relationship between
emission reductions—either of VOC,
NOX, or both—and ozone reductions.
This relationship is established for the
attainment year. As noted previously,
the modeled attainment demonstration
establishes the overall VOC and/or NOX
emission targets that are consistent with
attainment of the standard in the
attainment year. When EPA determines
that a demonstration of attainment is
approvable, i.e., it demonstrates that the
relevant area will timely attain the
NAAQS, we are making an implicit
corollary conclusion that the mix of
VOC and/or NOX control measures
included in the area’s demonstration of
attainment is sufficient for timely
attainment.
The post-1996 ROP plan requirement
is used to phase-in emission reductions
between the time of plan adoption and
the attainment date. EPA does not
require modeling of interim years for the
purpose of trying to update the NOX/
VOC/ozone relationship for a number of
reasons, including the following that are
provided in our December 1993 NOX
Substitution Guidance:
a. The strong likelihood that optimum
‘‘exchange’’ rates vary from year to year
and across a geographic area as an area’s
emissions distribution and atmospheric
chemistry change over time;
b. Uncertainty in modeling analyses,
particularly when attempting to
ascertain responses from small
percentage perturbations in emissions;
and
c. Resource limitations associated
with modeling specific control measures
during interim years before attainment
dates.
EPA continues to believe in the
validity of this guidance and in the
reasoning set forth therein as it relates
to NOX substitution under the post-1996
ROP plan requirements.
Legal Rationale for EPA’s December
1993 NOX Substitution Guidance. The
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comment focuses exclusively upon the
phrase ‘‘result in a reduction in ozone
concentrations at least equivalent to that
which would result from the amount of
VOC emission reductions
required* * * ’’ to the exclusion of
remaining language of section
182(c)(2)(C). The comment would
completely ‘‘write-out’’ of the statutory
text provisions such as ‘‘in lieu of the
demonstration required under
subparagraph (B), a demonstration to
the satisfaction of the Administrator
* * * ’’ and ‘‘in accord with such
guidance [the substitution guidance
required by section 182(c)(2)(C)] a lesser
percentage of VOCs may be accepted as
an adequate demonstration * * * ’’
(emphases added). In the plain text of
the statute Congress explicitly and
affirmatively granted EPA broad
discretion as to what sort of
demonstration is acceptable on this
technical and science-driven issue. See,
e.g., Sierra Club v. EPA, 294 F.3d at
162–163.
In addition, EPA still stands behind
its legal rationale underlying the
interpretation of ‘‘equivalency’’ that
appears in our December 1993 NOX
Substitution Guidance in section 4. In
that guidance, the basis for equivalency
is the ability of a given control strategy
(i.e., any particular mix of NOX and
VOC emission reductions) to effect
attainment of the ozone NAAQS by the
designated attainment year (December
1993 NOX Substitution Guidance, p. 2).
Further, as we previously set out, the
NOX emission reductions credited
toward ROP may be limited to the
amount of NOX reductions required in
the demonstration of attainment.
In allowing a combination of NOX and
VOC controls or the substitution of NOX
emissions reductions for VOC emissions
reductions, section 182(c)(2)(C) of the
statute states that the resulting
reductions ‘‘in ozone concentrations’’
must be ‘‘at least equivalent’’ to that
which would result from the 3 percent
VOC reductions required as a
demonstration of ROP under section
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2002
2005
39
1.1
8
62.8
37.8
1.1
9
68.1
37.1
1.1
9
66.2
7.2
7.8
7.5
182(c)(2)(B).12 The second sentence of
section 182(c)(2)(C) requires EPA to
issue guidance ‘‘concerning the
conditions under which NOX control
may be substituted for [or combined
with] VOC control.’’ In particular, the
Agency has been authorized by
Congress to address in the guidance the
appropriate amounts of VOC control
and NOX control needed, in
combination, ‘‘in order to maximize the
reduction in ozone air pollution.’’
Further, the Act explicitly provides that
the guidance may permit ROP
demonstrations that allow a lower
percentage of VOC emission reductions
as long as compensating NOX reductions
are achieved. In light of the language in
the Act evidencing Congressional intent
under this subsection to maximize the
opportunity for ozone reductions, EPA
believes that section 182(c)(2)(C) confers
on the Agency the discretion to select,
for purposes of determining ‘‘at least
equivalent’’ reductions, a percentage of
NOX emission reductions that is
reasonably calculated to achieve the
statutorily required ozone reduction and
attainment progress goals intended by
Congress. See Chevron U.S.A., Inc. v.
NRDC, 467 U.S. 837, 842–44 (1984),
Sierra Club v. EPA, 294 F.3d at 162–163.
As we have previously stated, when
we determine that a demonstration of
attainment is approvable, we are making
an implicit corollary conclusion that the
mix of VOC and/or NOX control
measures included in the area’s
demonstration of attainment is
sufficient for timely attainment.
As additional evidence that Congress
was concerned with getting more than
minimal reductions in ozone
concentrations through substitution,
EPA notes that the ROP demonstration
described in section 182(c)(2)(B) focuses
on reductions of a specified quantity of
VOC emissions per year (similarly, the
15 percent ROP reductions required for
12 Equivalent means: ‘‘equal in value, force,
amount, effect or significance,’’ or ‘‘corresponding
in effect or function; nearly equal; virtually
identical.’’ Black’s Law Dictionary, Eighth Edition,
2004. (emphasis added).
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moderate ozone nonattainment areas
focuses on reductions of that specific
quantity of VOC emissions per year). By
contrast, the alternative ROP
demonstration in section 182(c)(2)(C)
allows flexible VOC/NOX emission
reduction strategies, but only so long as
the overall quantitative reduction in
ozone concentrations is equivalent to
the amount which, for serious ozone
nonattainment areas, Congress initially
determined must be met (i.e., the ozone
concentrations achieved by VOC
reductions of 3 percent per year) in
order to ensure expeditious progress
towards attainment. In this regard the
House Committee Report states: ‘‘NOX
reductions may not be substituted for
VOC reductions in a manner that delays
attainment of the ozone standard or that
results in lesser annual reductions in
ozone concentration than provided for
in the demonstration of attainment.’’
H.R. Rep. No. 490, 101st Cong., 2d Sess.
239 (1990).
Additional support for EPA’s view
that our December 1993 NOX
Substitution Guidance’s focus on the
NOX and VOC reductions necessary for
attainment is consistent with
Congressional intent is found in section
182(g), which waives the requirement
for a milestone demonstration for a
milestone that coincides with an area’s
attainment date for an area that attains
the standard by that date.
EPA disagrees with the comment that
EPA’s ‘‘Guidance on the Post-1996 Rateof-Progress Plan and Attainment
Demonstration’’ (corrected version as of
2/18/94) specifies a different test, that
is, a modeled showing of equivalency,
than does EPA’s December 15, 1993
NOX Substitution Guidance. In section
4.1 of the ‘‘Guidance on the Post-1996
Rate-of-Progress Plan and Attainment
Demonstration,’’ EPA restated the
equivalency test set forth in sections 2
and 3 of our December 1993 NOX
Substitution Guidance.
With regard to the photochemical grid
modeling. section 4.1 of the ‘‘Guidance
on the Post-1996 Rate-of-Progress Plan
and Attainment Demonstration’’ reads:
Section 182(c)(2)(C) states that actual NOX
emission reductions which occur after 1990
can be used to meet post-1996 emission
reduction requirements, provided that such
reductions meet the criteria outlined in
EPA’s December 15, 1993 NOX Substitution
Guidance. The condition for meeting the rateof-progress requirement is that the sum of all
creditable VOC and NOX emission reductions
must equal 3 percent per year averaged over
each applicable milestone period. The
percent VOC reduction is determined from
the VOC rate-of-progress inventory and the
percent NOX reduction is determined from
the NOX rate-of-progress inventory. In
addition, the overall VOC and NOX
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reductions must be consistent with the area’s
modeled attainment demonstration. In other
words, the NOX emission reductions
creditable toward the rate-of-progress plan
cannot be greater than the cumulative
reductions dictated by the modeled
attainment demonstration.
This portion of the 1994 guidance
merely summarizes, and does not alter,
the guidance provided in our December
1993 NOX Substitution Guidance. With
regard to the photochemical grid
modeling, section 2 of our December
1993 NOX Substitution Guidance
specifies that the provision for NOX
substitution recognizes that a VOC-only
control pathway may not be the most
effective approach for effecting
attainment in all areas. Consequently,
NOX reductions are placed on a near
equal footing with VOC through
substitution. The December 1993 NOX
Substitution Guidance establishes two
conditions pursuant to both the
substitution and RFP provisions in the
Act. The first condition requires that
control strategies incorporating NOX
emission reduction measures must
demonstrate that the ozone NAAQS will
be attained within time periods
mandated by the Act. This condition
reflects the Title I provision for
photochemical grid modeling
demonstrations (section 182(c)). The
second condition, addressed in section
3 of the guidance, maintains the
requirement for periodic emission
reductions in order to realize progress
toward attainment. Flexibility is
introduced by allowing VOC and NOX
reductions rather than VOC reductions
alone. A third condition exists in which
the periodic emission reductions must
be consistent with the modeled
demonstration of attainment.
In both cases, the guidance refers to
the photochemical grid modeling that is
necessary for the modeled
demonstration of attainment and that
establishes the NOX/VOC/ozone
relationship at the attainment date.
Neither our December 1993 NOX
Substitution Guidance nor the
‘‘Guidance on the Post-1996 Rate-ofProgress Plan and Attainment
Demonstration’’ require a modeled
demonstration of equivalence for an
interim period for the reasons discussed
previously.
The 1999–2005 ROP Plans Provide for
Any Required NOX and VOC Reductions
by 2002 in a Timely Manner. Section
182(c)(2)(C) of the Act states that ‘‘[t]he
revision may contain, in lieu of the
demonstration required under
subparagraph (B), a demonstration to
the satisfaction of the Administrator that
the applicable implementation plan, as
revised, provides for reductions of VOCs
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and [NOX] (calculated according to the
creditability provisions of subsection
(b)(1)(C) and (D) of this section) * * *
that would result in reduction in ozone
concentrations equivalent to that which
would result from the amount of VOC
reductions required under subparagraph
(B).’’ The salient provisions of the
demonstration of ‘‘subparagraph B’’,
that is, section 182(c)(2)(B) of the Act,
are: (1) The requirement to reduce
baseline emissions by an average of 3
percent per year averaged over each
three-year period after 1996, and (2) the
reductions creditable towards ROP must
meet the same creditability
requirements as for the 15 percent
reduction by 1996 requirement of
section 182(b)(1)(A).
Our post-1996 guidance implements
section 182(c)(2)(B) by requiring that the
area demonstrate that milestone year
emissions with the ROP control
strategies will be less than the target
level of emissions.13 Because the target
level is determined by reducing 1990
baseline emissions and because the
future year projected inventory with all
the ROP control strategies must reflect
estimated growth in emissions
activities, this demonstration accounts
for growth between 1990 and the
milestone year. Section 182(c)(2)(B)
does not contain the phrase ‘‘accounting
for growth after 1990’’ which is found
in section 182(b)(1)(A). Nevertheless,
EPA has inferred that the 3 percent
reduction requirement of section
182(c)(2)(B) must be net of growth.
EPA’s interpretation is sound when
considering relevant provisions of the
statute as a whole because: (1) Section
182(b)(1)(A) contains a statement,
‘‘accounting for growth after 1990,’’ of
Congressional intent regarding ROP and
growth under section 182; and (2) the
last sentence of section 182(c)(2)(B)
allows creditable VOC reductions
between 1990 and 1996 that are in
excess of those needed to meet the 15
percent reduction by 1996 requirement
to count towards post-1996 ROP.
Reductions under section 182(b)(1)(A)
are excess only to the extent they are net
of growth.
EPA believes that in section
182(c)(2)(C) Congress granted EPA even
greater discretion as to the composition
of the demonstration required by section
182(c)(2)(C). As noted previously in
other portions of this response, section
182(c)(2)(C) allows a post-1996 ROP
demonstration ‘‘in lieu of’’ that required
under section 182(c)(2)(B). This
demonstration must be ‘‘to the
13 ‘‘Guidance on the Post ’96 Rate-of-Progress Plan
(RPP) and Attainment Demonstration’’ (Corrected
version of February 18, 1994).
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satisfaction of EPA,’’ and allows that a
‘‘lesser percentage of VOCs may be
accepted’’ in accordance with the
guidance that the EPA was required to
issue.
Thus, EPA was granted discretion
regarding the content of the ROP
demonstration allowable under section
182(c)(2)(C). For instance, section
182(c)(2)(C) does not use the phrase
‘‘accounting for growth after 1990.’’
However, EPA’s December 1993 NOX
Substitution Guidance is based upon the
use of the future inventories used in the
photochemical grid modeling to account
for growth in emissions related
activities, and thus reflect emissions
reductions that are net of growth.
Furthermore, section 182(c)(2)(C) does
not require that the plan providing for
reductions of VOC and NOX provide for
reductions in ‘‘baseline emissions.’’
EPA’s guidance for demonstrations of
ROP under section 182(c)(2)(C) reflects
many of the same features in our
guidance implementing section
182(c)(2)(B): A ROP plan calculates
target levels by reducing 1990 baseline
emissions by a set percentage for each
ROP period; and, EPA chose to require
that NOX substitution be net of
growth.14 EPA believes that these
features are reasonable in order to
address a scenario where the
demonstration of post-1996 ROP for an
area for one ROP milestone year, say
1999, relies a mixture of VOC and NOX
control and then relies upon all VOC
reductions for the subsequent 2002
milestone. EPA believes that the claim
that the Act requires some non-zero
percentage of reductions in VOC
baseline emissions in ROP
demonstrations pursuant to section
182(c)(2)(C) or provides, that such a
percentage reduction net of growth
requirements required by section
182(c)(2)(B) is not supported by the
plain text of the statute. The Act allows
NOX substitution with lesser VOC
reductions and doesn’t prohibit 9
percent NOX substitution and zero
percent VOC. Therefore, we believe that
we can approve a ROP plan which
provides for 9 percent NOX reductions
and no specific level of VOC reductions.
EPA’s interpretation is reasonable given
the broad discretion afforded by section
182(c)(2)(C) on these matters.
EPA’s December 1993 NOX
Substitution Guidance focuses on
progress towards reducing the levels of
NOX and VOC needed for attainment. In
that guidance, EPA caps the NOX
14 Section 1.1 of ‘‘Guidance on the Post ’96 Rateof-Progress Plan (RPP) and Attainment
Demonstration’’ (Corrected version of February 18,
1994).
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emission reductions to be consistent
with those in the modeled
demonstration of attainment.
For the reasons discussed previously
in this response, EPA believes that the
Act allows approval of a ROP Plan even
when a ROP milestone is met with out
any reduction in VOC baseline
emissions for the milestone year. The
Act allows EPA to accept a ‘‘lesser
percentage of VOC.’’ EPA believes that
‘‘lesser percentage’’ can mean,
consistent with the plain language of the
Act, any percentage less than the
average 3 percent per year prescribed by
section 182(c)(2)(B), including zero
percent. EPA previously has approved
ROP plans under section 182(c)(2) that
relied solely upon NOX reductions
without regard to VOC reductions. See
69 FR 42880, July 19, 2004 (proposed at
69 FR 25348, May 6, 2004) and 64 FR
13348, March 18, 1999 (proposed by 63
FR 45172, August 25, 1998).
As to the growth in VOC emissions
‘‘offsetting’’ the 9 percent NOX
reductions, the comment fails to realize
that a ROP plan meeting the 9 percent
reduction requirement for some
milestone year, say 1999, prior to the
attainment date, say 2005, using only
VOC reductions, would not be required
to offset any growth in NOX emissions.
EPA believes that such a ROP plan
would meet the requirements of section
182(c)(2)(B), even if the area needed
significant NOX reductions for
attainment, as long as all the reductions
were creditable and the ROP plan
otherwise met the Act and EPA’s
guidance. Nothing in section
182(c)(2)(C) requires the converse—that
the ROP plan must ensure that a 9
percent NOX reduction is not ‘‘offset’’ by
changes in VOC emissions.
It is worthwhile to note that the 1999–
2005 ROP plans in the February 2004
SIP revisions do in fact provide for a
reduction in VOC emissions. The 1999–
2005 ROP plans in the February 2004
SIP revisions project that controlled
VOC emissions by November 15, 2002
will be 372.3TPD. This is significantly
less than both the 1990 VOC ROP
Inventory of 578.7 TPD and the 1990
baseline emissions, reduced by
reductions from noncreditable measures
(the ‘‘Adjusted 1990 Base Year
Inventory for 2002’’), of 420.5 TPD. The
1999–2005 ROP plans in the February
2004 SIP revisions project that
controlled VOC emissions by November
15, 2005 will be 331.6 TPD. This is
significantly less than the 1990 baseline
emissions, reduced by reductions from
noncreditable measures (the ‘‘Adjusted
1990 Base Year Inventory for 2005’’), of
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25697
412.1 TPD.15 Therefore, the 1999–2005
ROP plans do provide for VOC
reductions by the 2002 and 2005
milestone years, and, provide for a net
reduction in VOC emissions by these
dates. However, EPA has concluded that
the States’ 1999–2005 ROP plans meet
section 182(c)(2) of the Act because the
States’ 1999–2005 ROP plans
demonstrate a 9 percent reduction in
baseline NOX emissions by 2002 and a
further 9 percent reduction in baseline
NOX emissions by 2005 and can be
approved based upon these reductions
in baseline NOX emissions.
EPA has concluded that the States’
NOX measures are sufficient to achieve
a 9 percent reduction in NOX baseline
emissions by November 15, 2002.
Because ROP is demonstrated through
the use of a 9 percent reduction in NOX
emissions by 2002, EPA believes that
there is no requirement for the plan to
have a target level of VOC emissions for
the 2002 milestone year for the reasons
discussed previously in this response.
Therefore, EPA believes that the plan
cannot be deficient for not achieving
any set reduction in VOC baseline
emissions (net of growth) by November
15, 2002—no such requirement exists.
B. Comment on the Transportation
Demand Model (TDM) Used in the Plans
Comment: We received a comment
asserting that the TDM used to project
the mobile source emissions does not
properly predict traffic volumes in the
Washington area on roadways. The
comment alleges that the inaccuracies
are significant enough that the results
cannot form a basis for predicting future
motor vehicle emissions or the emission
cuts needed to meet ROP targets, or to
show that the SIP contains sufficient
transportation control measures to offset
any growth in emissions from growth in
vehicle miles traveled or numbers of
vehicle trips in the nonattainment area.
Response: EPA disagrees with this
comment. EPA’s conformity regulation
requires that for serious, severe, and
extreme ozone nonattainment areas (if
their metropolitan planning area
contains an urbanized area population
over 200,000), the estimates of regional
transportation-related emissions, which
support conformity determinations,
must be made at a minimum using
network-based TDMs according to
15 Table IX. A–1 ‘‘Demonstration of ROP’’ and
2002 and Table V. D–3 ‘‘2005 ROP Target Levels’’
of ‘‘Technical Support Document for Approval and
Promulgation of Air Quality Implementation Plans;
District of Columbia, Maryland, and Virginia; Post1996 Rate-of-Progress Plan, Contingency Measures,
Transportation Control Measures, 1990 Base Year
Inventory Changes, and VMT Offset SIP for the
Metropolitan Washington, DC Nonattainment
Area,’’ dated January 5, 2005.
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procedures and methods that are
available and in practice, and which are
supported by current and available
documentation. 40 CFR 93.122(b). These
network-based travel models must at a
minimum satisfy the certain
requirements, including a requirement
that network-based travel models must
be validated against observed counts
(peak- and off-peak, if possible) for a
base year that is not more than 10 years
prior to the date of the conformity
determination. Model forecasts must be
analyzed for reasonableness and
compared to historical trends and other
factors, and the results must be
documented. 40 CFR 93.122(b)(1)(i); 62
FR 43793, August 15, 1997.
Even though this regulation applies to
network-based travel models used for
conformity determinations, it represents
EPA’s determination as to acceptable
practices and was issued through notice
and comment rulemaking. The
conformity regulation’s adequacy
provisions (40 CFR 93.118(e)) require
that MVEBs in control strategy SIP
revisions be the product of interagency
consultation between air quality
planning agencies and transportation
planning agencies. Therefore, EPA
believes that it is reasonable to assume
that the transportation planning
agencies will want the MVEBs to be
developed using the same network
models currently in use at the time the
MVEBs are developed. This is indeed
the case for the February 2004 SIP
revisions. The TDM model used for
development of the February 2004 SIP
revisions was based upon the execution
of the COG/TPB’s Version 2.1/TP+
travel forecasting process.16 See page B–
10 of Appendix B to the February 2004
SIP revisions.17
EPA believes that only one of the six
modeling criteria of section 93.122 of
the conformity rule is implicated by the
comment. This criterion is that
validation must be against observed
counts for base year not more than 10
years prior to conformity determination.
The comment does not allege that the
validation of the model was made
against data that was more than 10 years
old. Rather, the commenter alleges the
model results are not ‘‘reasonable.’’
EPA disagrees with this comment,
and, we specifically disagree with
certain factual allegations made therein.
For instance, on page 15 of the
16 COG is the Metropolitan Washington Council
of Governments. The TPB is the National Capital
Region Transportation Planning Board.
17 The ‘‘Version 2.1/TP+’’ model is also called
Version 2.1/TP+, Release C in ‘‘COG/TPB Travel
Forecasting Model Version 2.1/TP+, Release C
Calibration Report,’’ Metropolitan Washington
Council of Governments, December 23, 2002.
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supporting documentation to the
comment, the commenter claimed that
‘‘the [Transportation Research Board
(TRB) review] committee found that 8 of
33 facility type traffic volume classes
had percent Root Mean Square Error
(RMSE) values that were unacceptable.’’
The TRB review committee actually
stated that ‘‘for 8 of 33 facility type
traffic volume classes, RMSE values
were marginally acceptable * * *’’ 18
EPA concludes that the claim that the
review committee found the model
results unacceptable is not borne out by
the factual record.
The supporting documentation for
this comment asserted that the TDMs on
average underestimated traffic on the 20
highest volume freeway links by 26
percent, and on the 10 highest volume
arterials by 41 percent as demonstrated
by ‘‘the comparison of simulated to
observed traffic data for over 11,000
links grouped by traffic volume class
and facility type.’’ The same claim was
made to the TPB during the
development of the FY 2005–2010
Transportation Improvement Program
for the Washington Metropolitan
Region. The TPB responded by
concluding that the analysis in the
comment did not support the
conclusion. Specifically the TPB stated:
(1) That the commenter did not
understand the TPB’s data upon which
the conclusion was made; (2) that there
are many factors which lead to
differences between observed data and
model outputs; (3) that the RMSE for the
model declines with volume, i.e, there
is less error associated with higher
volumes; (4) that the ‘‘20 highest
freeway links’actually represent only
five roadway segments in the region
because freeway links are directionally
coded and these links are split between
interchanges resulting in four links per
these five highway segment; (5) that the
comment focuses only on a few values
at the high-end of the volumes ranges,
but draws the mistaken conclusion that
the model underestimates volumes for
the regional highway network links with
the highest ‘‘observed’’ volumes; (6) that
the ‘‘observed date’’ for the 11,000 link
segments of the regional highway
network, do not represent actual traffic
counts but rather represent factored
estimates of average daily traffic
volumes based on continuous traffic
counts taken at a very limited number
of permanent counting stations, and; (7)
18 Letter from David J. Forkenbrock, Chair,
Transportation Research Board’s Committee for
Review of Travel Demand Modeling by the
Metropolitan Washington Council of Governments
to Peter Shapiro, Chairman, National Capital region
Transportation Planning Board, dated, September 3,
2003.
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that ‘‘observed’’ volumes on the ‘‘20
highest freeway links’’ are either
factored estimates of average daily or
are ‘‘uncounted manual’’ estimates.19
EPA notes that the supporting
documentation cited by the comment is
for the COG/TPB Travel Forecasting
Model, Version 2.1D Draft #50. The
TDM model actually used for
development of the February 2004 SIP
revisions actually was the COG/TPB’s
Version 2.1/TP+ travel forecasting
process. See Appendix B to the
February 2004 SIP revisions, p. B–10.
Version 2.1/TP+ model was validated
using year 2000 data. See ‘‘COG/TPB
Travel Forecasting Model Version 2.1/
TP+, Release C Calibration Report,’’
Metropolitan Washington Council of
Governments, December 23, 2002, p. 9–
1. The conclusion in the validation
report was that VMT is shown to be
overestimated by about 8 percent,
screenlines estimates are high by 17
percent overall, and the RMSE is about
51 percent, but the model performs well
in other capacities (transit estimation,
restrained speeds, trip distribution
pattern. COG/TPB’s Version 2.1 travel
forecasting process represented the
continuation of a multi-year models
development plan that was formulated
in FY–93 in response to the Federal
Clean Air Act Amendments of 1990 and
the Intermodal Surface Transportation
Efficiency Act (ISTEA) of 1991. Id., p.
1–1. For instance, the validation report
states that the ratio of estimated to
observed transit trips was 0.95 which
means that overall the TDM predictions
were only 5 percent less than the
observed values. For transit trips, the
ratio was 0.93 or 7 percent less. The
overall ratio of estimated to observed
VMT for the entire model domain was
1.08 which is equivalent to the TDM
over-predicting VMT by 8 percent. For
the Washington area, the TDM over
predicted VMT by 9 percent overall.
Overall, the Version 2.1/TP+ TDM
model used for the February 2004 SIP
revisions over predicted VMT by facility
type by 13 percent. See ‘‘COG/TPB
Travel Forecasting Model Version 2.1/
TP+, Release C Calibration Report,’’
Metropolitan Washington Council of
Governments, December 23, 2002, Ex.
9–1 through 9–12.
While the Version 2.1/TP+ TDM
model under-predicts VMT on some
highway segments it over predicts on
most others. EPA believes that the claim
made in the comment that the TDM
19 ‘‘FY 2005–2010 Transportation Improvement
Program for the Washington Metropolitan Region
National Capital Region,’’ Transportation Planning
Board and the Metropolitan Washington Council of
Governments, dated November 17, 2004, pp. 260 to
262.
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systematically underestimates traffic
and therefore that the SIP revisions
‘‘necessarily understate emission
reductions needed’’ to achieve required
rates of progress, attainment or the VMT
offset requirements is not supported by
the facts. In actuality, the model
generally overestimated VMT, as we
have noted.
In a letter to the TPB, the TRB noted
that in the four decades of experience
with the use of travel demand models in
transportation planning there are few
universally accepted guidelines or
standards of practice for these models
and their application, and any
assessment of these models, their
performance, and the current state of
transportation demand modeling
practices relies primarily upon
professional experience and
judgement.20 Given that TDMs are
constantly undergoing refinement, and
that models can always be improved,
EPA believes we need not hold up the
approval process until a hypothetical
‘‘best model’’ is eventually, if ever,
developed. For these reasons, EPA
disagrees with the comment. We
conclude that the TDM model used in
the SIP revisions is acceptable and that
the SIP revisions can be approved.
C. Comment on the VMT Offset SIP
Comment: We received a comment
asserting that the SIP revisions are
deficient because they do not contain
sufficient TCMs to offset growth in
emissions from growth in VMT or in
trip numbers. The comment alleges that
the Act requires the SIP to offset any
growth in emissions due to growth in
VMT or in trip numbers be offset rather
than a showing that overall motor
vehicle emissions are expected to
decline. The comment implies that the
VMT offset provisions apply to both
VOC and NOX emissions.
Response: The VMT Offset Provision
Applies Only to VOC Increases. As an
initial matter EPA believes that the VMT
offset provision applies only to
increases of VOC emissions. As
explicitly stated in the proposed
rulemaking for the General Preamble for
the Implementation of Title I of the
Clean Air Act Amendments of 1990, 57
FR 13498 at 13521, Apr. 16, 1992, EPA
has consistently interpreted the VMT
offset requirements of the Act, set forth
in section 182, to apply only to VOC
emissions. See, e.g., 60 FR 38718 at
38721, July 28, 1995; 60 FR 48896 at
48898–48899, September 21, 1995. As
20 Letter from David J. Forkenbrock, to
Christopher Zimmerman, Chairman, National
Capital Region Transportation Planning Board,
dated, May 10, 2004.
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19:27 May 12, 2005
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we explain, EPA disagrees with the
commenter’s assertion that the VMT
offset SIP revisions are deficient because
these revisions do not address growth in
NOX emissions.
Section 182(d)(1)(A) of the Act
provides that ‘‘any growth in emissions’’
from growth in VMT must be offset.
EPA believes that in the plain language
of the Act Congress intended that this
offset requirement be limited to VOC
emissions. First, section 182(d)(1)(A)’s
requirement that a State’s adopted
TCMs comply with the ‘‘periodic
emissions reduction requirements’’ of
subsections 182(b) and (c) the Act,
indicates that the VMT offset SIP
requirement is VOC-specific, and NOX
emissions are not required to be offset.
Section 182(c)(2)(B), which requires
reasonable further progress
demonstrations for serious ozone
nonattainment areas, provides that such
demonstrations will result in VOC
emissions reductions; thus, the only
‘‘periodic emissions reduction
requirement’’ of section 182(c)(2)(B) is
VOC-specific. In fact, it is only in
section 182(c)(2)(C)—a provision not
referenced in section 182(d)(1)(A)—that
Congress provided States the authority
to submit demonstrations providing for
reductions of VOC and NOX emissions
in lieu of the SIP otherwise required by
section 182(c)(2)(B).
Moreover, the 15 percent periodic
reduction requirement of section
182(b)(1)(A)(i) applies only to VOC
emissions, while only the separate
‘‘annual’’ reduction requirement applies
to both VOC and NOX emissions. We
believe that Congress did not intend the
terms ‘‘periodic emissions reductions’’
and ‘‘annual emissions reductions’’ to
be synonymous, and that the former
does not include the latter. In section
176(c)(3)(A)(iii) of the Act, Congress
required that conformity SIPs
‘‘contribute to annual emissions
reductions’’ consistent with section
182(b)(1) (and thus achieve NOX
emissions reductions), but did not cross
reference the 15 percent periodic
reduction requirement. Conversely,
section 182(d)(1)(A) refers to the
periodic emissions reduction
requirements of the Act, but does not
refer to annual emissions reduction
requirements that require NOX
reductions. Consequently, we interpret
the requirement that VMT Offset SIPs
comply with periodic emissions
reduction requirements of the Act to
mean that only VOC emissions are
subject to section 182(d)(1)(A) in severe
ozone nonattainment areas.
Finally, we note that where Congress
intended section 182 ozone SIP
requirements to apply to NOX as well as
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25699
VOC emissions, it specifically extended
applicability to NOX. Thus, references to
ozone or emissions in general in section
182 do not on their own implicate NOX.
For example, in section 182(a)(2)(C), the
Act requires States to issue
preconstruction permits for new or
modified stationary sources ‘‘with
respect to ozone.’’ Congress clearly did
not believe this reference to ozone alone
was sufficient to subject NOX emissions
to the permitting requirement, since it
was necessary to enact section 182(f)(1)
of the Act, which specifically extends
the permitting requirement to major
stationary sources of NOX. Since section
182(d)(1)(A) does not specifically
identify NOX emissions requirements in
addition to the VOC emissions
requirements identified in the
provision, EPA does not believe States
are required to offset NOX emissions
from VMT growth in their section
182(d)(1)(A) SIPs.
The VMT Offset Provision in Section
182 Does Not Apply as Claimed in
Comments. EPA has consistently
explained that the purpose of the VMT
offset requirement is to maintain motor
vehicle VOC emissions beneath a
‘‘ceiling level’’ established through
modeling of mandated transportationrelated controls, so that VOC emission
reductions resulting from such measures
are not cancelled out by growth in
motor vehicle emissions. See, e.g., 57 FR
13498 at 13521–13523, April 16, 1992;
61 FR 51214, October 1, 1996; 61 FR
53624, October 15, 1996; and 66 FR
57247 at 57247–57248, November 14,
2001.
The VMT offset provision of section
182(d)(1) of the Act requires that states
submit by November 15, 1992 specific
enforceable TCMs and transportation
control strategies to offset any growth in
emissions from growth in VMT or
number of vehicle trips and to attain
reductions in motor vehicle emissions
sufficient, in combination with other
measures, to allow total emissions in the
sever nonattainment area to comply
with the ROP and attainment
requirements of the Act.
As discussed in the General Preamble,
EPA believes that section 182(d)(1)(A) of
the Act requires the State to ‘‘offset any
growth in emissions’’ from growth in
VMT, but not, as the comment suggests,
all emissions resulting from VMT
growth. See 57 FR at 13522–13523. As
we explained in response to similar
comments objecting to our application
of the General Preamble’s approach
when approving other SIPs, the purpose
is to prevent a growth in motor vehicle
emissions from canceling out the
emission reduction benefits of the
federally mandated programs in the Act.
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See 60 FR at 48898; 60 FR at 38720–
38721. The baseline for emissions is the
1990 level of vehicle emissions and the
subsequent reductions in emission
levels required to reach attainment with
the NAAQS for ozone. Thus, the
anticipated benefits from the mandated
measures such as the Federal motor
vehicle pollution control program,
lower Reid vapor pressure, enhanced
inspection and maintenance and all
other motor vehicle emission control
programs are included in the ceiling
line calculations used by the States in
the VMT Offset SIP. Chapter 10 of the
February 2004 SIP revisions, shows how
emissions will decline substantially and
will not begin to rise over the ceiling
established by the mandated controls.
Emission reductions are expected every
year through the year 2005.
Our approach is consistent with the
purposes Congress had in enacting
section 182(d)(1)(A). The ceiling line
level decreases from year to year as the
state implements various control
measures, and the decreasing ceiling
line prevents an upturn in mobile
source emissions. Dramatic increases in
VMT that could wipe out the benefits of
motor vehicle emission reduction
measures will not be allowed and will
trigger the required implementation of
TCMs. This prevents mere preservation
of the status quo, and ensures emissions
reductions despite an increase in VMT
or number of vehicle trips. To prevent
future growth changes from adversely
impacting emissions from motor
vehicles, states are required under
section 182(c)(5) of the Act to track
actual VMT and to periodically
demonstrate that the actual VMT is
equal to or less than the projected VMT,
with TCMs required to offset VMT that
is above the projected levels. Under the
commenter’s approach to section
182(d)(1)(A), the States would have to
offset VMT growth even while vehicle
emissions are declining. Although the
statutory language could arguably be
read to require offsetting any VMT
growth, EPA believes that the language
can also be reasonably and
appropriately read so that only actual
emissions increases resulting from VMT
growth need to be offset. The statute by
its own terms requires offsetting of ‘‘any
growth in emissions from growth in
[VMT].’’ 42 U.S.C. 7511a(d)(1). EPA has
reasonably and consistently interpreted
the VMT offset provision of the Act to
require that states adopt, and submit to
EPA for approval into their SIPs, TCMs
or transportation control strategies
sufficient to at least offset ‘‘growth in
[VMT] or numbers of vehicle trips,’’ but
only if the VMT growth would result in
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actual emissions increases from mobile
sources. Our consistent historic
interpretation of the language of section
182(d)(1)(A) is entitled to deference.
Chevron U.S.A., Inc. v. NRDC, 467 U.S.
837, 842–44 (1984). See also U.S. v.
Mead, 533 U.S. 218, 227–35 (2001).
Given the susceptibility of the
statutory language to these two
alternative interpretations, EPA believes
it is the Agency’s role in administering
the statute to take the interpretation
most reasonable in light of the practical
implications of such interpretation, and
the purposes and intent of the statutory
scheme as a whole. In the context of the
intricate planning requirements
Congress established in title I to bring
areas towards attainment of the ozone
standard, and in light of the absence of
any discussion of this aspect of the VMT
Offset provision by the Congress as a
whole (either in floor debate or in the
Conference Report), EPA has
consistently concluded that the
appropriate interpretation of section
182(d)(1)(A) requires offsetting VMT
growth only when such growth would
result in actual emissions increases.21
When growth in VMT and vehicle
trips would otherwise cause an upturn
in emissions from motor vehicles, this
upturn must be prevented. The
emissions level at the point of upturn
becomes a ceiling on motor vehicle
emissions. This requirement applies to
projected emissions in the years
between the submission of the SIP
revision and the attainment
demonstrations. The ceiling level is
defined, therefore, up to the point of
upturn, as motor vehicle emissions that
would occur in the ozone season of that
year, with VMT growth, if all measures
for that area in that year were
implemented by the Act. When this
curve begins to turn up due to growth
in VMT or vehicle trips, the ceiling
becomes a fixed value. The ceiling line
would include the effects of federal
measures such as new motor vehicle
standards, phase II Reid vapor pressure
(RVP) controls, and reformulated
gasoline, as well as the statutorilymandated SIP requirements. For the
reasons outlined in the February 9, 2005
NPR (70 FR 2085), EPA believes that the
February 2004 SIP revisions fulfill the
first element.
21 As noted previously, EPA has applied this
interpretation since the enactment of the 1990
amendments to the Clean Air Act adding section
182(d)(1)(A), and in response to adverse comments
submitted on other rulemaking actions. See, e.g., 60
FR 48898 (final approval of Illinois’ SIP) and 60 FR
39720–39721 (final approval of Indiana’s SIP); 66
FR 57247 at 57247–57248, November 14, 2001 (final
approval of Texas SIP).
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Under EPA’s approach, the second
element, which requires the VMT offset
SIP to comply with the 15 percent ROP
requirement of the Act, was due on
November 15, 1993 for areas initially
classified as severe nonattainment.
November 15, 1993 is the same date on
which the 15 percent ROP SIP itself was
due under section 182(b)(1) of the Act.
For areas initially classified as severe
nonattainment, EPA believes it was
reasonable to extend the deadline for
this VMT offset element from November
15, 1992 to the date on which the entire
15 percent SIP was due, as this allows
states to develop the comprehensive
strategy to address the 15 percent
requirement and assure that the TCMs
elements required under section
182(d)(1)(A) are consistent with the
remainder of the 15 percent
demonstration. Indeed, EPA believes
that only upon submittal of the broader
15 percent plan can a state have had the
necessary opportunity to coordinate its
VMT strategy with its 15 percent plan.
In the case of the Washington area, the
second element has been fulfilled
because the 15 percent ROP plans were
approved long before the area was
reclassified to severe nonattainment.
See 64 FR 42629, August 5, 1999; 65 FR
44686, July 19, 2000; and, 65 FR 59727,
October 6, 2000.
The third element, which requires the
VMT offset SIP to comply with the post1996 ROP and attainment requirements
of the Act, was due on November 15,
1994, the statutory deadline for those
broader submissions. For areas initially
classified as severe nonattainment, EPA
believes it is reasonable to similarly
extend the deadline for this VMT
element to the date on which the post1996 ROP and attainment SIPs are due
for the same reason it is reasonable to
extend the deadline for the second
element.22 First, it is arguably
impossible for a state to make the
showing required by section
182(d)(1)(A) for the third element until
the broader demonstrations have been
developed by the State. Moreover,
allowing states to develop the
comprehensive strategy to address post1996 ROP plans and attainment by
providing a fuller opportunity to assure
that the TCMs elements comply with
the broader ROP plans and attainment
demonstrations, will result in a better
program for reducing emissions in the
long term. In the case of the Washington
area, EPA believes the third element has
22 In the case of the Washington area, the post1999 portions of the post-1996 ROP plan required
under section 182(c)(2) were in fact due on the
same as the VMT offset SIP. See 68 FR 3410,
January 24, 2003.
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been fulfilled for the reasons outlined in
the February 9, 2005 NPR (70 FR 2085)
and this document because EPA is
approving the 1996–1999 and 1999–
2005 ROP plans and the modeled
demonstration of attainment. EPA thus
finds that the SIPs contain all measures
necessary to provide for timely
attainment and ROP, and therefore that
no additional TCMs will be necessary to
meet those requirements.
D. Comment on the Contingency
Measures Plans
Comment 1: We received a comment
asserting that EPA cannot approve the
contingency measures which were
identified in the SIP revisions to address
the Washington area’s the failure to
attain by November 15, 1999. The
comment claims that, because these
measures in the plan required further
action by the States, these contingency
measures do not meet the CAA’s
requirement that the measures take
effect without further action by the State
or EPA after the failure to attain. The
comment also claims the contingency
measures do not meet EPA’s own
guidance which requires contingency
measures to achieve reductions no later
than the year after the one in which the
failure is identified because these
contingency measures identified by the
SIP revision were not implemented
until 5 to 6 years after the failure to
attain.
Response 1: EPA disagrees with the
comment that the contingency plan for
the failure of the Washington serious
ozone nonattainment area to attain by
November 15, 1999 cannot be approved.
The comment does not address the
factual situation for the Washington area
where the SIP did not contain a
contingency measures plan consisting of
fully adopted measures until the
submission of the February 2004 SIP
revisions and submission of the various
adopted rules identified as the
contingency measures that is the
contingency measures implemented in
response to the failure of the
Washington area to attain the 1-hour
ozone NAAQS by November 15, 1999.
Prior to our January 12, 2004 NPR (70
FR 2085), EPA had recognized that the
SIP of each of the Washington area
States did not contain contingency
measures to address the failure to attain
(FTA) the ozone NAAQS by November
15, 1999 (the ‘‘contingency measures for
1999 FTA’’). In the January 12, 2004
NPR (70 FR at 2087), we provided a
brief history of the severe area SIP
revisions by noting that EPA had
previously conditionally approved the
post-1996 ROP plans and those versions
of the attainment plans submitted
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during 1998 and 2000, contingent upon
the States fulfilling commitments they
made to submit the additional elements
required of SIPs for a severe area within
one year. One of the conditions for
approval in the April 17, 2003 final
conditional approval (68 FR 19106) was
that the States had to revise the
Washington area severe attainment plan
to include a contingency plan
containing those adopted measures that
qualify as contingency measures to be
implemented for the failure of the
Washington area to attain the one-hour
ozone standard for serious areas by
November 15, 1999; that is, the States
had to submit SIP revisions to add the
contingency measures for 1999 FTA. 68
FR at 19106. In the NPR for the April
17, 2003 final conditional approval,
EPA noted that the States in the
Washington area had committed to
submit to the EPA those measures that
qualify as contingency measures due to
the failure of the Washington area to
attain the ozone standard for serious
areas by November 15, 1999. 68 FR at
5248, February 3, 2003. In the February
3, 2003 NPR, EPA also recounted that
our January 3, 2001 approval (66 FR
586) of the post-1996 ROP plans and
those versions of the attainment plans
submitted during 1998 and 2000 had
been vacated by the Court of Appeals.
The Court of Appeals determined that
EPA lacked the authority to approve
attainment plan and ROP SIPs without
contingency measures. Sierra Club v.
Whitman, 294 F.3d at 164. EPA had
noted that the post-1996 ROP plans and
those versions of the attainment plans
submitted during 1998 and 2000
covered by the January 3, 2001 final rule
‘‘[did] not specify any specific measures
as contingency measures.’’ 66 FR at
615–616, January 3, 2001. EPA also
agreed with comment that the lawn/
garden measure identified in the
contingency plan as a contingency
measure was insufficient. Therefore,
EPA believes that prior to submittal of
the February 2004 SIP revisions and the
SIP revisions containing the adopted
rules for the contingency measures the
Washington area States had not
submitted the necessary SIP revisions
for the contingency measures for 1999
FTA.
EPA has interpreted the requirement
that contingency measures must ‘‘take
effect without further action by the State
or the Administrator’’ to mean that no
further rulemaking activities, such as
public hearings or legislative review, by
the State or the EPA should be needed
to implement the contingency measures.
See 57 FR at 13512, April 16, 1992;
section 9.0 of ‘‘Guidance for Growth
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25701
Factors, Projections, and Control
Strategies for the 15 Percent Rate-ofProgress Plans,’’ (EPA–452/R–93–002,
March 1993). EPA has required that
contingency measures must be fully
adopted rules or measures but do not
have to be implemented unless and
until they are triggered by a failure to
either meet a milestone or attain the
NAAQS. See section 5.6 of ‘‘Guidance
on the Post ’96 Rate-of-Progress Plan
(RPP) and Attainment Demonstration’’
(Corrected version of February 18,
1994).
The States did not have adopted
contingency measures to implement
without further action by the States on
the effective date of EPA’s
determination that the Washington area
failed to attain by 1999. If EPA were to
now disapprove the contingency
measures plan because the States
needed to take further action after the
1999 FTA in order to implement the
contingency measures to address the
1999 FTA, the States would have to
adopt and submit SIP revisions
consisting of a revised contingency
measures plan and adopted control
measures, and, EPA would have to
approve those SIP revisions in order to
prevent or lift sanctions required by
section 179 of the Act. This would be
an impossibility since the relevant 1999
date has long since passed. In short, the
States and EPA would have to
undertake rulemaking actions on those
remedial SIP revisions, and those
rulemakings would suffer the same fate
that the commenter’s claim make the
measures we approve today supposedly
defective—we would have to
disapprove them because they were not
implementable prior to the States’
failure to attain in 1999. The commenter
would have EPA produce an endlessly
looping, absurd result, namely, the
States would be left in a position where
no SIP revision would be able to lift
sanctions because the States cannot go
back in time to adopt measures that
were not adopted by a deadline in the
past. The fact that the States failed to
adopt and submit these measures in a
timely fashion should not preclude EPA
from approving them now that they
have been adopted, implemented, and
submitted.
EPA further disagrees with the
comment that the contingency measures
needed to address the contingency
measures for 1999 FTA are inadequate
because these measures do not meet
EPA’s guidance which requires
contingency measures to achieve
reductions no later than the year after
the one in which the failure is
identified. Once again, the commenter
would have EPA produce an absurd
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result. Because the States cannot go
back in time to implement measures
that were not implemented by a
deadline in the past, if EPA were to
disapprove the contingency measures
for 1999 FTA for the reason advanced in
the comment, the States again would be
left in the situation where no SIP
revisions or measures could be
approved to halt or lift sanctions. Any
further SIP revisions to address the
contingency measures for 1999 FTA
would suffer the same defect of
timeliness. Given this impossibility EPA
believes that it is appropriate and
beneficial to the environment to
belatedly get the reductions
contemplated by the 1999 FTA
contingency measures.
EPA agrees that our guidance and
policy requires contingency measures,
once triggered, to achieve reductions no
later than the year after the one in
which the failure is identified. However,
this guidance applies to contingency
measures that meet the requirement that
the measures can be ‘‘implemented
without further action’’ by the state or
EPA. EPA expects that certain actions,
such as notification of sources,
modification of permits, etc., would
probably be needed before a measure
could be implemented effectively
needed to affect full implementation of
the contingency measures and expect
such actions to occur within 60 days
after EPA notifies the State of its failure.
See 57 FR at 13512, April 16, 1992. EPA
considers that in the case of a failure to
attain, the State is notified of a failure
to attain only once EPA has published
the notice in the Federal Register
pursuant to section 181(b)(2)(B) that
EPA has determined that the area has
failed to attain by the statutory
attainment date, and that such
notification is effective on the effective
date of the Federal Register publication.
Under section 181, such a notification
can be published no later than May 15th
of the year following the attainment date
and still be timely under the Act. For a
November 15, 1999 attainment date, the
one-year period for implementation of
the contingency measures for 1999 FTA
could well have started May 15, 2000.
For the Washington area, EPA’s
determination that the area had failed to
attain by the serious attainment date of
November 15, 1999 was in fact effective
March 24, 2003. 68 FR 3410, January 24,
2003. In the case of the Washington
area, the States adopted and
implemented by January 1, 2005 all the
measures identified in the plan as
addressing the contingency measures for
1999 FTA. See Table X. B–1 Summary
of Benefits from Measures 7.4.11, 7.4.12
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and 7.4.14 of the January 5, 2005 TSD.23
Arguably, the one-year period after the
States were notified of the failure to
attain ended March 24, 2004, but as
discussed previously, the States needed
to first adopt the measures that would
be used as the contingency measures for
1999 FTA before the measures could be
implemented. The comment offers no
suggestion on how the States might
retroactively obtain emission reductions
in 2004 (or for that matter 2000) for
measures that the States did not adopt
and implement until after that time.
As pointed out by the Court of
Appeals in Sierra Club v. EPA, 356 F.3d
296, with respect to the reclassification
of the area to severe nonattainment
status due to the its failure to attain the
1-hour ozone NAAQS by November 15,
1999, this commenter ‘‘challenged
EPA’s decision to extend the States’
final deadline for submitting revised
SIPs complying with the Act’s
requirements for severe areas, including
post-1999 ROP plans, to March 1,
2004.’’ 356 F.3d at 308–09.
The Court of Appeals acknowledged
that ‘‘the deadline for filing severe area
SIP components including post-1999
ROP plans had already passed long
before reclassification took place.
Indeed, the statutory deadline for such
submittals was November 15, 1994.’’ Id.
at 309. Citing to a prior decision, Sierra
Club v. Whitman, 285 F.3d 63 (D.C. Cir.
2002), the Court reiterated that ‘‘ ‘The
relevant provisions of the Clean Air Act
* * * contain no language suggesting
that Congress intended to give EPA the
unusual ability to implement rules
retroactively,’ ’’ in upholding EPA’s
reliance on the discretion conferred by
section 182(i) of the CAA to adjust
applicable statutory deadlines, other
than attainment dates, when it
reclassifies an attainment area.
Similarly, EPA believes that it would
be arbitrary and capricious to impose a
retroactive obligation on the States that
can never be fulfilled, resulting in
sanctions that could never be lifted. It
would be especially egregious for EPA
to put the States in that position since
the States’ failure to submit contingency
measures or to even realize that the
November 15, 1999 attainment date
pertained to the Washington area was
due to their reliance on published EPA
guidance.24 The failure to begin
23 ‘‘Technical Support Document for Approval
and Promulgation of Air Quality Implementation
Plans; District of Columbia, Maryland, and Virginia;
Post-196 Rate-of-Progress Plan, Contingency
Measures, Transportation Control Measures, 1990
Base Year Inventory Changes, and VMT Offset SIP
for the Metropolitan Washington, DC
Nonattainment Area,’’ dated January 5, 2005.
24 See, Memorandum dated July 16, 1998, from
Richard Wilson, Acting Assistant Administrator for
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implementation of contingency
measures in 2000, upon a March 24,
2003 EPA finding that the area failed to
attain in November 1999, cannot be
cured by a state rulemaking that
occurred before March 24, 2003; there
was no such rulemaking then, it does
not exist now, and it never can be. After
March 24, 2003, the States could
complete their respective state
rulemaking processes to develop the
missing contingency measures. They
have done so, and all those measures
have been implemented.
In this action EPA is acting on SIP
revisions that, with respect to the
contingency measures for 1999 FTA,
identify additional measures that the
States have implemented subsequent to
November 15, 1999 attainment date for
serious areas. EPA concludes that in the
circumstances of this case it is
appropriate and consistent with the
statute to approve these contingency
measures that have now been
implemented.
Comment 2: We received a comment
asserting that the contingency plan for
2005 cannot rely on measures already
adopted and in place or to be in place
before the 2005 attainment and ROP
deadline. The comment claims that the
Act requires that contingency measures
must be additional measures that will be
triggered by the attainment or milestone
failure, that is, the Act provision is
prospective, not retrospective. In
support of their argument, the comment
cites language, ‘‘to be undertaken in the
event the area fails,’’ from the legislative
history for the 1990 amendments to the
Act.
Response 2: EPA believes that its
interpretation of the contingency
measure provisions of the Act
applicable to severe nonattainment
areas is a reasonable interpretation of
the Act because reductions from these
contingency measures are continuing in
nature. Sections 172(c)(9) and 182(c)(9)
of the Act direct that a state’s revised
SIP shall include ‘‘specific measures to
be undertaken’’ if an ROP or attainment
milestone is missed, and that the
contingency measures are ‘‘to take effect
in any such case without further action
by the State or the Administrator.’’ 42
U.S.C. 7502(c)(9), 7511a(c)(9) (emphasis
added).
EPA has consistently stated that any
rule or measure that meets the
creditability requirements of section
182(b)(1)(C) and (D), that would achieve
real, permanent, enforceable reductions,
and that is not already required as a part
of the relevant ROP or attainment
Air and Radiation, ‘‘Extension of Attainment Dates
for Downwind Areas.’’
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demonstration SIP, can be adopted as a
contingency measure. See ‘‘Guidance on
the Post-1996 Rate-of-Progress Plan and
Attainment Demonstration’’ (corrected
version as of 2/18/94), section 5.6.
Congress, in the Act, did not define
the terms ‘‘to take effect’’ and ‘‘to be
undertaken.’’ The terms ‘‘to take effect’’
and ‘‘to be undertaken’’ could imply a
purely prospective action that excludes
the possibility of contingency measure
implementation prior to an area’s failure
to meet an ROP milestone or attainment
date. If we were to read the CAA this
way, the only acceptable contingency
measure would be those that are
adopted but not implemented. Under
that reading, the states could adopt the
contingency measures but hold their
implementation in reserve to meet the
contingency measure requirement. If we
read the Act to allow adopted and
implemented measures that continue to
result in emissions reductions in years
subsequent to their implementation to
serve as contingency measures,
provided that those measures’ emission
reductions are not needed to
demonstrate expeditious attainment
and/or ROP, the states could implement
the contingency measures early and
would achieve the environmental
benefits prior to the triggering of the
contingency requirement. Nothing in
the language of sections 172(c)(1),
172(c)(9) or 182(c)(9) prohibits this
interpretation. Implemented
contingency measures achieve
continuing emissions reductions. We
reasonably interpret the term ‘‘to take
effect’’ and ‘‘to be undertaken,’’ as used
in sections 172(c)(9) and 182(c)(9) of the
Act, to allow as contingency measures,
measures implemented prior to the
failure to achieve an ROP or attainment
milestone, that will continue to achieve
emissions reductions after the plan fails,
so long as those measures are not
needed to demonstrate expeditious
attainment and/or ROP. As noted
previously, this interpretation is a
longstanding exercise of EPA’s authority
to construe a statutory scheme it is
entrusted to administer, by filling the
gap left by Congress’s failure to define
the terms ‘‘to take effect’’ and ‘‘to be
undertaken.’’ See generally, U.S. v.
Mead Corp., 553 U.S. at 227–35;
Chevron U.S.A, Inc. v. NRDC, 467 U.S.
837, 842–45 (1984).25
EPA believes that allowing early
reductions to be used as contingency
measures comports with a primary
purpose of the Act—the aim of ensuring
25 The commenter’s appeal to the legislative
history does not add to its argument, since the
quoted language reiterates, but does not elaborate,
explain or expound upon, the statutory text.
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that nonattainment areas reach NAAQS
compliance in an efficient manner and
achieving additional emissions
reductions that will improve air quality.
The contingency plan allows the
Washington area to include sufficient
contingency measures to ensure that
‘‘upon implementation of such
measures, additional emissions
reductions of up to 3 percent of the
emissions in the adjusted base year
inventory (or such lesser percentage that
will cure the identified failure) would
be achieved in the year following the
year in which the failure has been
identified.’’ See 57 FR at 13511, April
16, 1992.
The emissions reductions from the
measures in the Washington area
contingency plan are not available for
any other use so long as the measures
remain in the SIP as contingency
measures. A failure to attain or failure
to demonstrate ROP will result in these
emissions reductions being applied
toward attainment or ROP (depending
on which milestone is not being met).
Even though these measures are already
implemented, the continuing reduction
credits are, in effect, set aside to be
applied in the event that attainment or
ROP is not achieved. These credits are
immediately available, without further
action by the States. We note that
measures that have already been
implemented clearly meet CAA section
172(c)(9) requirement that contingency
measures take effect without further
action by the State or Administrator.
EPA believes that it would be illogical
and counterproductive to penalize
nonattainment areas that are taking
extra step of implementing contingency
measures prior to a failure to achieve a
ROP or attainment milestone, to further
insure that the area will comply with
the CAA’s mandate that states attain the
NAAQS as ‘‘expeditiously as
practicable.’’ 42 U.S.C. 7502(c)(1). As
we have noted previously, ‘‘There are a
number of benefits to allowing and even
encouraging the early implementation of
contingency measures. The chief benefit
is that their emission reductions and
thus their public health benefit are
realized early. Another is that it allows
states to build uncredited cushions into
their attainment and RFP
demonstrations, a cushion which makes
actual failures to make progress or attain
less likely.’’ 67 FR 48718, 48731, July
25, 2002.
The standard advocated by the
comment would allow EPA to approve
the contingency measure plan only if
the measures were scheduled for
implementation in the event of a future
failure to make a ROP target or attain the
NAAQS. EPA believes that the States
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25703
could correct a disapproval issued
pursuant the standard advocated by the
comment by amending the contingency
measure rules themselves to replace the
current requirement for compliance by a
date certain with a requirement to
comply by some date(s) in future to be
determined only upon a ROP or
attainment failure. Such a revision
would not interfere with ROP or
attainment because EPA believes that
the reductions from the measures in the
contingency plan to address a ROP
failure or a failure to attain by
November 15, 2005 must go beyond the
emissions reductions needed to
demonstrate ROP and timely attainment
(i.e., they are ‘‘surplus’’). Although this
result might arguably comply with the
statute as the commenter suggests, it
would actually be detrimental for air
quality as the measures would not be
producing emissions reductions
currently as under the submitted SIP.
The comment alleges that if an area
fails to meet a progress or attainment
deadline, the measures already in effect
are insufficient, thus warranting the
implementation of additional controls
which the comment claims should be
the contingency measures. Yet, the
comment fails to recognize that if the
area fails to attain on time, such failure
would have been worse in the absence
of the contingency measures. Likewise,
if an area has an ROP shortfall, such
shortfall would have been larger in the
absence of the contingency measures.
EPA has approved many contingency
measure plans relying upon early
implementation of contingency
measures. See, e.g., 67 FR 60590,
September 26, 2002. EPA’s
interpretation that early implemented
contingency measures meet the
requirements of the Act was upheld in
Louisiana Environmental Action
Network v. EPA, 382 F.3d 575 (5th Cir.
2004), though the court found that the
particular measure at issue did not
qualify as a contingency measure for
other reasons.
Comment 3: We received a comment
that the Act requires a set of
contingency measures to address any
failure to meet ROP requirements for the
2002–2005 period, that is separate from
those required for failure to attain. The
comment claims that the requirement
for contingency measures to address
post-1996 milestone failures is
explicitly set out in the Act as an
additional mandate in addition to the
requirement for contingency measures
to address attainment failures. The
comment further claims that the 2005
ROP deadline here could precede the
attainment date if, in the case of an area
which qualifies for one or both of the 1-
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year attainment date extensions allowed
by the Act.
Response 3: EPA disagrees that
section 182(c)(9) of the Act necessarily
adds anything substantive to the
requirement of section 172(c)(9) other
than a requirement that the contingency
plan be able to address a milestone
failure pursuant to section 182(g). EPA
first notes that neither section 182(c)(9)
nor 172(c)(9) of the Act specify how
many contingency measures are needed
or the magnitude of emissions
reductions that must be provided by
these measures. The Act is totally silent
on this issue. EPA rejected the
interpretation that the Act requires
states to adopt sufficient contingency
measures to make up for a shortfall
resulting from the failure where none of
the state measures produce any
expected reductions. We thus rejected
an interpretation where the state would
have to adopt ‘‘double’’ the measures
needed to satisfy the applicable
emissions reduction requirements
because EPA believes that this would be
an unreasonable requirement given the
difficulty many States will already have
in identifying and adopting sufficient
measures to meet ROP and other
requirements, let alone contingency
measures. See 57 FR at 13510–13512,
April 16, 1992.
Instead, EPA believes that the
contingency measures should, at a
minimum, ensure that an appropriate
level of emissions reduction progress
continues to be made if attainment or
ROP is not achieved and additional
planning by the state is needed.
Therefore, EPA has interpreted the Act
to require states with moderate and
above ozone nonattainment areas to
include sufficient contingency measures
so that, upon implementation of such
measures, additional emissions
reductions of up to 3 percent of the
emissions in the adjusted base year
inventory 26 (or such lesser percentage
that will cure the identified failure)
would be achieved in the year following
the year in which the failure has been
identified. This ‘‘additional’’ reduction
would ensure that progress toward
attainment occurs at a rate similar to
that specified under the ROP
requirements for moderate areas (i.e., 3
percent per year), and that the state
would achieve these reductions while
conducting additional control measure
development and implementation as
necessary to correct the shortfall in
emissions reductions and/or to adopt
newly required measures resulting from
26 The adjusted base year inventory is that
inventory specified by the provisions under section
182(b)(1)(B).
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reclassification to a higher
classification, in the case of a moderate
or serious area, or to meet the 3 percent
per year requirements specified by
section 181(b)(4)(A) of the Act for severe
areas that fail to attain. Under this
approach, the State would have 1 year
to modify its SIP and take other
corrective action needed to ensure that
milestones are achieved and that ROP
toward attainment continues. See 57 FR
at 13510–13512, April 16, 1992.
Section 182(c)(9) provides that ‘‘[i]n
addition to the contingency provisions
required under section [172(c)(9)] * * *
the plan revision [for serious and above
nonattainment areas] shall provide for
the implementation of specific measures
to be undertaken if the area fails to meet
any applicable milestone.’’ Section
172(c)(9) requires contingency measures
for failure of an area to ‘‘make
reasonable further progress, or to attain’’
the NAAQS. As clarified by section
182(g)(1) of the Act, the ‘‘applicable
milestones’’ for serious, and above,
nonattainment areas, such as the
Washington area, which is a severe
nonattainment area, are those tied to the
ROP plan percent emission reductions.
The commenter urges EPA to interpret
sections 172(c)(9) and 182(c)(9) to
require not only that there be
contingency measures in the SIP tied to
the ROP milestones for the Washington
area, but that these contingency
measures must be different from the
measures required under 172(c)(9).
We believe, however, that 182(c)(9)
merely adds milestones for serious and
above areas that must be included as
triggers for contingency measures, and
does not impose any requirement for a
state to adopt contingency measures in
addition to those being used in the
contingency plan required by section
172(c)(9), provided that such measures
will generate reductions in all the
relevant years.27 Thus a state may
specify the same contingency measure
to be used for failure to attain the
NAAQS as for failure to meet an ROP
milestone, in a year for which the
measure produces emission reductions.
Of course, if a measure is triggered for
failure to meet a milestone in an early
year the area would have to submit an
additional measure to be available in the
event of a later failure to meet a
subsequent milestone or demonstrate
attainment. Since the plain language of
27 We note that if a serious or above
nonattainment area fails to meet an applicable
milestone, the contingency measures will not even
necessarily be triggered. A state may opt to be
reclassified to the next higher classification or to
adopt an economic incentive program in lieu of
implementing the measures in its contingency plan.
42 U.S.C. 7511a(g)(3).
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the statute supports this interpretation,
and nothing in the statute prohibits this
interpretation, EPA’s interpretation of
how these two contingency measure
provisions relate to each other is
entitled to deference. See U.S. v. Mead
Corp., 553 U.S. 218 (2001); Chevron
U.S.A, Inc. v. NRDC, 467 U.S. 837
(1984).
Comment 4: We received a comment
asserting that the contingency plan does
not meet EPA’s guidance because the
plan does not contain a commitment for
timely adoption of additional measures
if the 3 percent contingency plan is not
adequate to correct a failure to attain or
achieve an ROP milestone.
Response 4: While EPA’s guidance
does specify that the States to backfill a
contingency measures plan after the
need for the measures is triggered
neither the statute nor the guidance
contains the sort of commitment
claimed by the comment.
‘‘Any implemented measures (that are
not needed for the rate-of-progress
requirements or for the attainment
demonstration) would need to be
backfilled only to the extent they are
used to meet a milestone * * *. The
State would be required to adopt new
contingency measures as part of the
process of developing their new SIP for
their new classification.’’ See section 5.6
of ‘‘Guidance on the Post ’96 Rate-ofProgress Plan (RPP) and Attainment
Demonstration’’ (Corrected version of
February 18, 1994). ‘‘Within 1 year of
the triggering of a contingency requiring
the early implementation of control
measures, the State must submit a
revision to the SIP containing whatever
additional measures will be needed to
backfill the SIP with replacement
measures to cure any eventual shortfall
that would occur as the result of the
early use of the contingency measure.’’
See 57 FR at 13511, April 16, 1992.
The commitment discussed in the
General Preamble (57 FR 13498 at
13511–31512, April 16, 1992) was to an
annual tracking program—not a
commitment to backfill the plan with
new measures. As interpreted in the
general preamble, EPA does not believe
that contingency measures are required
to completely fill any shortfall caused
by a failure. This will be filled by the
revised plan required to cure the failure.
Comment 5: We received a comment
asserting that the contingency plan must
contain some NOX reductions since the
ROP and attainment plans rely upon
NOX reductions as well as VOC
reductions.
Response 5: With regard to the need
for NOX contingency measures, EPA
disagrees with the comment that the
contingency plan must contain NOX
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contingency measures simply because
the ROP and attainment plans rely upon
NOX reductions. As to contingency
measures to address a failure to in the
ROP plans, the Act creates a clear
command that VOC reductions
presumptively meet the ROP
requirements applicable to moderate,
serious and worse areas. Section
182(b)(1)(A) requires a ROP plan for a
15 percent reduction in baseline VOC
emissions. EPA has never interpreted
the Act to allow NOX substitution in the
15 percent plan for an area which is
subject to subpart 2 of part D to Title I
of the Act and which is not already
covered by a 15 percent ROP plan. See,
section 1.1 of ‘‘Guidance on the Post1996 Rate-of-Progress Plan and
Attainment Demonstration’’ (corrected
version as of 2/18/94); see, 68 FR at
32826, June 2, 2003 (waiving the VOC
reduction requirement would require
‘‘absurd results;’’ ‘‘We believe that
absurd results will happen only rarely
in those cases where application of the
requirement in that area would thwart
the intent of Congress in enacting the
relevant provisions of the [Act].’’
Absurd results would require a showing
that ‘‘future VOC reductions required
under subpart 2 for a particular area
would actually cause ozone to increase
more than a de minimis amount,’’ and,
‘‘it would not be sufficient for the area
to show that VOC reductions would be
less beneficial than NOX reductions.’’)
See 68 FR at 32833, June 2, 2003.
Section 182(c)(2)(B) requires ROP
reductions averaging 3 percent per year
reduction in baseline VOC emissions.
Section 182(c)(2)(C) authorizes EPA to
accept ROP plans containing a lesser
percentage of VOC reductions plan if
the that substitutes NOX reductions in
accordance with EPA’s guidance.
The comment claims EPA’s policy
and guidance requires SIPs to provide
for contingency reductions in NOX
where the SIP for the area relies on NOX
substitution in lieu of or in addition to
VOC reductions. In support of this
position, the commenter quotes a
footnote in the General Preamble, 57 FR
13498, April 16, 1992. However, EPA
believes our interpretation of the Act set
forth in later guidance allows just the
opposite, namely, that the contingency
measures for both ROP and attainment
failures can provide for at least some
VOC reductions where the attainment
plan relies on VOC and NOX reductions
even if the ROP plan relies on all NOX
reductions. See ‘‘Guidance on Issues
Related to 15 Percent Rate-of-Progress
Plans,’’ Memorandum from Michael H.
Shapiro, Acting Assistant Administrator
for Air and Radiation to the Regional
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Division Directors, August 23, 1993.28
This later guidance provides that NOX
contingency reductions can be
substituted for VOC contingency
reductions, but plainly does not
preclude all of the contingency
reductions from being achieved through
VOC control.
Where a ROP plan relies upon 9
percent NOX reduction to demonstrate
ROP pursuant to section 182(c)(2)(C) of
the Act for one or more milestone years
after 1996, EPA believes that a
milestone failure caused by a shortage of
NOX reductions can be filled by VOC
reductions. Under EPA’s guidance for
NOX substitution, the VOC contingency
reductions would in essence change the
plan from one relying upon 9 percent
NOX reductions to a plan relying upon
a mixture of NOX and VOC percentage
reductions. For instance, a 1 percent
failure would change in such a ROP
plan from 9 percent NOX to 8 percent
NOX and at least 1 percent VOC.
EPA believes that the Washington
area attainment plans demonstrate
attainment through a strategy of VOC
and NOX control. Therefore, inclusion
of VOC measures in the contingency
measures plan is proper to address a
failure to attain.
Comment 6: We received a comment
alleging that all of the emission
reductions from the continency
measures are not ‘‘surplus’’ because
neither EPA nor the States have
quantified the total VOC and NOX
reductions needed to attain by
November 15, 2005. The comment
further claims that the use of a WOE
approach in the modeled demonstration
of attainment is incapable of identifying
the precise level of emission reductions
needed for attainment and thus does not
support the claim that there are
‘‘surplus’’ reductions in the SIP that can
be used for ‘‘contingency’’ purposes.
Response 6: The photochemical grid
modeling runs used in the SIP revisions
which were the subject of the April 17,
2003 final rule (68 FR 19106) are the
same as those photochemical grid
modeling runs used in the February
2004 SIP revisions which are the subject
of this final rule. The WOE analytical
methods and/or analyses that support
the modeled demonstration of
attainment in the February 2004 SIP
revisions, which are the subject of this
final rule, include the same WOE
analytical methods and/or analyses that
supported the modeled demonstration
of attainment which were the subject of
the April 17, 2003 final rule (68 FR
28 Reissued in Appendix D to ‘‘Guidance on the
Post-1996 Rate-of-Progress Plan and Attainment
Demonstration’’ (corrected version as of 2/18/94).
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25705
19106). This issue has been litigated by
the commenter and conclusively
decided in EPA’s favor. See Sierra Club
v. EPA, 356 F.3d at 304–307. In
addition, as noted in section IV. A. 2. of
the January 31, 2005 TSD prepared for
the February 9, 2005 NPR (70 FR 6796)
the States provided additional WOE in
the form of the results of EPA’s
photochemical grid modeling performed
for the Tier 2 final rule. See, sections VI.
A. 1. and 2. of ‘‘Technical Support
Document for Approval and
Promulgation of Air Quality
Implementation Plans; District of
Columbia, Maryland, and Virginia;
Attainment Demonstration for the
Metropolitan Washington, DC
Nonattainment Area,’’ dated January 31,
2005.
As discussed elsewhere in response to
comment, EPA believes that the States’
use of photochemical grid modeling
with an adjunct WOE analysis
demonstrates timely attainment and
meets the statutory requirements of the
Act and constitutes a modeled
demonstration of attainment.
Specifically, EPA incorporates by
reference the responses to comment in
section IV. A. ‘‘Comment on the
Attainment Demonstration Modeling’’ of
the preamble to this final rule. In the
TSD prepared for the NPR for this final
rule, EPA concluded that without the
reductions from the contingency
measures the SIP contained sufficient
creditable measures to achieve
emissions levels in the Washington area
of 331 TPD of VOC emissions and 491
TPD of NOX emissions.29
These overall emissions levels of 331
TPD of VOC and 491 TPD of NOX are
still less than the levels used in the
photochemical grid modeling which
assumed levels of 360 TPD of VOC
emissions and of over 500 TPD of NOX
emissions, and are sufficient to support
the WOE demonstration.30 The WOE
demonstration builds upon the
photochemical grid modeling by
considering other photochemical grid
modeling results, and the overall change
in emissions from the 1990 base year to
the 2005 attainment year. EPA
concludes that attainment is
29 Table IV.F–1 Relative Reductions on page A–
27 of ‘‘Technical Support Document for Approval
and Promulgation of Air Quality Implementation
Plans; District of Columbia, Maryland, and Virginia;
Attainment Demonstration for the Metropolitan
Washington, DC Nonattainment Area,’’ dated
January 31, 2005.
30 Table IV.F–1 Relative Reductions on page A–
27 of ‘‘Technical Support Document for Approval
and Promulgation of Air Quality Implementation
Plans; District of Columbia, Maryland, and Virginia;
Attainment Demonstration for the Metropolitan
Washington, DC Nonattainment Area,’’ dated
January 31, 2005.
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demonstrated without reliance upon the
reductions from the contingency
measures and therefore the reductions
from the contingency measures are
surplus for the purposes of attainment.
Comment 7: We received a comment
asserting that the SIP cannot rely on the
reformulated gasoline (RFG) program as
a ‘‘contingency’’ measure to address the
area’s failure to attain by 1999, because
the RFG program became mandated by
the Act once the Washington area
missed the 1999 attainment deadline.
The comment claims that contingency
measures are measures that must be in
addition to those mandated by the Act.
The comment also claims that RFG was
never intended as a contingency
measure and, thus, contrary to EPA’s
assertion, it is hardly a ‘‘penalty’’ to the
nonattainment area to disallow
contingency credit for a measure that
was never intended as a contingency
measure, and that was implemented at
a time when the area was already years
behind schedule in adopting adequate
ROP and attainment plans. The
comment further asserts that if the RFG
program is a permissible contingency
measure the agency’s guidance would
obligate the states to ‘‘backfill’’ the
measure with one year assuring
equivalent reductions and that the states
have not done so.
Response 7: EPA agrees with the
comment to the extent that it raises
questions about whether RFG can be
used as a contingency measure after an
area is reclassified to severe
nonattainment. The RFG requirement is
required under Title II of the Act once
an area is reclassified to severe
nonattainment. However, EPA believes
that whether or not RFG is a
contingency measure is not a deciding
factor whether EPA approve the
contingency measures plan in this case
because the plan contains other
sufficient measures to fulfill the
requirement. EPA concludes that the
contingency measures plan is
approvable even without considering
RFG to be a contingency measure and
thus EPA is not responding to the
allegations that RFG can not be
considered a contingency measure in
this case.
E. Comment Received Regarding the
TSD and EPA’s Response
We received the following comments
on our evaluation of the credits from the
States’ AIM coatings rules which was in
our January 12, 2005 TSD prepared for
the January 12, 2005 NPR. A summary
of these comments that we received on
our evaluation of the credits from the
States’ AIM coatings rules for the
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Washington area and our responses
follows.
Comment: We received one set of
comments that were critical of the
baseline per capita emission factor EPA
used to evaluate the States’ emission
reductions claims for the States’ AIM
coatings rules. Specifically, these
comments took issue with the precontrol baseline value of 4.5 pounds per
person per year (lbs/p/yr) that EPA
used. These comments also took issue
with the 6.7 lbs/p/yr emission factor
which was used by the States and which
is found in ‘‘Procedures for the
Preparation of Emission Inventories for
Carbon Monoxide and Precursors of
Ozone’’ (EPA–450/4–91–016), May
1991. These comments noted that EPA
has issued another document under
EPA’s ongoing Emission Inventory
Improvement Program with yet another
per capita emission factor of 5.7 lbs/p/
yr. In summary, the comments
questioned if any of the baseline per
capita emission factors (6.7, 5.7, or 4.5
lbs/p/yr) published by EPA is based
upon the best currently available data.
These comments supported EPA’s use of
the most recent California Air Resources
Board (CARB) survey data for deriving
the best estimate of the post-control per
capita emission factor to be realized
from the promulgation of the District’s,
Maryland’s and Virginia’s rules
modeled upon the Ozone Transport
Commission’s Model AIM coatings rule.
These comments advocate the position
that the CARB surveys provide the best
available data under federal data quality
criteria and asserts that the California
pre-control total emissions should be
similar on a per person basis to the rest
of the country. The commenter
examined the pre-control baseline used
by CARB and assert that the baseline per
capita emissions factor for VOC
emissions from AIM coatings in
California before controls should be 6.3
lbs/p/yr. The commenter states that this
6.3 lbs/p/yr factor is based upon CARB’s
data for VOC emissions from AIM
coatings for the years 1975 through
2004. The comments note that the first
significant AIM controls were not
adopted in California until 1984, and,
conclude that 1980 is an acceptable year
to use as a baseline year. The comments
state: California reports that in 1980,
according to its surveys, there were
148,579,090 pounds of VOC emitted
from AIM coatings; the population of
California in 1980 according to the U.S.
Census Bureau was 23,668,000 people,
and thus this yields a pre-control
baseline of 6.3 lbs/p/yr. The commenter
therefore urges EPA to evaluate the
benefits from the States’ AIM coatings
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rules using a pre-control baseline of 6.3
lbs/p/yr.
We received a second set of comments
supporting the States’ analysis of the
reduction credits from the States’ AIM
coatings rules but critical of EPA’s
reliance upon CARB data to determine
a per capita emission factor after
application of the States’s AIM coatings
rules. These comments assert that
because California has had more
restrictive VOC limits for architectural
coatings for over a decade, VOC
emissions for architectural and
industrial maintenance coatings in
California were already significantly
lower than the States’ pre-rule
emissions.
Response: The States’ Contingency
Measures, ROP and Attainment Plans
Are Still Approvable. EPA has
considered both set of comments and
analyzed the sufficiency of the
contingency measures, ROP and
attainment plans by considering the
baseline emission factors and reduction
calculation methodologies advocated by
each set of comments, as well as the
baseline emission factors and reduction
calculation methodology contained in
our January 5, 2005 TSD that was
prepared for the January 12, 2005 (70 FR
2085) NPR.31 EPA concludes that the
contingency measures, ROP and
attainment plans are approvable
regardless of whether we use the
baseline emission factor and reduction
calculation methodology advocated by
each set of comments, or whether we
use the baseline emission factors and
reduction calculation methodology
contained in our January 5, 2005 TSD.
EPA has evaluated the effect that
changing the 1990 per capita emission
factor for the AIM coatings source
category might have on the contingency
measures implemented to address the
failure of the Washington area to attain
in 1999, the 1999–2005 ROP plans, and
the attainment demonstration plans.
EPA has determined that regardless of
which of the 1990 per capita emission
factors and reduction calculation
methodologies—be it that advocated by
the first set of comments, or that
advocated by the second set of
comments, or that found in our
technical support for the January 12,
2005 (70 FR 2085) NPR—the States
secure sufficient VOC reductions to
meet the needs of the contingency
31 ‘‘Technical Support Document for Approval
and Promulgation of Air Quality Implementation
Plans; District of Columbia, Maryland, and Virginia;
Post-1996 Rate-of-Progress Plan, Contingency
Measures, Transportation Control Measures, 1990
Base Year Inventory Changes, and VMT Offset SIP
for the Metropolitan Washington, DC
Nonattainment Area,’’ dated January 5, 2005.
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measures plan for failure to attain in
1999, the 1999–2005 ROP plans or
attainment plans. As noted in the
January 12, 2005 NPR, the States
computed that the reductions needed to
address the 1999 failure to attain
contingency requirement was at least
13.0 TPD.32 Of these 13.0 TPD, 11.4
would be filled by the solvent cleaning
and portable fuels containers rules. The
States’ AIM coatings rules would thus
have to provide at least 1.6 TPD of
reductions to ensure that the
contingency plan is approvable. EPA
has evaluated the effects that changing
the 1990 per capita emission factor and
reduction methodologies for the AIM
coatings source category might have on
the contingency plan for failure to attain
by 1999. The States ascribed 12.3 tons
per day reduction from the States’ AIM
coatings rules. EPA arrived at a value of
over 16 tons per day using the 4.5
pounds per capita emission factor.33
EPA concludes that the States’
contingency plans are still approvable.
There is no effect on the approvability
of the 1999–2005 ROP plans because
any change in the 1990 per capita
emission factor for the AIM coatings
source category or the method to
determine reduction from the States’
AIM coatings rules will only affect VOC
emission reductions. EPA proposed
approval of the 1999–2005 ROP plans
based solely upon a showing that the
plans provided for a minimum 9 percent
reduction in baseline NOX emissions by
the 2002 milestone and a further 9
percent by 2005. As discussed
elsewhere in this document in response
to comment, EPA is approving the
1999–2005 ROP plans based upon these
NOX reductions alone.
With respect to the demonstration of
attainment, EPA evaluated the overall
change in VOC emissions relative to
1990 base year emissions which would
result from using the 4.5 or the 6.3
pounds per capita emission factor. The
results were an overall relative
reduction in VOC emissions of 45
percent in 1990 VOC emissions by 2005
from all sources (point plus area plus
nonroad plus on-road). The States’
credit claims corresponded to a
projected overall 42.8 percent reduction
in 1990 VOC emissions by 2005 from all
sources (point plus area plus nonroad
32 See Table 12. Contingency Measures in the
NPR for this action (70 FR 2085 at 2096, January
12, 2005).
33 The comments advocating the 6.3 pounds per
capita emission factor did not advocate by what
percentage this value would be reduced by the 1998
Federal AIM coatings rule, EPA assumed for the
purposes of this analysis that the Federal AIM
coatings rule would result in the same post-rule per
capita emission factor.
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plus on-road). 70 FR at 6803, February
9, 2005. EPA concludes that the States’
estimate of the overall relative reduction
in VOC emissions is conservative
relative to the use of either the 4.5 or the
6.3 emission factors. EPA concludes that
using either baseline the States get at
least the reductions they claimed and
needed to demonstrate timely
attainment, to meet the ROP
requirements, and to provide for
sufficient reduction for the contingency
plan. EPA concludes that the issues
raised in the comments do not change
the approvability of the attainment
plans.
After considering the comments
received during the public comment
period, EPA’s analysis indicates that the
reduction claims in the February 2004
SIP revisions are supported using the
alternative per capita base line emission
factors in the record in that the States’
reduction claims are less than the other
methods. EPA is neither approving nor
disapproving the States’ method nor
promoting an alternative method. EPA’s
analysis in support of this rulemaking is
to determine if any information received
during the comment period would give
cause for us to reconsider our proposed
approval. Regardless of which of the
baseline emission factors or methods
that have been proffered by the
commenters or by EPA is used to
calculate VOC emission reductions for
the States’ AIM coatings rules, we have
determined that the States’ ROP,
attainment and contingency measures
plans for the Washington area
demonstrate ROP, provide sufficient
VOC reductions to satisfy the need for
implemented contingency measures set
by EPA’s guidance and demonstrate
attainment. Therefore, EPA is approving
the States’ SIP revisions.34 Further
details of EPA’s analysis can be found
in the supplemental TSD prepared for
this final rule.35
A determination of the best baseline
from which to estimate the reductions
from the States’ AIM rules is not
essential for this final rule because, as
stated earlier, regardless of whether
those reductions are calculated as
34 As noted elsewhere in this doucment, EPA is
not approving Maryland’s attainment plan for the
Washington area but is making a finding that
Maryland’s attainment plan, in conjunction with
those of the District and Virginia, contains control
measures that ‘‘fully satisfy the emission reduction
requirements relevant to * * * attainment.’’
35 ‘‘Supplement to the Technical Support
Document for Approval and Promulgation of Air
Quality Implementation Plans; District of Columbia,
Maryland, Virginia; 1-Hour Ozone Attainment
Plans, Rate-of-Progress Plans, Contingnecy
Measures, Transportation Control Measures, VMT
Offset, and 1990 Base Year Inventory,’’ dated May
3, 2005.
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proposed by EPA or as advocated by
either of the commenters, the States’
ROP, attainment and contingency
measures plans demonstrate ROP,
provide sufficient VOC reductions to
satisfy the need for implemented
contingency measures, and demonstrate
attainment.
However, EPA recognizes the need to
resolve conclusively how to determine
the amount of VOC emission reductions
achieved from the implementation of
AIM coatings rules in a given ozone
nonattainment area. This remains an
issue of concern to the states, the
regulated sector, and other interested
parties. Therefore, EPA intends to
conduct a separate process to solicit
further comment, information and
recommendations from all interested
parties as to how to determine the
amount of VOC emission reductions
achieved from the implementation of
AIM coatings rules in a given ozone
nonattainment area.
EPA’s Policy on Changes in Inventory
Methods. EPA is clarifying its proposal
in the NPR (70 FR 2085) that EPA was
not proposing that the District,
Maryland and Virginia change the ROP
plans to reflect a new 1990 per capita
emission factor for the AIM source
category prepared for this action, but
rather intended to verify that the ROP
plans were adequate without using the
reduction methodology upon which the
States relied.
EPA acknowledges that emissions
factors, as well as inventory calculation
methodologies, are continually being
improved. In general, EPA has not
required changes to submitted SIPs that
result from changes in factors and
methodologies that occur after the SIP is
submitted. With respect to the 15
percent plan due in November 1993, in
section 2.4 of ‘‘Guidance on the
Adjusted Base Year Emissions Inventory
and the 1996 Target for 15 Percent Rateof-Progress Plans’’ (EPA–452/R–92–005)
EPA stated: ‘‘If other significant changes
occur in emissions factors or
methodologies before which time it is
impossible for states to make
adjustments to their 15 percent
calculations and associated control
strategies, then EPA may require states
to make corrections to the base year
emissions inventory, as well as to the
adjusted base year inventory and the
1996 target level of emissions.’’ This
guidance discussed the then pending
transition from the MOBILE4.1 model to
the MOBILE5 model but only
prospectively, by requiring that
emissions values calculated using
MOBILE4.1 would have to be
recalculated using MOBILE5 before
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submittal of the final ROP plans in
November 1993.
Likewise with respect to the post1996 ROP plans, EPA has advised the
states when changes in emissions
factors or in methodologies for
developing emissions inventories would
force revisions to the inventories or
plans. Changes would be necessary if
they occurred before the plan was
submitted. ‘‘However, if such changes
occur after November 15, 1991, but prior
to November 15, 1994, a serious or
above area may be required to make
corrections to the base year inventory
and attainment year projection
inventory for purposes of developing
the 3 percent rate-of-progress
demonstration. If such changes occur
after November 15, 1994, EPA will
advise on when it would be appropriate
for the states to make corrections in
future supplements to this General
Preamble.’’ 57 FR at 13517 (April 16,
1992). In the context of the guidance,
‘‘November 15, 1994’’ would mean the
date by which the post-1996 plan was
due. In the case of the Washington area,
the 1996–1999 ROP plans were due on
November 15, 1994 because the area
was serious nonattainment area, and the
1999–2005 ROP plans were due by
March 1, 2004, which was the date
established in our final rule
reclassifying the Washington area to
severe nonattainment. See 68 FR 3410 at
3422, January 24, 2003.
From the States’ perspective, the
baseline per capita emission factor of
4.5 pounds per person per year (lbs/p/
yr) for the AIM coatings source category
could be seen as a change in factors and
methodologies which occurred after the
SIP is submitted. As for the 1996–1999
ROP plans, EPA notes that the plan was
projected to have a surplus of 14 tons
per day in VOC emission reductions.
Nor did EPA propose that the States do
so in the NPR (70 FR 2085) prepared for
this action. Indeed, to require the States
to revise completed plans every time a
new emission factor or changed
methodology is announced would lead
to significant costs and potentially
endless delays in the approval
processes. In the case of the 1996–1999
ROP plans, any possible claim that EPA
required a ‘‘changed methodology’’
would have to accept that the ‘‘changed
methodology’’ came to light years after
the 1996–1999 ROP plans were
submitted. For the policy reasons stated
previously, EPA has not required the
States revise their 1996–1999 ROP plans
for the Washington area.
Additional Response to the Second
Set of Comments. EPA further believes
that the second set of comments
misstates the role CARB data played in
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the EPA’s estimate of the OTC rule
reduction. EPA used data from CARB to
ascertain an end point for the OTC rule
(post-OTC rule per capita emission
factor) not a 1990 baseline factor. EPA
did so in order to evaluate the States’
reduction claims using methods other
than those used by the States for the
reasons stated in the January 12, 2005
(70 FR 2085) NPR.
IV. Comment Received on the
Attainment Demonstration and EPA’s
Response
We received the following additional
comments adverse to the proposed
approval of the attainment plans. In
addition to comments that are unique to
the attainment plan (set forth in sections
IV. A. and IV. B of this document), we
also received a number of comments
identical to those submitted in relation
to the ROP plans, VMT Offset SIPs, and
contingency measure plans, to which
we responded in section III of this
document. We have set forth in this
section of this document each comment
we received relevant to the attainment
demonstrations and plans and respond
separately to it even if that comment is
identical to a comment to which we
responded in section III. A summary of
these additional adverse comments that
we received on our proposed action to
approve the attainment plans for the
Washington area and our responses
follows.
A. Comment on the Attainment
Demonstration Modeling
Comment: We received a comment
asserting that the SIP does not
demonstrate attainment as required by
the Act. The comment alleges that
attainment is not demonstrated using
photochemical grid modeling, or other
analytical tool which EPA has
determined to be at least as effective,
that the WOE approach does not satisfy
the CAA’s requirement to assure
attainment as expeditiously as
practicable or the CAA’s requirement for
a modeled demonstration of attainment,
that EPA provides no evidence that the
core assumption underlying its WOE
approach—i.e., that ozone will be
reduced in the same proportion as
emissions—is valid. The comment
alleges that such an assumption
conflicts with EPA’s own repeated
findings that the relationship between
ozone formation and precursor
emissions is nonlinear, and cannot be
accurately predicted by means other
than photochemical grid models. The
comment also asserts that the
photochemical grid model used in the
modeled demonstration of attainment
and WOE analysis is not based upon a
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photochemical grid model that
represents sound science and that meets
current regulations and guidance.
Therefore, the comment claims EPA
cannot approve the WOE determination.
Response: Attainment Is
Demonstrated Using Photochemical
Grid Modeling, the Woe Approach
Satisfies the Act Requirements. The
photochemical grid modeling runs used
in the pre-2001 SIP revisions’
attainment plan are the same as those
photochemical grid modeling runs used
in the February 2004 SIP revisions
which are the subject of this final rule.
The WOE analytical methods and/or
analyses that support the modeled
demonstration of attainment in the
February 2004 SIP revisions, which are
the subject of this final rule, include the
same WOE analytical methods and/or
analyses that supported the modeled
demonstration of attainment which
were the subject of the April 17, 2003
final rule (68 FR 19106). In addition, as
noted in section IV. A. 2. of the January
31, 2005 TSD prepared for the February
9, 2005 NPR (70 FR 6796) the States
provided additional WOE in the form of
the results of EPA’s photochemical grid
modeling performed for the Tier 2 final
rule. See, sections VI. A. of ‘‘Technical
Support Document for Approval and
Promulgation of Air Quality
Implementation Plans; District of
Columbia, Maryland, and Virginia;
Attainment Demonstration for the
Metropolitan Washington, DC
Nonattainment Area,’’ dated January 31,
2005.
EPA had received a comment from the
same commenter alleging the same
deficiencies of WOE for the same
photochemical grid modeling runs and
some of the same adjunct WOE analyses
when EPA conditionally approved the
pre-2001 SIP revisions’ attainment plan.
Specifically the commenter had alleged
that photochemical grid modeling
shows that the Washington area will not
attain the ozone standard by the
November 2005 attainment date and
because the WOE analysis used by EPA
to conclude that the Washington area
has demonstrated attainment by
November 2005 is not authorized by the
Act or by EPA rules. The commenter
had claimed that the modeling
demonstration and WOE used in the
attainment demonstration for the
Washington area do not meet
requirements of section 182(c) of the
[Act] and EPA’s own regulations for
photochemical grid modeling and other
analytical methods, that the WOE is an
alternative method to photochemical
grid modeling which has not been
shown to be equally effective to the
Urban Airshed Model (UAM), and that
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WOE is a proscribed rollback method.
See 68 FR 19106 at 19111/3, April 17,
2003.
The claim in the comment from the
same commenter received during the
public comment period for this
rulemaking ‘‘that ozone will be reduced
in the same proportion as emissions’’
merely restates the claim that the WOE
approach relies upon ‘‘’proportional’’’
rollback. Likewise, the comment on this
rulemaking assert that the modeled
demonstration of attainment does not
meet the CAA’s requirement for a
modeled demonstration of attainment or
that attainment is not demonstrated
using a photochemical grid model and
that WOE does not demonstrate timely
attainment simply restate, with less
specificity, comment made by the same
commenter on our April 17, 2003 final
rule, 68 FR 19106. See 68 FR 5246,
February 3, 2003.
EPA provided responses to these
comments in our April 17, 2003 final
rule (68 FR 19106) and incorporates our
responses in the April 17, 2004 final
rule by reference, particularly those in
response to ‘‘comment 1’’ on pages
19111 to 19112 of the April 17, 2003
final rule. See 68 FR 19112–19115,
April 17, 2003.
Furthermore, this commenter’s
assertions that EPA’s use of
photochemical grid modeling with an
adjunct WOE analysis does not
demonstrate timely attainment, violates
statutory requirements of the Act and
does not constitute a ‘‘modeled
demonstration of attainment,’’
encompasses all those issues related to
WOE that the commenter has restated in
this rulemaking, and were briefed and
litigated to conclusion in a suit brought
by the commenter against EPA. See
Sierra Club v. EPA, 356 F.3d at 304–07;
see also Initial Opening Brief of
Petitioner Sierra Club, Docket No. 03–
1084 (June 23, 2003), pp. 25–37; Final
Reply Brief of Petitioner Sierra Club,
Docket No. 03–1084 (September 22,
2003), pp. 8–19. The Court of Appeals’
decision upholding the very same
photochemical grid modeling and WOE
that is at issue herein (as resubmitted by
the States and supplemented with an
analysis of the effects of the Tier 2 rule
that strengthened the conclusion of the
WOE analysis), is binding on both EPA
and the commenter. After extensively
analyzing the record, the Court of
Appeals resolved the commenter’s
claims in EPA’s favor with respect to the
Urban Airshed Model–IV (UAM–IV) and
the WOE analysis, stating:
‘‘[P]hotochemical modeling [using the
UAM–IV] is the primary basis for the
attainment demonstration,’’ while the [WOE]
‘‘is merely an adjunct for assessing the
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photochemical grid modeling. * * * ’’ [T]hat
analysis was employed to ensure that the
model achieved its statutory purpose:
determining whether the SIPs actually
‘‘provide for attainment of the ozone national
ambient air quality standard by the
applicable attainment date.’’ 42 U.S.C.
7511a(c)(2)(A). And the adjustments appear
well-suited to that end, as they do no more
than correct for the model’s over-prediction
of ozone levels as compared to actual
observations, and for its reliance on a base
day that appears to be a statistical outlier.
See, Sierra Club v. EPA, 356 F.3d at 306.
Res judicata bars re-litigation not only
of matters determined in a previous
litigation but also ones that a party
could have raised. * * * Collateral
estoppel further bars parties from relitigating issues of law or fact resolved
in prior cases between those parties.
* * * (When a court determines an
issue of fact or law that is actually
litigated and necessary to its judgment,
that conclusion binds the same parties
in a subsequent action.).’’ Appalachian
Power Co. v. EPA, 251 F.3d 1026, 1033–
34 (D.C. Cir. 2001) (internal citations
and quotations omitted). While EPA
believes that the commenter is
precluded from re-litigating the binding
holding of the court in Sierra Club v.
EPA with respect to the validity of WOE
analyses, EPA reiterates that, as
articulated and explained in the April
17, 2004 final conditional approval rule
at 68 FR 19112–19115, April 17, 2003,
WOE in general as a supplement to
photochemical grid modeling, and
Washington Area WOE analysis in
particular (as upheld by the Court of
Appeals), is a valid tool for
demonstrating attainment with the
NAAQS. The Washington Area WOE
analysis demonstrates that the
Washington Area will timely attain the
1-hour ozone NAAQS for all the reasons
previously explained in the April 17,
2004 final conditional approval.
EPA continues to believe that the
commenter is wrong on the law, as
EPA’s use of WOE as an analytical
adjunct to photochemical grid modeling
has been successfully litigated to
conclusion several times. Each time the
Court of Appeals has upheld both EPA’s
interpretation of the Act to allow
supplemental analysis to photochemical
grid modeling to demonstrate
attainment, and EPA’s determination
that each of the WOE analyses at issue,
including the core of the WOE analysis
at issue in the conditional approval and
in this current rulemaking, was valid.
See 356 F.3d at 304–07; Environmental
Defense v. EPA, 369 F.3d 193, 203–07
(2d Cir. 2004); BCCA Appeal Group v.
EPA, 348 F.3d 817, 203–09 (5th Cir.
2003). Accord, 1000 Friends of
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25709
Maryland v. Browner, 265 F.3d 216, 234
(4th Cir. 2001).
The Amendments to Appendix W Do
Not Preclude Use of UAM–IV. EPA
disagrees that the use of the UAM–IV for
photochemical grid modeling represents
a reason to disapprove the attainment
plan even though UAM–IV is no longer
on the list of refined models that are
preferred or recommended for use in
regulatory applications. EPA notes that
no other photochemical grid models for
modeling urban areas are on the
preferred list found in Appendix A to
Appendix W to 40 CFR part 51, even
though the Act reflects a clear
preference, or, in the case of serious and
worse areas, essentially mandates that a
modeled demonstration of attainment be
based on photochemical grid modeling.
42 U.S.C. 7511a(c)(2)(A); (j)(1)(B). All
photochemical grid models for
modeling ozone in urban areas are on
EPA’s list of alternative models which is
now posted on the internet as opposed
to being issued as Appendix B to
Appendix W to 40 CFR part 51.
Nothing in the Appendices to 40 CFR
part 51 indicate that EPA may no longer
rely on UAM–IV modeling, or that other
photochemical grid models are
mandated for use in lieu of UAM–IV.
The ‘‘[s]imulation of ozone formation
and transport is a highly complex and
resource intensive exercise. Control
agencies with jurisdiction over areas
with ozone problems are encouraged to
use photochemical grid models, such as
the Models-3/Community Multi-scale
Air Quality (CMAQ) modeling system
* * * to evaluate the relationship
between precursor species and ozone.’’
See section 6.2.1.a. ‘‘Choice of Models
for Multi-source Applications’’ in
Appendix W to 40 CFR part 51
(emphases added); see also 68 FR at
18457–18458, April 15, 2003.
Explicitly, the ‘‘[d]etermination of
acceptability of a model is a Regional
Office responsibility. Where the
Regional Administrator finds that an
alternative model is more appropriate
than a preferred model, that model may
be used subject to the recommendations
of this subsection. This finding will
normally result from a determination
that (1) a preferred air quality model is
not appropriate for the particular
application; or (2) a more appropriate
model or analytical procedure is
available and applicable. (emphasis
added). See section 3.2.2 in Appendix
W to 40 CFR part 51. See 68 FR at
18452, April 15, 2003.
In this case, the States had submitted
the pre-2001 SIP revisions’ attainment
plan which demonstrated that the States
had sufficient measures in the SIP to
demonstrate that the Washington area
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would attain the 1-hour ozone NAAQS
no later then November 15, 2005. EPA
acknowledged that the SIP could not be
fully approved at that time because the
States had not demonstrated that all
RACM had been adopted and the plan
lacked certain other elements which we
initially identified in our February 3,
2003 proposed conditional approval.
See 68 FR 5246, February 3, 2003. All
that adoption of additional rules as
RACM would have done to the
attainment plan would be to strengthen
the WOE that the area would timely
attain or advance the date by which the
area would attain. Of the other elements
noted as needing revision under the
conditional approval, the only one
which could possibly have implicated
the modeling demonstration was a
proposed condition that required the
States to commit to revise and submit to
the EPA by April 17, 2004, an updated
attainment plan SIP that reflects revised
MOBILE6-based MVEBs, including
revisions to the attainment modeling
and/or WOE demonstration, as
necessary, to demonstrate that the SIP
continues to demonstrate attainment by
November 15, 2005. See 68 FR at 5253,
5258, 5260–5261, February 3, 2003. We
included this condition in our April 17,
2003 (68 FR 19106) final rule
conditionally approving the pre-2001
SIP revisions’ attainment plan.
The States readily agreed to this
condition because, in their pre-2001 SIP
revisions’ attainment plan, the States
had included a commitment to revise
the 2005 attainment MVEBs within oneyear of the EPA’s release of the
MOBILE6 model. See 66 FR at 631–632
(regulatory text for 40 CFR 52.476(c),
52.1076(g) and 52.2428(d)), January 3,
2001. By the time we issued the April
17, 2003 conditional approval EPA had
released the MOBILE6 model and its
implementing guidance. That guidance
does not mandate redoing the entire
modeling demonstration due to a
change in the MVEBs.36 EPA reasonably
believes that the Act does not mandate
a revision to the photochemical grid
modeling due to a change in the MVEBs,
and, this interpretation has been upheld
on review. See 1000 Friends of
Maryland v. Browner, 265 F.3d 216 (4th
Cir. 2001). EPA concludes that where
MVEBs are changed the state must
analyze the impacts of such change on
the modeled attainment demonstration,
36 See, Joint memorandum dated January 18,
2002, From John S. Seitz, Director, Office of Air
Quality Planning & Standards, and Margo Tsirigotis
Oge, Director of Office of Transportation and Air
Quality, ‘‘Policy Guidance for the Use of MOBILE6
in SIP Development and Transportation
Conformity.’’
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but that the state need not rerun the
entire model.
In this case EPA believes that
disapproving the February 2004 SIP
revisions based on alleged defects in the
modeling demonstration for the reason
cited in the comment would be arbitrary
and capricious because in the February
3, 2003 notice of proposed rulemaking
(68 FR 5246) EPA did not propose to
require that the States redo the
photochemical grid modeling. Because,
as of February 3, 2003, the changes to
Appendix W to 40 CFR part 51 had not
been issued, only, proposed,37 EPA
believes that it would not have been
appropriate to disapprove the SIP
revisions in the April 17, 2003 final rule
which was the final action issued
pursuant to the February 3, 2003 NPR.
We believe that it would not be
appropriate to disapprove the SIP
revisions now because the States have
relied on the same photochemical grid
modeling analysis for the February 2004
SIP revisions as they previously did.
In addition, the modeled
demonstration of attainment does not
depend solely upon the UAM–IV
modeling results. The WOE contained
in the February 2004 SIP revisions
relied upon EPA’s modeling conducted
for the NOX SIP call and the Tier 2
rulemaking. These modeling rules relied
upon photochemical grid modeling that
used the UAM–V and/or the CAMx
models. See, 63 FR 57356 at 57381,
October 27, 1998; ‘‘Technical Support
Document for the Tier 2/Gasoline Sulfur
Ozone Modeling Analyses,’’ EPA420–R–
99–031, December 1999. The UAM–V
and the CAMx models are among those
listed on the replacement for what was
formerly Appendix B of the Guideline
on Air Quality Models (Appendix W to
40 CFR Part 51). ‘‘The models listed in
this section are: ADAM, ADMS,
AFTOX, ASPEN, CAMx, CMAQ,
DEGADIS, HGSYSTEM, HOTMAC,
HYROAD, OZIPR, OBODM, Panache,
PLUVUEII, REMSAD, SCIPUFF, SDM,
SLAB, UAM–V.’’ (See https://
www.epa.gov/scram001/
tt22.htm#altmod, last checked April 6,
2005). For these reasons, EPA believes
the Regional Administrator
appropriately and reasonably exercised
the discretion afforded by Appendix W
to allow the continued use of the UAM–
IV modeling results in this particular
case.
Furthermore, the law is well
established that res judicata bars relitigation not only as to all matters
actually determined in prior litigation,
37 The final rule amending Appendix W was
signed on April 2, 2003, nearly two months after the
proposed conditional approval.
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but also as to all matters that might have
been determined. See, e.g., Appalachian
Power, supra, at 1033–34; Natural
Resources Defense Council, Inc. v.
Thomas, 838 F.2d 1224, 1235 (D.C. Cir.
1988). EPA proposed to remove UAM–
IV as obsolete on April 21, 2001. 65 FR
21506. EPA proposed the conditional
approval based on WOE. See 68 FR
5246, February 3, 2003. As noted
previously, EPA took final action to
remove UAM–IV as obsolete on April
15, 2003, 68 FR 18440, two days before
final action on the conditional approval,
April 17, 2003. See 68 FR at 19121. The
commenter did not raise the issue that
UAM–IV was no longer a preferred
model listed in Appendix A of
Appendix W to 40 CFR 51 in its
comments on the conditional approval,
and in the subsequent litigation over
that EPA action, although it could have,
although the commenter had raised the
general issue that the modeling
demonstration and WOE used in the
modeled demonstration of attainment
for the Washington area did not meet
requirements of section 182(c) of the Act
and EPA’s own regulations for
photochemical grid modeling and other
analytical methods.38 See 68
FR at 19111, April 17, 2003. Res
judicata would bar raising the UAM–IV
claim now as it could have been
litigated in the suit over EPA’s
conditional approval. Nevertheless, and
without waiving its contention that res
judicata and/or collateral estoppel bar
litigation of the UAM–IV claim, for the
reasons stated previously in this
response, EPA believes: (1) The
Regional Administrator appropriately
and reasonably exercised the discretion
afforded by Appendix W to allow the
continued use of the UAM–IV modeling
results in this particular case, (2) EPA’s
guidance is reasonable and is not a
38 The fact that EPA had not finalized its
proposed removal of UAM–IV as an approved
model was no bar to raising this issue in the
litigation over the Conditional Approval. Section
307(d)(7)(B) of the Act specifically allows, if certain
conditions are met, for comment on a rule after the
comment period was closed if ‘‘it was impracticable
to raise such objection within such time or if the
grounds for such objection arose after the period for
public comments (but within the time specified for
judicial review. * * * ’’ Although EPA’s proposal
clearly demonstrated its intention to remove the
UAM–IV as a preferred model three years prior to
the opening of the comment period on the
Conditional Approval, EPA’s final action on the
UAM–IV occurred just two days prior to the
Conditional Approval, thereby arising within the
time period specified by Section 307(d)(7)(B).
Importantly, the commenter did not invoke this
administrative reconsideration provision of the Act
at the time of the conditional approval. Had the
Court of Appeals not vacated and remanded the
conditional approval for reasons entirely unrelated
to the WOE analysis issue, the commenter would
not have been afforded opportunity to attempt add
to the record on WOE.
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proportional rollback, (3) WOE and the
photochemical grid modeling used to
demonstrate attainment is consistent
with the Act and EPA regulations.
B. Comment On the MVEBs
Comment: We received a comment
that EPA cannot approve the MVEBs in
the attainment plan SIP because the
NOX budgets are 70 tons per day higher
than those in the previous attainment
SIP budget for the same year. The
comment claims that the MVEBs in the
previous attainment plan were
inadequate because that SIP did not
demonstrate attainment with
photochemical grid modeling as
required by the Act and did not include
all reasonably available transportation
control measures. The comment asserts
that because the MVEBs in the previous
attainment plan were inadequate EPA
cannot approve the NOX MVEBs that are
70 tons per day higher and that EPA
does not demonstrate, with
photochemical grid modeling as
required by the Act, how it can assure
attainment in 2005 with such a major
increase in allowable motor vehicle
emissions.
Response: EPA disagrees with the
comment that the MVEBs in the SIP
revisions are inadequate. EPA had
proposed to conditionally approve the
previous attainment plan and in the
alternative to disapprove the attainment
plan with a protective finding that
would allow the MVEBs to be used for
transportation conformity purposes. Our
proposed protective finding was based
upon our conclusion that the pre-2001
SIP revisions’ attainment plan, which
were the subject to the February 3, 2003
notice of proposed rulemaking, had
demonstrated that the Washington area
will attain the 1-hour ozone NAAQS no
later than November 15, 2005, by
providing enough reductions with
adopted measures to demonstrate
attainment. See 68 FR at 5259, February
3, 2003. Our final conditional approval
was granted on the basis that the pre2001 SIP revisions’ attainment plan did
demonstrate attainment with
photochemical grid modeling as
required by the Act. We granted a
conditional, rather than a full approval
solely on the basis that the pre-2001 SIP
revisions’ attainment plan lacked some
adopted measures required by an
attainment plan for a severe ozone
nonattainment area. See 68 FR 19106
(April 17, 2003). While the conditional
approval itself was vacated, our
determination that the modeled
demonstration of attainment in the pre2001 SIP revisions’ attainment plan
demonstrated attainment with
photochemical grid modeling as
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required by the Act was specifically
upheld. Sierra Club v. EPA, 356 F.3d at
304–307.
The conditional approval was
predicated in part upon the States
revising and submitting to the EPA by
April 17, 2004, SIP revisions
constituting an update to the attainment
plan incorporating MOBILE6-based
MVEBs. Further, the States would need
to include in the submittal revisions to
the attainment modeling and/or WOE
demonstration, as necessary, to show
that the SIP would continue to
demonstrate attainment by November
15, 2005. See 68 FR at 5258, February
3, 2003.
EPA acknowledged at the time of the
conditional approval the possibility that
the MVEBs in the pre-2001 SIP
revisions’ attainment plan might not
have included all RACM or all adopted
transportation control strategies and
TCMs to offset increases in emissions
resulting from growth in VMT or
numbers of vehicle trips and to obtain
reductions in motor vehicle emissions
as necessary (in combination with other
emission reduction requirements) to
comply with the CAA’s ROP milestones
and attainment demonstration
requirements. We had conditioned
approval of the pre-2001 SIP revisions’
attainment plan upon the States
adopting any remaining RACM and any
required TCMs. See 68 FR at 19106–
19107, 19129–19130 (April 17, 2004).
For the reasons outlined in our
notices of proposed rulemakings, and in
conjunction with response to comments
elsewhere in this document, EPA has
concluded that the SIP revisions now
before us demonstrate that all RACM
has been adopted and that the SIP
contains all necessary transportation
control strategies and TCMs to offset
increases in emissions resulting from
growth in VMT or numbers of vehicle
trips and to obtain reductions in motor
vehicle emissions as necessary (in
combination with other emission
reduction requirements) to demonstrate
attainment and ROP.
EPA disagrees that the ‘‘70’’ ton per
day increase from the mobile sector is
the only relevant criterion for analyzing
the impact of the MVEBs. MVEBs exist
in the context of the attainment plan
and do not in and of themselves
determine whether an area will attain
the NAAQS. MVEBs merely are the
amount of motor vehicle emissions
allowed by a control strategy SIP which
consists of, among other things the
estimated further reductions from
adopted rules affecting all source
categories including stationary and area
sources in the States’ SIPs or
promulgated by EPA. A change in the
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MVEBs higher or lower cannot, in a
vacuum, lead to a conclusion as to
whether an area is still on track to attain
the NAAQS. Rather, the MVEBs must be
considered in context, as follows:
EPA first addressed the sufficiency of
the attainment plan in our first round of
rulemaking on the pre-2001 SIP
revisions’ attainment plan. See 68 FR at
5249 (February 3, 2003) (citing 64 FR
70460 (December 16, 1999); 66 FR 586
(January 3, 2001).
In the December 16, 1999 NPR we
noted that the ‘‘1998 SIP revisions’’ did
not contain adequate MVEBs.39 In the
December 16, 1999 (64 FR 70460), NPR,
we also stated that:
[A] motor vehicle emissions budget is the
estimate of motor vehicle emissions in the
attainment year that when considered with
emissions from all other sources is consistent
with attainment. The attainment
demonstrations for the Washington area
contain levels of modeled emissions that EPA
concludes demonstrate attainment once
transport from upwind areas is addressed.
The basis for this conclusion will not be
altered if the Washington area States can
demonstrate that the level of nonattainment
area emissions in 2005 is equal to or less than
the 1999 control strategy levels contained in
the attainment demonstrations considering
growth. 64 FR at 70473.
In other words, we required the States
to revise the MVEBs and to demonstrate
that the SIP contained enough measures
that when considered with the revised
2005 MVEBs, the overall emissions
levels in 2005, taking into account
growth through 2005, were less than or
equal to the levels of emissions assumed
in the photochemical grid modeling. In
the TSD for the December 16, 1999 NPR
we noted that the photochemical grid
modeling performed for the area had
assumed local emissions levels of 360
TPD of VOC emissions and over 500
TPD of NOX emissions.40 These were
the local emissions levels the 1998 SIP
revisions projected the Washington area
would have by 1999. The pre-2001 SIP
revisions’ attainment plans were
submitted to fulfill these and other
prerequisites for approval proposed in
39 The ‘‘1998 SIP revisions’’ are those submittals
listed in Table 3 of this document which were
submitted during calendar year 1998.
40 ‘‘Technical Support Document for the OneHour Ozone Attainment Demonstrations submitted
by the State of Maryland, Commonwealth of
Virginia and the District of Columbia for the
Metropolitan Washington, DC Ozone
Nonattainment Area (DC039–2019, VA090–5036,
MD073–3045),’’ dated November 30, 1999. See also,
‘‘Technical Support Document for Approval and
Promulgation of Air Quality Implementation Plans;
District of Columbia, Maryland, and Virginia; Post1996 Rate-of-Progress Plan, Contingency Measures,
Transportation Control Measures, 1990 Base Year
Inventory Changes, and VMT Offset SIP for the
Metropolitan Washington, DC Nonattainment
Area,’’ dated January 5, 2005.
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the December 16, 1999 NPR. On January
3, 2001, we approved the pre-2001 SIP
revisions’ attainment plans.41 In the
TSD for that rulemaking, we concluded
that the creditable measures upon
which the pre-2001 SIP revisions’
attainment plan relied were projected to
achieve emissions levels of 356.7 TPD of
VOC emissions and 403 TPD of NOX
emissions.42 The pre-2001 SIP revisions’
attainment plan contained MVEBs of
101.8 TPD of VOC emissions and 161.8
TPD of NOX emissions. See 66 FR at
590, January 3, 2001. The pre-2001 SIP
revisions’ attainment plans were later
conditionally approved on April 17,
2004, 68 FR 19106, one condition of the
approval being that the States revise the
budgets using the MOBILE6 model and
revise, as necessary, the attainment
modeling and/or WOE demonstration to
show that the SIP continues to
demonstrate attainment by November
15, 2005. In the TSD prepared for this
final rule, EPA concluded that even
with the higher MVEBs the SIP
contained sufficient creditable measures
applying to all source categories to
achieve overall emissions levels in the
Washington area of 331 TPD of VOC and
491 TPD of NOX.43 Even though the
February 2004 SIP revisions contained
the higher, 234.7 TPD of NOX MVEBs
(and lower motor vehicle VOC
emissions budgets of 97.4 TPD) than the
pre-2001 SIP revisions’ attainment plan
(101.8 TPD for VOC and 161.8 TPD for
NOX), the overall emissions levels from
all sources of 331 TPD of VOC and 491
TPD of NOX are still less than the levels
used in the photochemical grid
modeling. Because the overall VOC and
NOX emissions are less than both the
360 TPD of VOC and over 500 TPD of
NOX used in the photochemical grid
modeling, EPA concludes that the 70
ton increase in the NOX MVEB will not
adversely impact the Washington area’s
41 That rule was vacated by the Court of Appeals
for reasons unrelated to the adequacy of the
modeled demonstration of attainment. See Sierra
Club v. Whitman, 294 F.3d at 163.
42 Table II—Summary of Creditable Measures in
‘‘Supplement to Technical Support Document for
the One-Hour Ozone Attainment Demonstrations,
Attainment Date Extension and Post-1996 Rate-ofProgress Plans submitted by the State of Maryland,
Commonwealth of Virginia and the District of
Columbia for the Metropolitan Washington, DC
Ozone Nonattainment Area and Commitment to
Revise Motor Vehicle Budgets for the Metropolitan
Washington, DC Ozone Nonattainment Area (DC–
2025, VA–5052, MD–3064),’’ dated December 15,
2000.
43 Table IV. F–1 Relative Reductions on page A–
27 of ‘‘Technical Support Document for Approval
and Promulgation of Air Quality Implementation
Plans; District of Columbia, Maryland, and Virginia;
Attainment Demonstration for the Metropolitan
Washington, DC Nonattainment Area,’’ dated
January 31, 2005.
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ability to timely attain the one-hour
ozone NAAQS.
Comment: We received a comment
claiming that EPA cannot approve the
MVEBs in the attainment plan because
the attainment plan is based on a
‘‘flawed WOE analysis’’ and relies on an
outdated photochemical model and thus
the modeled demonstration of
attainment does not accurately identify
the mobile source budgets required to
ensure timely attainment.
Response: EPA disagrees with the
comment. As explained elsewhere in
the response to comments portion of
this document, EPA believes that the
both WOE analysis and the
photochemical grid model upon which
the States relied meets the requirements
of the Act, and EPA’s regulations and
guidance. Therefore, EPA believes that
the MVEBs consistent with the
attainment modeling would not be
defective based upon any alleged
defects in the modeling.
Comment: We received a comment
asserting that the photochemical
modeling runs for the modeled
demonstration of attainment assumed
motor vehicle NOX emissions of 161.8
tons per day instead of the motor
vehicle NOX emissions budgets of 234.7
tons per day in the attainment plan. The
comment states that because EPA has
found that emissions projections
determined using MOBILE6 are more
accurate than the MOBILE5 values
relied on in the photochemical grid
modeling runs the States should have
rerun the photochemical grid model
with the MOBILE6 values. The
comment contends that the
demonstration of attainment is flawed
because the demonstration assumes that
2005 ozone levels will be no different
even though NOX emissions will be
more than 72 tons per day higher than
assumed in the photochemical grid
modeling runs and that because this
conclusion of no increase in 2005 ozone
levels is based not on photochemical
grid modeling, but on the conclusion
that ozone levels in 2005 will be
determined not by actual 2005 emission
levels but by the relative reduction in
emissions between the baseline and
2005. The comment claims that this
assumption is invalid because ozone
levels do not respond in linear fashion
to emission changes and claim that EPA
does not demonstrate, with
photochemical grid modeling as
required by the Act, how it can assure
attainment in 2005 with such a major
increase in allowable motor vehicle
emissions. The comment further alleges
that this approach would allow any
absolute increase in projected 2005
emissions over the level used in the
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photochemical grid modeling, as long as
the ‘‘relative increase over baseline
emissions is the same or less.’’
Response: EPA disagrees with the
comment because the comment assume
that in this case the overall emissions
levels in the Washington area in 2005
will be higher than those assumed in the
photochemical grid modeling for the
attainment year because the MVEB for
NOX will be higher.
We have noted previously that the
photochemical grid modeling performed
for the area had assumed local
emissions levels of 360 TPD of VOC
emissions and over 500 TPD of NOX
emissions in the attainment year. In the
TSD prepared for the February 9, 2005
NPR (which is the notice of proposed
rulemaking published for this final
rule), EPA concluded that even with the
higher MVEBs the SIP would contain
sufficient creditable measures
applicable to all source categories to
achieve emissions levels in the
Washington area of 331 TPD of VOC and
491 TPD of NOX.44 Even though the
February 2004 SIP revisions contained
the higher 234.7 TPD NOX, MVEB (and
a lower VOC MVEB of 97.4 TPD) than
the pre-2001 SIP revisions’ attainment
plan (101.8 TPD for VOC and 161.8 TPD
for NOX), the overall emissions levels of
331 TPD of VOC and 491 TPD of NOX
are still less than the levels assumed in
the photochemical grid modeling.
Therefore in the attainment year,
notwithstanding an increase in mobile
source NOX emissions, there is a
decrease in overall emissions in the
attainment year, not an increase as
implied by the commenter.
The comment that EPA’s policy
would allow any absolute increase in
projected 2005 emissions over the level
used in the photochemical grid
modeling, as long as the ‘‘relative
increase over baseline emissions is the
same or less,’’ is irrelevant because as
discussed in the preceding paragraph
the overall emissions levels for the
Washington area in 2005 are projected
to be less than the overall levels
assumed in the photochemical grid
modeling used in the demonstration of
attainment. That is, the February 2004
SIP revisions achieve emissions levels
less than that assumed in the
photochemical grid modeling for the
attainment year and a greater relative
emissions reduction between the 1990
baseline and 2005 attainment year. The
44 Table IV. F–1 Relative Reductions on page A–
27 of ‘‘Technical Support Document for Approval
and Promulgation of Air Quality Implementation
Plans; District of Columbia, Maryland, and Virginia;
Attainment Demonstration for the Metropolitan
Washington, DC Nonattainment Area,’’ dated
January 31, 2005.
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photochemical grid modeling for the
Washington area shows that VOC and
NOX reductions, along or in
combination, that go beyond those
assumed in the attainment year will
result in additional reduction in ozone
concentrations. While ozone may not
respond linearly to reductions, the
photochemical grid modeling for this
area indicates that ozone concentration
does respond directionally to a
reduction in ozone precursors (a
decrease in the ozone precursors VOC
and NOX will result in a decrease, not
an increase in ozone concentration,
albeit not necessarily a proportional
decrease). Therefore the demonstration
that this SIP will result in emissions
levels of ozone precursors at levels less
than that assumed in the photochemical
grid modeling for the attainment year,
along with a showing of a greater
relative emissions reduction, only adds
to the WOE that attainment is
demonstrated.
EPA also believes that an upward
revision of the MVEBs, which is more
than offset by other emissions
reductions from other source categories,
does not mandate a new photochemical
grid modeling demonstration. EPA
believes that, if an ozone attainment
plan relied on changes in emissions
from the base year to an attainment or
maintenance year inventory to estimate
via photochemical grid modeling the
relative changes in monitored ozone
levels, that the attainment plan SIP
revision with revised MVEBs continues
to demonstrate attainment of the ozone
NAAQS showing that the relative
emission reductions between the base
year and the attainment are the same or
greater using MOBILE6 than they were
using MOBILE5, and that projected
emissions levels for the attainment year
are lower than those assumed in the
modeling demonstration. The
Washington area attainment plan relies
upon the use of the photochemical
modeling results in a relative manner,
and, the attainment plan shows a greater
relative emission reduction with the
MOBILE6-based base year and
attainment year MVEBs. See, Joint
Memorandum dated January 18, 2002,
From John S. Seitz, Director, Office of
Air Quality Planning & Standards, and
Margo Tsirigotis Oge, Director of Office
of Transportation and Air Quality,
‘‘Policy Guidance for the Use of
MOBILE6 in SIP Development and
Transportation Conformity.’’ EPA has
reasonably interpreted the Act not to
require new photochemical grid
modeling for every revision of a SIP.
While section 182(c)(2)(A) requires
demonstrations of attainment for serious
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and above areas be based upon
photochemical grid modeling (or
something equivalent), the Act only
establishes a time frame for the initial
submittal of the attainment
demonstration and does not explicitly
require new modeling in connection
with every SIP revision. The Act simply
requires that the demonstration of
attainment be based upon
photochemical grid modeling and
demonstrate attainment of the ozone
NAAQS. See 1000 Friends of Maryland
v. Browner, 265 F.3d 216 (4th Cir. 2001)
(‘‘Nothing in [section 182(c)(2)(A)]
prohibits the use of previously
performed modeling if that modeling
can show that the plan as revised will
allow the area to reach attainment’’).
Comment: We received a comment
asserting that photochemical grid
modeling runs and WOE analysis relied
on by EPA in its 2001 approval of the
attainment plan assumed that motor
vehicle NOX emissions would be 161.8
tons per day and that neither EPA nor
the States ever proclaimed that were any
surplus emission reductions under that
scenario. The comment contends that
the photochemical grid modeling runs
showed continued nonattainment even
with motor vehicle emissions at that
level and therefore EPA cannot find that
motor vehicle NOX emissions more than
72 tons per day higher than those
assumed in the photochemical grid
modeling runs are consistent with
timely attainment.
Response: As discussed elsewhere in
this document in section IV. A.
‘‘Comment on the Attainment
Demonstration Modeling,’’ EPA
disagrees that the photochemical grid
modeling runs showed continued
nonattainment even with motor vehicle
NOX emissions at 161.8 TPD. This issue
has previously been litigated by the
commenter and conclusively decided in
EPA’s favor. See Sierra Club v. EPA, 356
F.3d at 304–307. As noted in our
response to previous comments on the
MVEBs, EPA has concluded that the
MVEBs must be analyzed in the context
of the entire SIP, and in that context
EPA even with the higher MVEBs the
SIP contains sufficient creditable
measures applicable to all source
categories to achieve overall emissions
levels consistent with attainment in a
demonstration based on the submitted
photochemical grid modeling.
C. Comment on the ROP Plans and NOX
Substitution
Comment: We received a comment
asserting the ROP plans do not meet the
requirements to demonstrate a nine
percent reduction in VOC emissions
from 1999 to 2002 and a further nine
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25713
percent from 2002 to 2005 because the
NOX substitution in the ROP plans is
impermissible. The comment asserts
that the plan does not meet section
182(c)(2)(c) of the Act because the plan
does not show that a nine percent
reduction in NOX emissions will result
in the same reduction in ozone
concentration as a nine percent
reduction in VOC emissions. The
comment asserts that EPA’s reliance on
our December 1993 NOX Substitution
Guidance is flawed because the plain
language of the Act requires proof of
actual equivalent benefits of NOX
substitution.
The comment also asserts that
because the ROP plans for each of the
1999 to 2005 periods rely solely upon
NOX reductions the plans do not meet
the requirement of section 182(c)(2)(C)
because the plan does not provide for
some percentage of VOC reduction
during each period. The comment
claims that the Act requires some nonzero percentage reduction in VOC
emissions for any ROP period. Finally,
the comment asserts that the Act
requires the ROP plan to have VOC
reductions by November 15, 2002 to
prevent a net increase in VOC emissions
by the 2002 milestone date, which
would offset the progress achieved by
the nine percent NOX reductions. The
comment notes that the plan provides
for such reductions but asserts that EPA
cannot approve the ROP plans because
the plan does not provide for all of these
reductions by the 2002 milestone date.
Response: EPA disagrees with the
comment and incorporates by reference
the response found in section III. A.
‘‘Comment on the ROP plans and NOX
Substitution’’ of this document.
D. Comment on the Transportation
Demand Model (TDM) Used in the Plans
Comment: We received a comment
asserting that the TDM used to project
the mobile source emissions does not
properly predict traffic volumes in the
Washington area on roadways. The
comment alleges that the inaccuracies
are significant enough that the results
cannot form a basis for predicting future
motor vehicle emissions or the emission
cuts needed to demonstrate attainment
of the 1-hour ozone NAAQS by
November 15, 2005.
Response: EPA disagrees with the
comment and incorporates by reference
the response found in section III. B.
‘‘Comment on the Transportation
Demand Model (TDM) Used in the
plans’’ of the this document.
E. Comment on the VMT Offset SIP
Comment: We received a comment
asserting that the SIP revisions are
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deficient because they do not contain
sufficient transportation control
measures (TCMs) to offset growth in
emissions from growth in vehicle miles
traveled (VMT) or in trip numbers. The
comment alleges that the Act requires
that the SIP offset any growth in
emissions due to growth in VMT or in
trip numbers not a showing that overall
motor vehicle emissions are expected to
decline.
Response: EPA disagrees with the
comment and incorporates by reference
the response found in section III. C.
‘‘Comment on the VMT Offset SIP’’ of
this document.
F. Comment on the Contingency
Measures Plans
Comment 1: We received a comment
asserting that EPA cannot approve the
contingency measures which were
identified in the SIP revisions to address
the Washington area’s failure to attain
by November 15, 1999. The comment
claims that, because these measures in
the plan required further action by the
States, these contingency measures do
not meet the CAA’s requirement that the
measures take effect without further
action by the State or EPA after the
failure to attain. The comment also
claims the contingency measures do not
meet EPA’s own guidance which
requires contingency measures to
achieve reductions no later than the
year after the one in which the failure
is identified because these contingency
measures identified by the SIP revision
were not implemented until 5 to 6 years
after the failure to attain.
Response 1: EPA disagrees with the
comment and incorporates by reference
the response to the comment labeled
‘‘comment 1’’ found in section III. D.
‘‘Comment on the Contingency
Measures Plans’’ of this document.
Comment 2: We received a comment
asserting that the contingency plan for
2005 cannot rely on measures already
adopted and in place or to be in place
before the 2005 attainment and ROP
deadline. The comment claims that the
Act requires that contingency measures
must be additional measures that will be
triggered by the attainment or milestone
failure, that is, the Act provision is
prospective, not retrospective.
Response 2: EPA disagrees with the
comment and incorporates by reference
the response to the comment labeled
‘‘comment 2’’ found in section III. D.
‘‘Comment on the Contingency
Measures Plans’’ of this document.
Comment 3: We received a comment
that the Act requires a set of
contingency measures to address any
failure to meet ROP requirements for the
2002–2005 period, that is separate from
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those required for failure to attain. The
comment claims that the requirement
for contingency measures to address
post-1996 milestone failures is
explicitly set out in the Act as an
additional mandate in addition to the
requirement for contingency measures
to address attainment failures. The
comment further claims that the 2005
ROP deadline here could precede the
attainment date if, in the case of an area
which qualifies for one or both of the 1year attainment date extensions allowed
by the Act.
Response 3: EPA disagrees with the
comment and incorporates by reference
the response to the comment labeled
‘‘comment 3’’ found in section III. D.
‘‘Comment on the Contingency
Measures Plans’’ of this document.
Comment 4: We received a comment
asserting that the contingency plan does
not meet EPA’s guidance because the
plan does not contain a commitment for
timely adoption of additional measures
if the 3 percent contingency plan is not
adequate to correct a failure to attain or
achieve an ROP milestone.
Response 4: EPA disagrees with the
comment and incorporates by reference
the response to the comment labeled
‘‘comment 4’’ found in section III. D.
‘‘Comment on the Contingency
Measures Plans’’ of this document.
Comment 5: We received a comment
asserting that the contingency plan must
contain some NOX reductions since the
ROP and attainment plans rely upon
NOX reductions as well as VOC
reductions.
Response 5: EPA disagrees with the
comment and incorporates by reference
the response to the comment labeled
‘‘comment 5’’ found in section III. D.
‘‘Comment on the Contingency
Measures Plans’’ of this document.
Comment 6: We received a comment
alleging that all of the emission
reductions from the continency
measures are not ‘‘surplus’’ because
neither EPA nor the States have
quantified the total VOC and NOX
reductions needed to attain by
November 15, 2005. The comment
further claims that the use of a WOE
approach in the modeled demonstration
of attainment is incapable of identifying
the precise level of emission reductions
needed for attainment and thus does not
support the a claim that there are
‘‘surplus’’ reductions in the SIP that can
be used for ‘‘contingency’’ purposes.
Response 6: EPA disagrees with the
comment and incorporates by reference
the response to the comment labeled
‘‘comment 6’’ found in section III. D.
‘‘Comment on the Contingency
Measures Plans’’ of this document.
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Comment 7: We received a comment
asserting that the SIP cannot rely on the
reformulated gasoline program (RFG
program) as a ‘‘contingency’’ measure to
address the area’s failure to attain by
1999, because the RFG program became
mandated by the Act once the
Washington area missed the 1999
attainment deadline. The comment
claims that contingency measures are
measures in addition to those mandated
by the Act. The comment also claims
that RFG was never intended as a
contingency measure and, thus, contrary
to EPA’s assertion, it is hardly a
‘‘penalty’’ to the nonattainment area to
disallow contingency credit for a
measure that was never intended as a
contingency measure, and that was
implemented at a time when the area
was already years behind schedule in
adopting adequate ROP and attainment
plans. The comment further asserts that
if the RFG program is a permissible
contingency measure the agency’s
guidance would obligate the states to
‘‘backfill’’ the measure with one year
assuring equivalent reductions and that
the states have not done so.
Response 7: EPA incorporates by
reference the response to the comment
labeled ‘‘comment 7’’ found in section
III. D. ‘‘Comment on the Contingency
Measures Plans’’ of this document.
G. Comment on Protective Finding
We also received comment adverse to
issuing a protective finding in concert
with a disapproval of the Maryland
attainment plan. Because we are not
issuing a protective finding in this final
rule, we do not address this comment in
this document. Our response to these
comment adverse to issuing a protective
finding are addressed in the final rule
disapproving Maryland’s attainment
plan with a protective finding that is
published elsewhere in today’s Federal
Register.
V. Other Matters
In 1995, Virginia adopted legislation
that provides, subject to certain
conditions, for an environmental
assessment (audit) ‘‘privilege’’ for
voluntary compliance evaluations
performed by a regulated entity. The
legislation further addresses the relative
burden of proof for parties either
asserting the privilege or seeking
disclosure of documents for which the
privilege is claimed. Virginia’s
legislation also provides, subject to
certain conditions, for a penalty waiver
for violations of environmental laws
when a regulated entity discovers such
violations pursuant to a voluntary
compliance evaluation and voluntarily
discloses such violations to the
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Commonwealth and takes prompt and
appropriate measures to remedy the
violations. Virginia’s Voluntary
Environmental Assessment Privilege
Law, Va. Code Sec. 10.1–1198, provides
a privilege that protects from disclosure
documents and information about the
content of those documents that are the
product of a voluntary environmental
assessment. The Privilege Law does not
extend to documents or information (1)
that are generated or developed before
the commencement of a voluntary
environmental assessment; (2) that are
prepared independently of the
assessment process; (3) that demonstrate
a clear, imminent and substantial
danger to the public health or
environment; or (4) that are required by
law.
On January 12, 1998, the
Commonwealth of Virginia Office of the
Attorney General provided a legal
opinion that states that the Privilege
law, Va. Code Sec. 10.1–1198, precludes
granting a privilege to documents and
information ‘‘required by law,’’
including documents and information
‘‘required by Federal law to maintain
program delegation, authorization or
approval,’’ since Virginia must ‘‘enforce
Federally authorized environmental
programs in a manner that is no less
stringent than their Federal
counterparts. * * * ’’ The opinion
concludes that ‘‘[r]egarding [section]
10.1–1198, therefore, documents or
other information needed for civil or
criminal enforcement under one of these
programs could not be privileged
because such documents and
information are essential to pursuing
enforcement in a manner required by
Federal law to maintain program
delegation, authorization or approval.’’
Virginia’s Immunity law, Va. Code
Sec. 10.1–1199, provides that ‘‘[t]o the
extent consistent with requirements
imposed by Federal law,’’ any person
making a voluntary disclosure of
information to a state agency regarding
a violation of an environmental statute,
regulation, permit, or administrative
order is granted immunity from
administrative or civil penalty. The
Attorney General’s January 12, 1998
opinion states that the quoted language
renders this statute inapplicable to
enforcement of any Federally authorized
programs, since ‘‘no immunity could be
afforded from administrative, civil, or
criminal penalties because granting
such immunity would not be consistent
with Federal law, which is one of the
criteria for immunity.’’
Therefore, EPA has determined that
Virginia’s Privilege and Immunity
statutes will not preclude the
Commonwealth from enforcing its
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program consistent with the Federal
requirements. In any event, because
EPA has also determined that a state
audit privilege and immunity law can
affect only state enforcement and cannot
have any impact on Federal
enforcement authorities, EPA may at
any time invoke its authority under the
Clean Air Act, including, for example,
sections 113, 167, 205, 211 or 213, to
enforce the requirements or prohibitions
of the state plan, independently of any
state enforcement effort. In addition,
citizen enforcement under section 304
of the Clean Air Act is likewise
unaffected by this, or any, state audit
privilege or immunity law.
VI. Final Actions
A. The District of Columbia—1996–1999
ROP Plan
EPA is approving as a revision to the
District’s SIP the District of Columbia’s
1996–1999 ROP plan SIP revision for
the Washington area which was
submitted on November 3, 1997, as
supplemented on May 25, 1999. EPA is
approving the 1999 MVEBs of 128.5
tons per day of VOC and 196.4 tons per
day of NOX established and identified in
the Post 1996–1999 ROP plan.
25715
E. The District of Columbia—
Contingency Measure Plan
EPA is approving as a revision to the
District’s SIP the District of Columbia’s
contingency measure plan SIP revision
for the Washington area which was
submitted on September 5, 2003, as
supplemented on February 25, 2004.
F. The District of Columbia—
Attainment Demonstration and Plan
EPA is approving as a revision to the
District’s SIP the modeled
demonstration of attainment and
adjunct WOE analyses that the
Washington area will attain the 1-hour
ozone NAAQS by November 15, 2005
and the District’s 1-hour ozone
attainment plan for the Washington area
both of which were submitted on
September 5, 2003 as supplemented on
February 25, 2004. EPA is approving the
2005 MVEBs of 97.4 tons per day for
VOC and 234.7 tons per day of NOX
established and identified in the
attainment plan.
G. Maryland—Post 1996–1999 Rate-ofProgress Plan and TCMs
EPA is approving as a revision to the
District’s SIP the revision to the 1990
Base Year Emissions Inventory
submitted by the District of Columbia
on September 5, 2003 as supplemented
on February 25, 2004.
EPA is approving as a revision to the
State of Maryland’s SIP Maryland’s post
1996–1999 ROP plan SIP revision for
the Washington area which was
submitted on December 24, 1997, as
supplemented on May 20, 1999, and the
TCMs in Appendix H of the May 20,
1999 submittal. EPA is approving the
1999 MVEBs of 128.5 tons per day of
VOC and 196.4 tons per day of NOX
established and identified in the Post
1996–1999 ROP plan.
C. The District of Columbia—Post 1999–
2005 Rate-of-Progress Plan and TCMs
H. Maryland—1990 Base Year Inventory
Revisions
EPA is approving as a revision to the
District’s SIP the District of Columbia’s
post 1999–2005 ROP plan SIP revision
for the Washington area which was
submitted on September 5, 2003 as
supplemented on February 25, 2004 and
the TCMs in Appendix J of the February
25, 2004 submittal. EPA is approving
the 2002 MVEBs of 125.2 tons per day
for VOC and 290.3 tons per day of NOX
and the 2005 MVEBs of 97.4 tons per
day for VOC and 234.7 tons per day of
NOX established and identified in the
Post 1999–2005 ROP Plan.
EPA is approving as a revision to the
State of Maryland’s SIP the revision to
the 1990 Base Year Emissions Inventory
submitted by Maryland on September 2,
2003 as supplemented on February 24,
2004.
B. The District of Columbia—1990 Base
Year Inventory Revisions
D. The District of Columbia—VMT
Offset SIP
EPA is approving as a revision to the
District’s SIP the District of Columbia
VMT Offset SIP revision for the
Washington area which was submitted
on September 5, 2003, as supplemented
on February 25, 2004.
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I. Maryland—Post 1999–2005 Rate-ofProgress Plan and TCMs
EPA is approving as a revision to the
State of Maryland’s SIP Maryland’s post
1999–2005 ROP plan SIP revision for
the Washington area which was
submitted on September 2, 2003 as
supplemented on February 24, 2004 and
the TCMs in Appendix J of the February
24, 2004 submittal. EPA is approving
the 2002 MVEBs of 125.2 tons per day
for VOC and 290.3 tons per day of NOX
and the 2005 MVEBs of 97.4 tons per
day for VOC and 234.7 tons per day of
NOX established and identified in the
Post 1999–2005 ROP Plan.
E:\FR\FM\13MYR5.SGM
13MYR5
25716
Federal Register / Vol. 70, No. 92 / Friday, May 13, 2005 / Rules and Regulations
J. Maryland—VMT Offset SIP
EPA is approving as a revision to the
State of Maryland’s SIP Maryland’s
VMT Offset SIP revision for the
Washington area which was submitted
on September 2, 2003 as supplemented
on February 24, 2004
K. Maryland—Contingency Measure
Plan
EPA is approving as a revision to the
State of Maryland’s SIP Maryland’s
contingency measure plan SIP revision
for the Washington area which was
submitted on September 3, 2003, as
supplemented on February 24, 2004.
L. Maryland—Modeled Demonstration
of Attainment and Determination That
Maryland’s Submitted SIP Contains
Measures That Fully Satisfy the
Emission Reduction Requirements
Relevant to Attainment
EPA is approving as a revision to the
State of Maryland’s SIP the modeled
demonstration of attainment and
adjunct WOE analyses that the
Washington area will attain the 1-hour
ozone NAAQS by November 15, 2005,
which was submitted on September 2,
2003 as supplemented on February 24,
2004. EPA is issuing a determination
that Maryland’s submitted SIP for the
Washington area contains adopted
control measures that fully satisfy the
emission reduction requirements
relevant to attainment of the 1-hour
ozone NAAQS in the Washington area
by November 15, 2005.
M. Virginia—Post 1996–1999 Rate-ofProgress Plan and TCMs
EPA is approving as a revision to the
Commonwealth of Virginia’s SIP
Virginia’s post 1996–1999 ROP plan SIP
revision for the Washington area which
was submitted on December 29, 1997, as
supplemented on May 25, 1999, and the
TCMs in Appendix H of the May 25,
1999 submittal. EPA is approving the
1999 MVEBs of 128.5 tons per day of
VOC and 196.4 tons per day of NOX
established and identified in the Post
1996–1999 ROP plan.
N. Virginia—1990 Base Year Inventory
Revisions
EPA is approving as a revision to the
Commonwealth of Virginia’s SIP
Virginia’s revision to the 1990 Base Year
Emissions Inventory which was
submitted on August 19, 2003 as
supplemented on February 25, 2004.
O. Virginia—Post 1999–2005 Rate-ofProgress Plan and TCMs
EPA is approving as a revision to the
Commonwealth of Virginia’s SIP
Virginia’s post 1999–2005 ROP plan SIP
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19:27 May 12, 2005
Jkt 205001
revision for the Washington area which
was submitted on August 19, 2003 as
supplemented on February 25, 2004 and
the TCMs in Appendix J of the February
25, 2004 submittal. EPA is approving
the 2002 MVEBs of 125.2 tons per day
for VOC and 290.3 tons per day of NOX
and the 2005 MVEBs of 97.4 tons per
day for VOC and 234.7 tons per day of
NOX established and identified in the
Post 1999–2005 ROP Plan.
P. Virginia—VMT Offset SIP
EPA is approving as a revision to the
Commonwealth of Virginia’s SIP
Virginia’s VMT Offset SIP revision for
the Washington area which was
submitted on August 19, 2003, as
supplemented on February 25, 2004.
Q. Virginia—Contingency Measure Plan
EPA is approving as a revision to the
Commonwealth of Virginia’s SIP
Virginia’s contingency measure plan SIP
revision for the Washington area which
was submitted on August 19, 2003, as
supplemented on February 25, 2004.
R. Virginia—Attainment Demonstration
and Plan
EPA is approving as a revision to the
Commonwealth of Virginia’s SIP the
modeled demonstration of attainment
and adjunct WOE analyses that the
Washington area will attain the 1-hour
ozone NAAQS by November 15, 2005
and Virginia’s SIP Virginia’s 1-hour
ozone attainment plan for the
Washington area both of which were
submitted on August 19, 2003 as
supplemented on February 25, 2004.
EPA is approving the 2005 MVEBs of
97.4 tons per day for VOC and 234.7
tons per day of NOX established and
identified in the attainment plan.
VII. Statutory and Executive Order
Reviews
A. General Requirements
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this action is
not a ‘‘significant regulatory action’’ and
therefore is not subject to review by the
Office of Management and Budget. For
this reason, this action is also not
subject to Executive Order 13211,
‘‘Actions Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355, May
22, 2001). This action merely approves
state law as meeting Federal
requirements and imposes no additional
requirements beyond those imposed by
state law. Accordingly, the
Administrator certifies that this rule
will not have a significant economic
impact on a substantial number of small
entities under the Regulatory Flexibility
Act (5 U.S.C. 601 et seq.). Because this
PO 00000
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Fmt 4701
Sfmt 4700
rule approves pre-existing requirements
under state law and does not impose
any additional enforceable duty beyond
that required by state law, it does not
contain any unfunded mandate or
significantly or uniquely affect small
governments, as described in the
Unfunded Mandates Reform Act of 1995
(Pub. L. 104–4). This rule also does not
have tribal implications because it will
not have a substantial direct effect on
one or more Indian tribes, on the
relationship between the Federal
Government and Indian tribes, or on the
distribution of power and
responsibilities between the Federal
Government and Indian tribes, as
specified by Executive Order 13175 (65
FR 67249, November 9, 2000). This
action also does not have Federalism
implications because it does not have
substantial direct effects on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132 (64 FR 43255,
August 10, 1999). This action merely
approves a state rule implementing a
Federal requirement, and does not alter
the relationship or the distribution of
power and responsibilities established
in the Clean Air Act. This rule also is
not subject to Executive Order 13045
‘‘Protection of Children from
Environmental Health Risks and Safety
Risks’’ (62 FR 19885, April 23, 1997),
because it is not economically
significant.
In reviewing SIP submissions, EPA’s
role is to approve state choices,
provided that they meet the criteria of
the Clean Air Act. In this context, in the
absence of a prior existing requirement
for the State to use voluntary consensus
standards (VCS), EPA has no authority
to disapprove a SIP submission for
failure to use VCS. It would thus be
inconsistent with applicable law for
EPA, when it reviews a SIP submission,
to use VCS in place of a SIP submission
that otherwise satisfies the provisions of
the Clean Air Act. Thus, the
requirements of section 12(d) of the
National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note) do not apply. This rule does
not impose an information collection
burden under the provisions of the
Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.).
B. Submission to Congress and the
Comptroller General
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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Federal Register / Vol. 70, No. 92 / Friday, May 13, 2005 / Rules and Regulations
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. This rule is not a
‘‘major rule’’ as defined by 5 U.S.C.
804(2).
C. Petitions for Judicial Review
Under section 307(b)(1) of the Clean
Air Act, petitions for judicial review of
this action must be filed in the United
States Court of Appeals for the
appropriate circuit by July 12, 2005.
Filing a petition for reconsideration by
the Administrator of this final rule does
not affect the finality of this rule for the
purposes of judicial review nor does it
extend the time within which a petition
for judicial review may be filed, and
shall not postpone the effectiveness of
Name of non-regulatory SIP
revision
such rule or action. This action to
approve the District’s and Virginia’s
base year inventory revision, ROP, VMT
Offset, contingency measure and
attainment plans, MVEBs and TCMs,
Maryland’s base year inventory revision,
TCMs, and ROP, VMT Offset and
contingency measure plan, and
Maryland’s modeled demonstration of
attainment and demonstration that its
submitted SIP for the Washington area
contains adopted control measures that
fully satisfy the emissions reductions
requirements relevant to attainment of
the 1-hour ozone NAAQS may not be
challenged later in proceedings to
enforce its requirements. (See section
307(b)(2).)
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
relations, Nitrogen dioxide, Ozone,
Volatile organic compounds.
Dated: May 3, 2005.
Donald S. Welsh,
Regional Administrator, Region III.
I
State submittal
date
40 CFR part 52 is amended as follows:
PART 52—[AMENDED]
1. The authority citation for part 52
continues to read as follows:
I
Authority: 42 U.S.C. 7401 et seq.
Subpart J—District of Columbia
2. In § 52.470, the table in paragraph (e)
is amended by adding at the end of the
table, the entries for 1996–1999 Rate-ofProgress Plan, 1990 Base Year Inventory
Revisions, Post 1999–2005 Rate-ofProgress Plan and Transportation
Control Measures (TCMs) in Appendix J,
VMT Offset SIP, Contingency Measure
Plan and 1-hour Ozone Modeled
Demonstration of Attainment and
Attainment Plan to read as follows:
I
§ 52.470
*
Applicable geographic or nonattainment area
Identification of plan.
*
*
(e) * * *
*
1999 motor vehicle emissions
budgets of 128.5 tons per
day (tpy) of VOC and 196.4
tpy of NOX.
*
11/3/1997,
5/25/1999
*
*
5/13/05 ...................................
[Insert page number where
the document begins].
1990 Base Year inventory Revisions,.
Washington 1-hour ozone
nonattainment area.
9/5/2003,
2/25/2004
1999–2005 Rate-of-Progress
Plan SIP Revision and the
Transportation Control
Measures (TCMs) in Appendix J.
Washington 1-hour ozone
nonattainment area.
9/5/2003,
2/25/2004
5/13/05 ...................................
[Insert page number where
the document begins].
5/13/05 ...................................
[Insert page number where
the document begins].
VMT Offset SIP Revision ........
Washington 1-hour ozone
nonattainment area.
9/5/2003,
2/25/2004
Contingency Measure Plan ....
Washington 1-hour ozone
nonattainment area.
9/5/2003,
2/25/2004
1-hour Ozone Modeled Demonstration of Attainment and
Attainment Plan.
Washington 1-hour ozone
nonattainment area.
9/5/2003,
2/25/2004
5/13/05 ...................................
[Insert page number where
the document begins].
5/13/05 ...................................
[Insert page number where
the document begins].
5/13/05 ...................................
[Insert page number where
the document begins].
Control Measures (TCMs) in Appendix
H, 1990 Base Year Inventory Revisions,
Post 1999–2005 Rate-of-Progress Plan
I 3. In § 52.1070, the table in paragraph
and Transportation Control Measures
(e) is amended by adding at the end of
the table, the entries for 1996–1999 Rate- (TCMs) in Appendix J, VMT Offset SIP,
Contingency Measure Plan and Modeled
of-Progress Plan and Transportation
19:27 May 12, 2005
Jkt 205001
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*
Additional explanation
*
Washington 1-hour ozone
nonattainment.
VerDate jul<14>2003
*
EPA approval date
*
*
1996–1999 Rate-of-Progress
plan SIP.
Subpart V—Maryland
25717
Only the TCMs in Appendix J
of the 2/25/2004 revision,
2002 motor vehicle emissions budgets (MVEBs) of
125.2 tons per day (tpy) for
VOC and 290.3 tpy of NOX,
and, 2005 MvEBs of 97.4
tpy for VOC and 234.7 tpy
of NOX.
2005 motor vehicle emissions
budgets of 97.4 tons per
day (tpy) for VOC and
234.7 tpy of NOX.
Demonstration of Attainment to read as
follows:
§ 52.1070
*
Identification of plan.
*
*
(e)* * *
E:\FR\FM\13MYR5.SGM
13MYR5
*
*
25718
Federal Register / Vol. 70, No. 92 / Friday, May 13, 2005 / Rules and Regulations
Name of non-regulatory SIP
revision
Applicable geographic or nonattainment area
State submittal
date
*
*
*
1996–1999 Rate-of-Progress
Washington DC 1-hour ozone
Plan SIP and the Transpornonattainment area.
tation Control Measures
(TCMs) in Appendix H.
*
12/20/1997,
5/20/1999
1990 Base Year Inventory
Revisions.
Washington DC 1-hour ozone
nonattainment area.
9/2/2003,
2/24/2004
1999–2005 Rate-of-Progress
Plan SIP Revision and the
Transportation Control
Measures (TCMs) in Appendix J.
Washington DC 1-hour ozone
nonattainment area.
9/2/2003,
2/24/2004
VMT Offset SIP Revision .......
Washington DC 1-hour ozone
nonattainment area.
9/2/2003,
2/24/2004
Contingency Measure Plan ....
Washington, DC Area ............
9/2/2003,
2/24/2004
1-hour Ozone Modeled Demonstration of Attainment.
Washington DC 1-hour ozone
nonattainment area.
9/2/2003,
2/24/2004
EPA approval date
Additional explanation
*
*
*
5/13/05 ................................... Only the TCMs in Appendix H
[Insert page number where
of the 5/20/1999 revision,
the document begins].
1999 motor vehicle emissions budgets of 128.5 tons
per day (tpy) of VOC and
196.4 tpy of NOX.
5/13/05 ...................................
[Insert page number where
the document begins].
5/13/05 ................................... Only the TCMs in Appendix J
[Insert page number where
of the 2/24/2004 revision,
the document begins].
2002 motor vehicle emissions budgets (MVEBs) of
125.2 tons per day (tpy) for
VOC and 290.3 tpy of NOX,
and, 2005 MVEBs of 97.4
tpy for VOC and 234.7 tpy
of NOX.
5/13/05 ...................................
[Insert page number where
the document begins].
5/13/05 ...................................
[Insert page number where
the document begins].
5/13/05 ...................................
[Insert page number where
the document begins].
4. Section 52.1073 is revised by adding
paragraph (f) to read as follows:
ozone NAAQS in the Washington area
by November 15, 2005.
§ 52.1073
Subpart VV—Virginia
5. In § 52.2420, the table in paragraph
(e) is amended by adding at the end of
the table, the entries for 1996–1999 ROP
Plan and Transportation Control
Measures (TCMs) in Appendix H, 1990
Base Year Inventory Revisions, Post
1999–2005 Rate-of-Progress Plan and
Transportation Control Measures (TCMs)
in Appendix J, VMT Offset SIP,
Contingency Measure Plan and 1-hour
Ozone Modeled Demonstration of
Attainment and Attainment Plan to read
as follows:
§ 52.2420
I
Approval status.
*
*
*
*
*
(f) EPA is issuing a determination that
Maryland’s submitted SIP for the
Washington area contains adopted
control measures that fully satisfy the
emission reduction requirements
relevant to attainment of the 1-hour
Name of non-regulatory SIP
revision
I
Applicable geographic or nonattainment area
State submittal
date
*
Identification of plan.
*
*
(e)* * *
EPA approval date
*
*
*
Washington 1-hour ozone
nonattainment area.
*
12/29/2003,
5/25/1999
*
*
*
5/13/05 ...................................
[Insert page number where
the document begins].
1990 Base Year Inventory Revisions.
Washington 1-hour ozone
nonattainment area.
8/19/2003,
2/25/2004
1999–2005 Rate-of-Progress
Plan SIP Revision and the
Transportation Control
Measures (TCMs) in Appendix J.
Washington 1-hour ozone
nonattainment area.
8/19/2003,
2/25/2004
5/13/05 ...................................
[Insert page number where
the document begins].
5/13/05 ...................................
[Insert page number where
the document begins].
VMT Offset SIP Revision ........
Washington 1-hour ozone
nonattainment area.
8/19/2003,
2/25/2004
1996–1999 Rate-of-Progress
Plan SIP and the Transportation Control Measures
(TCMs) in Appendix H.
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19:27 May 12, 2005
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5/13/05 ...................................
[Insert page number where
the document begins].
E:\FR\FM\13MYR5.SGM
13MYR5
*
*
Additional explanation
Only the TCMs in Appendix H
of the 5/25/1999 revision,
1999 motor vehicle emissions budgets of 128.5 tons
per day (tpy) of VOC and
196.4 tpy of NOX.
Only the TCMs in Appendix J
of the 2/25/2004 the revision, 2002 motor vehicle
emissions budgets
(MVEBs) of 125.2 tons per
day (tpy) for VOC and
290.3 tpy of NOX, and,
2005 MVEBs of 97.4 tpy for
VOC and 234.7 tpy of NOX.
Federal Register / Vol. 70, No. 92 / Friday, May 13, 2005 / Rules and Regulations
Name of non-regulatory SIP
revision
Applicable geographic or nonattainment area
State submittal
date
Contingency Measure Plan ....
Washington 1-hour ozone
nonattainment area.
8/19/2003,
2/25/2004
1-hour Ozone Modeled Demonstration of Attainment and
Attainment Plan.
Washington 1-hour ozone
nonattainment area.
8/19/2003,
2/25/2004
[FR Doc. 05–9401 Filed 5–12–05; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[RME No. R03–OAR–2004–DC–0010; FRL–
7910–4]
Approval and Promulgation of Air
Quality Implementation Plans;
Maryland; Metropolitan Washington
DC 1-Hour Ozone Attainment
Demonstration Plans
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: EPA is disapproving a State
Implementation Plan (SIP) revision
submitted by the State of Maryland, and
is issuing a protective finding for that
plan pursuant to EPA’s transportation
conformity rule. The intended effect of
this action is to disapprove Maryland’s
attainment plan for the Metropolitan
Washington, DC severe 1-hour ozone
nonattainment area (the Washington
area) and to issue a protective finding
which allows the motor vehicle
emissions budgets identified in that
plan to be used in future conformity
determinations. This action allows
transportation planning activities,
including conformity analyses and
determinations, to continue normally
until such time as highway sanctions
would be imposed pursuant to the Clean
Air Act (the CAA or the Act) and EPA’s
order of sanctions rule.
DATES: Effective Date: This final rule is
effective on June 13, 2005.
ADDRESSES: EPA has established a
docket for this action under Regional
Material in EDocket (RME) ID Number
R03–OAR–2004–DC–0010. All
documents in the docket are listed in
the RME index at https://
www.docket.epa.gov/rmepub/. Once in
the system, select ‘‘quick search,’’ then
key in the appropriate RME
identification number. Although listed
in the electronic docket, some
information is not publicly available,
VerDate jul<14>2003
19:27 May 12, 2005
Jkt 205001
EPA approval date
5/13/05 ...................................
[Insert page number where
the document begins].
5/13/05 ...................................
[Insert page number where
the document begins].
i.e., confidential business information
(CBI) or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically in RME or
in hard copy for public inspection
during normal business hours at the Air
Protection Division, U.S. Environmental
Protection Agency, Region III, 1650
Arch Street, Philadelphia, Pennsylvania
19103. Copies of the State submittal are
available at the Maryland Department of
the Environment, 1800 Washington
Boulevard, Suite 705, Baltimore,
Maryland 21230.
FOR FURTHER INFORMATION CONTACT:
Christopher Cripps, (215) 814–2179, or
by e-mail at cripps.christopher@epa.gov.
SUPPLEMENTARY INFORMATION: In this
document any reference to ‘‘we’’ and
‘‘our’’ means EPA and EPA’s,
respectively.
I. Background
A. Summary
On February 9, 2005, (70 FR 6796),
EPA published a notice of proposed
rulemaking (NPR) for the State of
Maryland. In our February 9, 2005, NPR,
we proposed approval of an attainment
plan SIP revision submitted by the State
of Maryland for the Washington area
contingent upon the State submitting an
approvable SIP revision for certain
penalty fees, required by the Act, prior
to the time EPA issued a final rule on
Maryland’s attainment plan. In the
alternative, EPA proposed to disapprove
the attainment plan SIP revision
submitted by the State of Maryland for
the Washington area and to issue a
protective finding for the attainment
plan which would allow the use of the
motor vehicle emissions budgets (the
MVEBs) identified in the attainment
plan SIP to be used for demonstrating
conformity.
In the February 9, 2005, NPR, we also
proposed to approve attainment plan
SIP revisions for the Washington area
submitted by the Commonwealth of
Virginia and the District of Columbia
PO 00000
Frm 00033
Fmt 4701
Sfmt 4700
25719
Additional explanation
2005 motor vehicle emissions
budgets of 97.4 tons per
day (tpy) for VOC and
234.7 tpy of NOX.
(the District). EPA has taken final action
on the District’s and Virginia’s
attainment plans in a separate final rule
which is published elsewhere in today’s
Federal Register. In that same final rule
approving the District’s and Virginia’s
attainment plan for the Washington
area, we determine that the attainment
plan for Maryland contains adopted
control measures that fully satisfy the
emission reduction requirement
relevant to attainment of the 1-hour
ozone National Ambient Air Quality
Standard (NAAQS).
B. Relationship to Past SIP Revisions
and Litigation
1. Prior SIP Revisions
On April 29, 1998, Maryland
submitted an attainment plan for the
Washington area and supplemented
those submittals on August 17, 1998,
February 14, 2000 and March 31, 2000.
The April 29, 1998, August 17, 1998,
February 14, 2000 SIP revisions
cumulatively constituted the attainment
plan for the Washington area which, at
the time, was classified as a serious
nonattainment area for the 1-hour ozone
NAAQS. In the aggregate, these
attainment plans consisted of a
photochemical modeling demonstration
and adjunct weight of evidence analyses
to demonstrate attainment of the ozone
NAAQS, projected emissions
inventories showing that Maryland had
adopted sufficient measures to support
the demonstration of attainment,
attainment year MVEBs, and a
commitment to conduct and submit a
mid-course review to EPA by a date
certain. The March 31, 2000 SIP
revision consisted of a commitment to
revise the mobile vehicle emissions
budgets one-year after EPA released the
MOBILE6 model and MVEBs for years
after 2005 (outyear budgets). These
attainment plans were submitted to
demonstrate that the Washington area
would attain the 1-hour ozone NAAQS
by no later than November 15, 2005.
Hereafter these revisions will be called
the ‘‘pre-2001 SIP revisions’’ attainment
plan.’’ These are those SIP revisions
listed in Table 2 of a January 3, 2001
final rule (66 FR at 586) and those listed
E:\FR\FM\13MYR5.SGM
13MYR5
Agencies
[Federal Register Volume 70, Number 92 (Friday, May 13, 2005)]
[Rules and Regulations]
[Pages 25688-25719]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-9401]
[[Page 25687]]
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Part V
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 52
Approval and Promulgation of Air Quality Implementation Plans; Final
Rules
Federal Register / Vol. 70, No. 92 / Friday, May 13, 2005 / Rules and
Regulations
[[Page 25688]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[RME NO. R03-OAR-2004-DC-0009, R03-OAR-2004-DC-0010; FRL-7910-3]
Approval and Promulgation of Air Quality Implementation Plans;
District of Columbia, Maryland, Virginia; 1-Hour Ozone Attainment
Plans, Rate-of-Progress Plans, Contingency Measures, Transportation
Control Measures, VMT Offset, and 1990 Base Year Inventory
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is approving State Implementation Plan (SIP) revisions
submitted by the District of Columbia (the District), the State of
Maryland and the Commonwealth of Virginia. These revisions include the
1996-1999 and 1999-2005 rate-of-progress (ROP) plans, changes to the
1990 base year inventory, a contingency measures plan, certain
transportation control measures (TCMs), and a demonstration that each
SIP contains any necessary transportation control measures to offset
any growth in emissions from growth in vehicle miles traveled (VMT) and
to demonstrate ROP and attainment of the 1-hour national ambient air
quality standard (NAAQS) for ozone. These revisions also include the
District's and Virginia's attainment plan for the Washington, DC severe
1-hour ozone nonattainment area (the Washington area). The intended
effect of this action with respect to the following SIP revisions, all
of which were submitted to satisfy the SIP requirements of 1-hour ozone
nonattainment areas classified as severe, is to: approve the
District's, Maryland's and Virginia's modeling demonstration, which
includes the analysis based upon photochemical grid modeling, that the
Washington area will attain the 1-hour ozone NAAQS; approve the
District's, Maryland's and Virginia's post-1996 ROP plans, 1990 base
year inventory revisions, TCMs, VMT offset and contingency measures SIP
revisions; approve the District's and Virginia's attainment plans for
the Washington area; and, determine that Maryland's SIP for the
Washington area contains adopted control measures and determine that
these measures fully satisfy the emission reductions relevant to
attainment of the 1-hour ozone NAAQS.
DATES: Effective Date: This final rule is effective on June 13, 2005.
ADDRESSES: EPA has established a docket for this action under Regional
Material in EDocket (RME) ID Number R03-OAR-2004-DC-0010. All documents
in the docket are listed in the RME index at https://www.docket.epa.gov/
rmepub/. Once in the system, select ``quick search,'' then key in the
appropriate RME identification number. Although listed in the
electronic docket, some information is not publicly available, i.e.,
confidential business information (CBI) or other information whose
disclosure is restricted by statute. Certain other material, such as
copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically in RME or in hard copy
for public inspection during normal business hours at the Air
Protection Division, U.S. Environmental Protection Agency, Region III,
1650 Arch Street, Philadelphia, Pennsylvania 19103. Copies of the State
submittal are available at the District of Columbia Department of
Public Health, Air Quality Division, 51 N Street, NE., Washington, DC
20002; the Maryland Department of the Environment, 1800 Washington
Boulevard, Suite 705, Baltimore, Maryland 21230; and the Virginia
Department of Environmental Quality, 629 East Main Street, Richmond,
Virginia 23219.
FOR FURTHER INFORMATION CONTACT: Christopher Cripps, (215) 814-2179, or
by e-mail at cripps.christopher@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
A. Summary
On January 12, 2005 (70 FR 2085), EPA published a notice of
proposed rulemaking (NPR) for the District, the State of Maryland and
the Commonwealth of Virginia (the States). The NPR proposed approval of
the 1996-1999 and 1999-2005 ROP plans, changes to the 1990 base year
inventory, a contingency measures plan, certain TCMs, and a
demonstration that each SIP contains sufficient transportation control
measures to offset any growth in emissions from growth in VMT as
necessary to demonstrate ROP and attainment of the 1-hour NAAQS for
ozone.
Tables 1 and 2 identify the initial submittal dates and the dates
on which the States's submitted amendments for these plans and measures
covered by our January 12, 2005 NPR:
---------------------------------------------------------------------------
\1\ Maryland SIP revision submittals labeled as 97-04 and 99-12.
Table 1.--Post 1996-1999 ROP Plans From the States
----------------------------------------------------------------------------------------------------------------
DC MD \1\ VA
----------------------------------------------------------------------------------------------------------------
Initial submittal dates.............. November 10, 1997...... December 24, 1997...... December 19, 1997.
Amended submittal dates.............. May 25, 1999........... May 20, 1999........... May 25, 1999.
----------------------------------------------------------------------------------------------------------------
The post 1996-1999 ROP Plan SIP revisions also include certain
TCMs, specifically those TCMs identified in Appendix H of the States
submittals.
---------------------------------------------------------------------------
\2\ Maryland's identifiers for these SIP revision submittals are
SIP revisions numbers 03-05 and 04-01.
Table 2.--Attainment Plan, 1999-2005 ROP Plans, Contingency Measures Plan, Amendments to the 1990 Base Year
Inventory, and VMT Offset Plans
----------------------------------------------------------------------------------------------------------------
DC MD \2\ VA
----------------------------------------------------------------------------------------------------------------
Initial submittal dates.............. September 5, 2003...... September 2, 2003...... August 19, 2003.
Amended submittal dates.............. February 25, 2004...... February 24, 2004...... February 25, 2004.
----------------------------------------------------------------------------------------------------------------
[[Page 25689]]
Hereafter, the SIP revisions listed in Table 2 of this document
will be called the ``February 2004 SIP revisions.'' The States''
February 2004 SIP revisions include the post 1999-2005 ROP plans, the
VMT Offset SIPs, revisions to the 1990 base year emissions inventory,
and the contingency measures plans for ROP and attainment for the
Washington area.\3\ The February 2004 SIP revisions additionally
include certain TCMs, namely those TCMs identified in Appendix J of the
SIP revision submittals.
---------------------------------------------------------------------------
\3\ In this document a SIP revision which demonstrates the
state's SIP contains any necessary transportation control measures
to offset any growth in emissions from growth in VMT needed to
demonstrate ROP and attainment of the 1-hour NAAQS for ozone is
termed a ``VMT offset SIP.''
---------------------------------------------------------------------------
The February 2004 SIP revisions also included the States' revised
attainment plans for the Washington area. The States had initially
submitted an attainment plan for the Washington area in 1998 with later
supplements. These initial attainment plans were the subject of two
earlier rulemaking actions, 66 FR 586, January 3, 2001, and 68 FR
19106, April 17, 2003. The dates of submittal are shown in Table 3
which repeats the information found in Table 2 of both the January 3,
2001 and April 17, 2003 final rules.
Table 3.--Previous Attainment Demonstrations Submissions
----------------------------------------------------------------------------------------------------------------
DC MD \4\ VA
----------------------------------------------------------------------------------------------------------------
Initial submittal dates.............. April 24, 1998......... April 29, 1998......... April 29, 1998.
Amendment dates...................... October 27, 1998....... August 17, 1998........ August 18, 1998.
Supplemental dates................... February 16, 2000...... February 14, 2000...... February 9, 2000.
Supplemental dates................... March 22, 2000......... March 31, 2000......... March 31, 2000.
----------------------------------------------------------------------------------------------------------------
Hereafter those revisions listed in Table 3 will be called the
``pre-2001 SIP revisions'' attainment plan.'' \5\ Hereafter we refer to
the collective grouping of those SIP revisions listed in Tables 1 and 3
of this document as the ``pre-2001 SIP revisions.''
---------------------------------------------------------------------------
\4\ Maryland's identifiers for the February 14, 2000 and March
31, 2002 submittals are SIP revisions numbers 00-01 and No. 00-02.
\5\ Only a commitment to revise the motor vehicle emissions
budgets (MVEBs) found in the March 2000 SIP revisions listed in
Table 3 of this document were subject to the January 3, 2001 and
April 17, 2003 final rules. The portion of these SIP revisions
related to MVEBs for years after 2005 (``outyear budgets'') was not
subject to these actions.
---------------------------------------------------------------------------
In their February 2004 SIP revisions, each of the States
resubmitted to EPA the attainment plan contained in its prior SIP
revisions' attainment plan along with additional elements required for
a severe area attainment plan, such as a post-1999 ROP plan and the VMT
offset SIPs, a contingency measures plan to augment the previously
submitted 1996-1999 ROP plan and contingency measures plan,
respectively, as well as other SIP elements not included in the
previous SIP revisions' attainment plan.
We proposed action on these attainment plans in a separate NPR
published in the Federal Register on February 9, 2005 (70 FR 6796). In
our February 9, 2005, NPR, we also proposed approval of the attainment
plan SIP revisions submitted by the District and Virginia.
In our February 9, 2005, NPR, with respect to the State of
Maryland's attainment plan for the Washington area, we proposed
approval contingent upon the State submitting an approvable SIP
revision for certain penalty fees, required by the Clean Air Act (the
Act), prior to the time EPA would issue a final rule on Maryland's
attainment plan. In the alternative, we proposed to disapprove the
attainment plan SIP revision submitted by the State of Maryland for the
Washington area and to issue a protective finding for the attainment
plan which would allow the motor vehicle emissions budgets (MVEBs)
identified in the attainment plan SIP to be used for demonstrating
transportation conformity purposes. EPA has taken a final action on the
Maryland's attainment plan for the Washington area in a separate final
rule which is published elsewhere in today's Federal Register. In that
final rule, EPA is disapproving the Maryland's attainment plan for the
Washington area because Maryland failed to submit the required fee
program, and, pursuant to 40 CFR 93.120(a), and issuing a protective
finding to the February 2004 SIP revisions' attainment plan. As we
explain in that rule, the protective finding will allow Maryland to use
the MVEBs contained in the disapproved SIP for transportation
conformity purposes pursuant to 40 CFR 93.120. In this rule we are
approving the modeling demonstration, which includes an analysis based
upon photochemical grid modeling (the modeled demonstration of
attainment and adjunct weight-of-evidence (WOE) analysis), contained in
the District's, Maryland's and Virginia's February 2004 SIP revisions.
We also determine that based upon this modeled demonstration of
attainment and adjunct WOE analysis Maryland's submitted SIP for the
Washington area contains adopted control measures that fully satisfy
the emission reduction requirements relevant to the Washington area
attaining the 1-hour ozone NAAQS by November 15, 2005. This
determination supports issuance of the protective finding for
transportation conformity purposes pursuant to 40 CFR 93.120.
B. Relationship to Past SIP Revisions and Litigation
1. Prior SIP Revisions
During 1998, the States submitted an attainment plan for the
Washington area and supplemented these submittals on the dates listed
in Table 3 of this document. These 1998 and 2000 calendar year
revisions cumulatively constituted the attainment plan for the
Washington area which at the time was classified as being in
``serious'' nonattainment of the 1-hour ozone NAAQS. In the aggregate
these attainment plans consisted of a photochemical modeling
demonstration and adjunct WOE analyses that demonstrated attainment of
the ozone NAAQS; projected emissions inventories showing that the
States collectively had adopted sufficient measures to support the
demonstration of attainment; attainment year MVEBs; and a commitment to
conduct and submit a mid-course review to EPA by a date certain. As
noted previously, the March 2000 SIP revisions consisted of a
commitment to revise the MVEBs one-year after EPA released the MOBILE6
model and the outyear budgets. These pre-2001 SIP revisions' attainment
plans were submitted to demonstrate that the Washington area would
attain the 1-hour ozone NAAQS by no later than November 15, 2005. On
January 3, 2001, EPA approved the pre-2001 SIP revisions and extended
the attainment date for the Washington area (then a
[[Page 25690]]
serious nonattainment area) until November 15, 2005.
2. January 3, 2001 Final Rule Vacated
A petition for review challenging the January 3, 2001 final
approval was filed by the Sierra Club. The petition alleged, among
other things, that EPA could not lawfully extend the attainment date of
a serious ozone nonattainment area past November 15, 1999 without
reclassifying the area as severe nonattainment, could not approve a SIP
for an area with a 2005 attainment date unless the plan provides for
ROP reductions after 1999 and could not approve a SIP that does not
include contingency measures. On July 2, 2002, the U.S. Court of
Appeals for the District of Columbia Circuit (the Court of Appeals)
issued an opinion to vacate our rule extending the attainment date and
approving the attainment plans and 1996-1999 ROP plans. Among other
things, the Court of Appeals found that EPA had no authority to extend
the attainment date of a serious ozone nonattainment area without
reclassifying the area as severe nonattainment, and could not approve a
SIP for an area with a 2005 attainment date unless the plan provides
for ROP reductions until the attainment date. See Sierra Club v.
Whitman, 294 F.3d 155, 160-163 (D.C. Cir. 2002). The Court of Appeals
also found that EPA could not approve the pre-2001 SIP revisions
because a contingency measures plan, which is required under section
172(c)(9) of the Act, is one of the elements listed under section
172(c) as a requirement for a revised SIP for an area in nonattainment.
See Id. at 164.
3. Nonattainment Area Plan Requirements
Under section 172(c) of the Act, a revised SIP for an area in
nonattainment must also include elements such as an attainment
demonstration and all reasonably available control measures (RACM),
reasonable further progress toward attainment, an emissions inventory,
and new source permitting programs. Under section 182(d), a revised SIP
for an area in severe ozone nonattainment must include reasonably
available control technology (RACT) on, and new source review (NSR)
permitting of, major stationary sources of nitrogen oxides
(NOX) emissions and volatile organic compound (VOC)
emissions with a potential to emit of 25 tons per year (TPY) or
greater; new source permitting offset ratios of 1.3 to 1 or greater; a
VMT Offset SIP; a ROP plan to achieve a 15 percent reduction in VOC
emissions by 1996; plans for achieving an average of a 3 percent per
year ROP reductions after 1996 through the attainment date; and a SIP
revision to impose the penalty fees specified in section 185 of the
Act.
EPA believes Sierra Club v. Whitman, 294 F.3d 155, can be read to
require that before we can approve the overall revised SIP for the
nonattainment area we must approve all of the elements applicable to
the area under sections 172(c) and 182 of the Act. In this document,
the overall SIP for the nonattainment area will be termed the
``attainment plan.''
Under section 182 of the Act, a demonstration that the SIPs for a
nonattainment area, as revised, will provide for attainment of the 1-
hour ozone NAAQS by November 15, 2005 is a separate component of the
overall attainment plan. See 42 U.S.C. 7511a(c)(2)(A). Such a
demonstration for a severe ozone nonattainment area must be based upon
photochemical grid modeling (or similarly effective method) and must
show that the submitted demonstration relies upon or contains adopted
control measures that fully satisfy the emission reduction requirements
relevant to demonstrating attainment of the 1-hour ozone NAAQS by
November 15, 2005. Id.
4. Washington Area Reclassified to Severe Nonattainment
On January 24, 2003 (68 FR 3410), EPA reclassified the Washington
area to severe nonattainment because the area failed to attain 1-hour
ozone NAAQS by the November 15, 1999 statutory attainment date for
serious areas. This action made the area subject to the additional
requirements applicable to severe areas under section 182(d) of the
Act. On April 17, 2003 (68 FR at 19107), EPA conditionally approved the
pre-2001 SIP revisions (the history of litigation on the April 17, 2003
conditional approval will be discussed in a later paragraph of this
document titled ``April 17, 2003 Final Rule Vacated and Withdrawn'').
5. Recent SIP Revision Actions
In the months that followed the January 24, 2003 reclassification
of the Washington area to severe nonattainment and the April 17, 2003
conditional approval, the States submitted the SIP revisions necessary
to satisfy the requirements of section 182(d) of the Act for severe
areas and EPA's conditional approval, with the exception of Maryland
which failed to submit a SIP revision for the section 185 penalty fee
program. These SIP revisions included February 2004 SIP revisions. The
February 2004 SIP revisions contained the attainment plan which
consists of: (1) A photochemical modeling demonstration and adjunct WOE
analyses to demonstrate attainment of the ozone NAAQS by no later than
November 15, 2005; (2) projected emissions inventories showing that the
States, including Maryland, collectively had adopted sufficient
measures to support the demonstration of attainment; (3) attainment
year MVEBs; and (4) a commitment to conduct and submit a mid-course
review to EPA by a date certain.\6\ In their February 2004 SIP
revisions, each of the States resubmitted to EPA the attainment plan
contained in the State's pre-2001 SIP revisions' attainment plan along
with additional elements required for a severe area attainment plan,
such as a 1999-2005 ROP plan, and a contingency measures plan to
augment the previously submitted 1996-1999 ROP plan and contingency
measures plan, respectively, as well as other SIP elements not included
in the pre-2001 SIP revisions' attainment plan.
---------------------------------------------------------------------------
\6\ The February 2004 SIP revisions did not need to contain a
commitment to revise the MVEBs one-year after EPA released the
MOBILE6 model because the MVEBs in these plans were developed using
MOBILE6.
---------------------------------------------------------------------------
6. April 17, 2003 Final Rule Vacated and Withdrawn
A petition for review challenging the April 17, 2003 final
conditional approval was filed by the Sierra Club. The petition
alleged, among other things, that EPA could not lawfully conditionally
approve the SIPs due to a lack of specificity in the States' commitment
letters, that EPA should require the 1996-1999 ROP to be revised to use
the latest mobile sources emission factor model and that the
photochemical grid modeling supporting the attainment plan did not meet
the requirements of the Act. On February 3, 2004, the Court of Appeals
issued an opinion to vacate our rule conditionally approving the
attainment plans and 1996-1999 ROP plans insofar as that Court found
that our grant of conditional approval was defective. The Court of
Appeals denied the petition for review in all other respects. See
Sierra Club v. EPA, 356 F.3d 296, 301-07 (D.C. Cir. 2004). On April 23,
2004, the Court of Appeals issued its mandate thereby relinquishing
jurisdiction over the 1996-1999 ROP plans and the attainment plan SIP
revisions, and remanding them back to EPA.\7\
---------------------------------------------------------------------------
\7\ On April 16, 2004, the Court of Appeals issued an order
revising the February 3, 2004, opinion to address a petition for
rehearing filed by the Sierra Club, but otherwise leaving its
decision to vacate and remand the conditional approval to EPA
intact. Sierra Club v. EPA, No. 03-1084, 2004 WL 877850 (DC Cir.
Apr. 16, 2004).
---------------------------------------------------------------------------
[[Page 25691]]
Effective as of the April 23, 2004 date the Court of Appeals issued
its mandate for its February 3, 2004 ruling, all three States withdrew
their pre-2001 SIP revisions' attainment plan which had been submitted
during 1998 and 2000, specifically the SIP revisions listed in Table 2
of the April 17, 2003, final rule (68 FR 19107). By the time the three
States withdrew the pre-2001 SIP revisions' attainment plan, they had
already submitted revised attainment plan SIP revisions with an
analysis that the SIPs contained all RACM, post-1999 ROP plans
demonstrating ROP for 2002 and 2005, VMT offset plans and contingency
measures plans that superceded the earlier submissions. The States, in
their February 2004 SIP submissions, submitted not only this new
material, but resubmitted all of the previously withdrawn pre-2001 SIP
revisions' attainment plan.\8\ The newly submitted materials along with
the resubmitted pre-2001 SIP revisions' attainment plan, form a single
comprehensive package. EPA is taking final action today on both the
newly submitted and resubmitted materials, which we collectively refer
to as the February 2004 SIP revisions.
---------------------------------------------------------------------------
\8\ With one exception: the ``outyear budgets,'' which were
contained in the March 31, 2002 SIP revision on which EPA had never
proposed to take action, were not resubmitted.
---------------------------------------------------------------------------
7. District Court Action
The Sierra Club filed a complaint in the United States District
Court for the District of Columbia (District Court) claiming that
because the Court of Appeals vacated and remanded the conditional
approval of the pre-2001 SIP revisions' attainment demonstration and
the 1996-1999 ROP plans, EPA had an unfulfilled nondiscretionary duty
to complete final action on those SIP revisions. On April 7, 2005, the
District Court issued an order enjoining EPA to ``complete final
approval and disapproval action, in accordance with 42 U.S.C.
7410(k)(2), (3), on the state implementation plan submittals for the
Washington area identified at 66 FR 586, 586 (January 3, 2001).''
Sierra Club v. Johnson, C.A. No. 04-2163 (JR) (April 7, 2005). The
District Court's decision took note ``that the states formally withdrew
their pre-2001 submissions (except for the [ROP plans]) after the D.C.
Circuit's Sierra Club III remand,'' Id., slip op. at 7, but disputed
that ``these withdrawals removed EPA's duty to act,'' stating that ``
`withdrawal' of pre-2001 SIPs could [not] push back the deadlines
established by Congress.''
EPA does not dispute that withdrawal of a SIP cannot push back a
statutory deadline established by Congress. However, EPA disagrees that
it can act on a SIP submittal formally withdrawn by a state. We note,
however, that such a withdrawal is not without consequence, as
withdrawal of required SIP revision puts a state in jeopardy of
sanctions predicated upon a failure to submit the required SIP. However
in this case, as described in this document, the States resubmitted the
materials comprising their withdrawn pre-2001 SIP revisions' attainment
plan as part of the February 2004 SIP submissions. EPA therefore will
take action on what the District Court termed the ``pre-2001
submissions,'' \9\ as follows:
---------------------------------------------------------------------------
\9\ The District Court used the term ``pre-2001 submissions''
and ``pre-2001 SIPs'' which consists of what in this document we
call ``the pre-2001 SIP revisions' attainment demonstration'' and
``the 1996-1999 ROP plan.''
---------------------------------------------------------------------------
(1) In this final rule which
(a) approves all of the control measures and other constituents
needed to approve Maryland's severe area attainment plan (except for a
Section 185 fee program), including all control measures need to fully
satisfy the emissions reductions relevant to attainment of the 1-hour
ozone NAAQS;
(b) approves all of the control measures and other constituents
needed to approve the District's and Virginia's severe area attainment
plan;
(c) approves the 1996-1999 ROP plan for the District, Maryland and
Virginia;
(d) approves Maryland's modeled demonstration of attainment and
adjunct weight of evidence analyses; and
(e) approves the District's and Virginia's modeled demonstrations
of attainment and adjunct weight of evidence analyses and the
District's and Virginia's attainment plans, which include their pre-
2001 SIP revisions' attainment plan, as resubmitted and subsumed by
their February 2004 SIP revisions;
(2) Another final rule, which is published elsewhere in today's
Federal Register, which disapproves Maryland's pre-2001 SIP revisions'
attainment plan as resubmitted and subsumed by Maryland's February 2004
SIP revisions' attainment plan based upon Maryland's failure to submit
the required 185 fee program, and issues a protective finding on the
SIP, based upon our determination that the SIP contains all of the
control measures necessary to demonstrate attainment. That protective
finding will allow Maryland to use the MVEBs contained in the
disapproved SIP for transportation conformity purposes pursuant to 40
CFR 93.120.
II. The Relationship of Past SIP Revisions, February 2004 SIP Revisions
and the April 17, 2003 Conditional Approval
A. The Twelve Conditions for Approval
On April 17, 2003, EPA had conditionally approved the pre-2001 SIP
revisions subject to the following 12 conditions:
(1) Revise the 1996-1999 portion of the ROP plans to include a
contingency plan containing adopted measures;
(2) Revise the contingency plan containing those adopted measures
implemented for the failure of the Washington area to attain the one-
hour ozone standard for serious areas by November 15, 1999;
(3) Revise the ROP plans to include a contingency plan containing
adopted measures for the post-1999 ROP plans;
(4) Revise the attainment demonstration to include a contingency
plan containing adopted measures to be implemented if the Washington
area does not attain the one-hour ozone standard by November 15, 2005;
(5) Revise the ROP plans to demonstrate emission reductions of
ozone precursors of an average of 3 percent per year from November 15,
1999 to the November 15, 2005;
(6) Revise the attainment demonstration to include a revised RACM
analysis;
(7) Revise the major stationary source threshold to 25 tons per
year;
(8) Revise RACT rules to include the lower major source
applicability threshold;
(9) Revise new source review offset requirements to require an
offset ratio of at least 1.3 to 1.
(10) Submit a SIP revision that identifies and adopts specific
enforceable transportation control strategies and transportation
control measures to offset any growth in emissions from growth in
vehicle miles traveled or number of vehicle trips if required under
section 182(d)(1) of the Act;
(11) Submit the section 185 penalty fee SIP consisting of the
penalty fee requirement of Act sections 182(d)(3) and 185 for major
sources of VOC and NOX should the area fail to attain by
November 15, 2005;
(12) Update the Washington area severe attainment demonstration to
reflect revised MOBILE6-based motor vehicle emissions budgets,
including revisions to the attainment modeling/weight of evidence
demonstration and adopted control measures, as necessary, to show that
the SIP continues to demonstrate attainment by November 15, 2005.
[[Page 25692]]
In the February 3, 2003 (68 FR 5246) proposed rule for the April
17, 2003 final conditional approval, we proposed conditional approval
of the pre-2001 SIP revisions if the State committed to correct
condition numbers (1) through (3), (6) and (12). EPA revised the
conditional approval to include condition numbers (4), (5), and (7)
through (11) in response to comment which stated that EPA could not
fully approve the pre-2001 SIP revisions because the pre-2001 SIP
revisions did not cover all of the required severe area SIP components.
EPA agreed with the comment to the extent that condition numbers (4),
(5), and (7) through (11) were applicable severe area requirements that
precluded full approval. See 68 FR at 19121, April 17, 2003.
Conditions (1) and (2) were elements needed to correct deficiencies
in the SIP required for a serious nonattainment area.
Conditions (4) through (11) are SIP elements required as a
consequence of the reclassification of the Washington area to severe
nonattainment.
Conditions (3) through (6) were required to correct deficiencies in
the pre-2001 SIP revisions because the pre-2001 SIP revisions included
a demonstration that the Washington area would attain the 1-hour ozone
standard by November 15, 2005.
We conditioned approval on item (12) under EPA's policy related to
the transition from our prior mobile source emissions factor model,
MOBILE5, to the newer model, MOBILE6.
B. How the States Have Addressed the Twelve Conditions
In this section we will discuss how the States have addressed the
twelve conditions. EPA had already approved many of the States' SIP
revisions for the control measures needed to support the attainment
plan, the ROP plans and the contingency measure plan by the time we
published the NPRs on January 12, 2005 (70 FR 2085) and February 9,
2005 NPR (70 FR 6796) for the States' 1996-1999 ROP plans and the
February 2004 SIP revisions including the resubmitted pre-2001 SIP
revisions' attainment plan. In this document we will not reiterate the
specifics of such approvals but will provide details on the approval of
control measures which were not approved at the time of the January 12,
2005 and February 9, 2005 NPRs.
1. Conditions 1 to 4--Contingency Measures
At the time of the January 12, 2005 NPR for the contingency
measures plan, EPA had approved all the contingency measures except
each of the States' architectural and industrial maintenance coatings
rules (AIM coatings rules), and the District's motor vehicle
refinishing, consumer products, solvent cleaning and portable fuels
container rules.
On May 2, 2005, the Regional Administrator signed final rules
approving the District's, Maryland's and Virginia's AIM coatings rules.
Those final actions have been published in a recent Federal Register or
shortly will be published in the Federal Register.
On December 23, 2004 (69 FR 76855), December 28, 2004 (69 FR
77642), December 29, 2004 (69 FR 77906) and December 29, 2004 (69 FR
77903), EPA approved, respectively, the District's motor vehicle
refinishing, consumer products, solvent cleaning and portable fuels
container rules.
In this final rule, EPA is approving the States's contingency
measures plans for the Washington area. These contingency measure plans
provide sufficient contingency measures to meet our 3 percent (relative
to baseline emissions for the Washington area) reduction for all of the
relevant years for which the States need contingency measures. Our
basis for determining that the States' contingency measures plans get
the required reductions is discussed in detail in section V.
``Contingency Measures Plans'' of the January 12, 2005 NPR (70 FR at
2087-2095) and in our response to comments under sections III. D.
``Comment on the Contingency Measures Plans'' of this document.
EPA finds that the actions cited in the preceding four paragraphs
fulfilled conditions (1) through (4).
2. Condition 5--Post-1999 ROP
At the time of the January 12, 2005 NPR for the ROP plans and the
February 9, 2005 NPR on the attainment demonstration, EPA had approved
all the control measures except each of the States' AIM coatings rules,
the District's portable fuels container rule, the TCMs submitted with
the 1996-1999 and post-1999 ROP plans and Maryland's and Virginia's
nonregulatory measures SIP revisions.
As noted previously, EPA has approved the States' AIM coatings
rules and the District's portable fuel containers rule. In this action,
EPA is approving the TCMs submitted with the 1996-1999 and post-1999
ROP plans.
On May 2, 2005, the Regional Administrator signed a final rule
approving Maryland's and Virginia's nonregulatory measures SIP
revision. That final action has been published in a recent Federal
Register or shortly will be published in the Federal Register.
In this final rule EPA is approving the States' 1996-1999 and post-
1999 ROP plans. Our basis for determining that the States' ROP plans
get the required post-1996 ROP reductions of 3 percent per year
(averaged over consecutive 3-year periods) is discussed in detail in
section IV. ``Post 1996-1999 and Post 1999-2005 ROP Plans'' of the
January 12, 2005 NPR (70 FR at 2087-2095) and in our response to
comments under sections III. A. ``Comment on the ROP Plans and
NOX Substitution'' and B. ``Comment on the Transportation
Demand Model (TDM) Used in the Plans'' of this document.
EPA finds that the actions cited in the preceding four paragraphs
fulfilled condition (5).
3. Condition 6--RACM
For the reasons cited in our February 9, 2005 NPR, EPA believes
that the States' attainment demonstration in the February 2004 SIP
revisions demonstrated that no remaining RACM remain to be adopted for
the Washington area. We received no adverse comment on this aspect of
the proposal and find that the States have fulfilled condition 5 by
adoption of all the measures necessary to demonstrate attainment as
expeditiously as practicable.
4. Conditions 7 to 9--New Source Review and RACT Thresholds
EPA has approved a SIP revision to implement the severe area NSR
requirements in the Washington area for both VOC and NOX
including an offset ratio of 1.3:1 and a major source applicability
definition of 25 tons/year. See 69 FR 77647, December 28, 2004; 69 FR
56170, September 20, 2004; and 69 FR 48150, August 9, 2004, for the
District, Maryland, and Virginia, respectively. For each of the three
States, EPA has fully approved a SIP revision to implement RACT for
major sources of VOC and NOX with major source size
definition of 25 tons/year. See 69 FR 77647, December 28, 2004; 69 FR
56170, September 20, 2004; and 69 FR 48150, August 9, 2004, for the
District, Maryland, and Virginia, respectively. EPA finds that the
States have fulfilled conditions (7) through (9).
5. Condition 10--VMT Offset SIP
In this final rule EPA is approving the States' VMT Offset SIP
revisions which fulfills condition (10). Our basis for determining that
the States' VMT Offset SIP meets the Act's requirements is discussed in
detail in section VI. ``Vehicle Miles Traveled (VMT) Offset SIP and
Transportation Control Measures (TCMs)'' of the January 12,
[[Page 25693]]
2005 NPR (70 FR at 2098) and in our response to comments under section
III. C. ``Comment on the VMT Offset SIP'' of this document.
6. Condition 11--the Section 185 Penalty Fee SIP
On December 28, 2004 (69 FR 77639) and on December 29, 2004 (69 FR
77909), EPA approved the District's and Virginia's section 185 penalty
fee SIP revisions, respectively, and thus, believes that the District
and Virginia have fulfilled condition (11). To date, Maryland has not
submitted a section 185 penalty fee SIP revision. For the lack of a
section 185 penalty fee SIP revision, EPA is disapproving Maryland's
attainment plan with a protective finding which will allow the MVEBs
contained in Maryland's 2004 SIP revisions to be used for
transportation conformity purposes pursuant to 40 CFR 93.120. That
disapproval is published elsewhere in today's Federal Register.
7. Condition 12--MOBILE6-Based Attainment Plan Budgets
In their February 2004 SIP revisions, the States adopted MOBILE6-
based 2005 attainment year MVEBs. The final version of the 2005
attainment year MVEBs was contained in the February 2004 SIP revisions
identified in Table 2 of this document. These MVEBs are area-wide MVEBs
which cover the entire Washington area.
In this final rule EPA is approving the District's and Virginia's
attainment plan for the Washington area, namely the attainment plans
contained in the February 2004 SIP revisions which subsumes the
resubmitted pre-2001 SIP revisions' attainment plan. We are also
approving the final revision of the 2005 attainment year MVEBs for the
District and Virginia found in the February 2004 SIP revisions
identified in Table 2 of this document. EPA would have been able to
approve Maryland's attainment plan for the Washington area had Maryland
submitted a section 185 penalty fee program. We could not approve the
District's and Virginia's attainment plan without determining that the
three States collectively have adopted enough measures in their SIPs to
demonstrate that the area as a whole will attain the 1-hour ozone NAAQS
by no later than November 15, 2005. Such a finding is necessary because
this is an interstate area and any potential emissions shortfall would
have to be addressed collectively before any State's attainment plan
could be approved.
For the reasons stated in our February 9, 2005 NPR, the recently
approved control measures discussed previously in this final action and
given in our responses in this final action to comments received on
that proposed rule, EPA believes that the States collectively have
adopted enough measures in their SIPs to demonstrate that the area will
attain the 1-hour ozone NAAQS by no later than November 15, 2005 with
the MVEBs found in the February 2004 SIP revisions identified in Table
2 of this document. EPA believes that Maryland, in combination with the
District and Virginia, adopted sufficient measures and have fully
satisfied the emissions reduction requirements necessary to ensure that
attainment of the 1-hour ozone NAAQS will be attained by no later than
November 15, 2005. EPA believes that the States, including Maryland,
have satisfied condition (12) since they have demonstrated that the
attainment plans have been revised to reflect MOBILE6-based MVEBS and
have included the necessary revisions to the modeled demonstration of
attainment and adjunct WOE analyses and have adopted control measures
showing that the SIP continues to demonstrate attainment by November
15, 2005.
Therefore, in this final rule, EPA is approving the District's,
Maryland's, and Virginia's modeled demonstrations of attainment and
adjunct WOE analyses and the District's and Virginia's attainment
plans. EPA is also determining that the attainment plan for Maryland
contains adopted control measures that fully satisfy the emission
reduction requirement relevant to attainment of the 1-hour ozone NAAQS.
EPA is therefore approving the modeled demonstration of attainment and
adjunct WOE analyses contained in Maryland's February 2004 SIP
revisions which includes the analysis based upon photochemical grid
modeling demonstrating timely attainment of the 1-hour ozone standard.
In addition, EPA is therefore issuing Maryland's 2004 SIP revisions'
attainment plan--a protective finding which will allow the MVEBs
contained in Maryland's 2004 SIP revisions to be used for
transportation conformity purposes pursuant to 40 CFR 93.120.
EPA concludes that once we issue our approval of the District's and
Virginia's February 2004 SIP revisions the District and Virginia will
have cured the deficiencies we identified in their pre-2001 SIP
revisions through the various SIP revisions that they have submitted
since April 17, 2003. In the case of Maryland, EPA concludes that all
of the deficiencies except the section 185 penalty fee SIP revision
will have been cured for Maryland's pre-2001 SIP revisions by the
various SIP revisions submitted since April 17, 2003 once we issue our
approval of:
(1) Maryland's 1996-1999 and 1999-2005 ROP plans,
(2) the changes to the 1990 base year inventory, the contingency
measures plan, TCMs,
(3) the modeled demonstration of attainment which includes the
analysis based upon photochemical grid modeling and adjunct WOE
analyses that Maryland's submitted SIP for the Washington area contains
adopted control measures that fully satisfy the emission reduction
requirements to provide for attainment of the 1-hour ozone NAAQS in the
Washington area by November 15, 2005.
III. Comment Received on the ROP plans, VMT Offset SIP and Contingency
Measures Plan and EPA's Response
We received comments adverse to the proposed approval of the ROP,
VMT offset, contingency measures, and attainment plans. A summary of
these adverse comments, and our responses, follows.
A. Comment on the ROP plans and NOX Substitution
Comment: We received a comment asserting that the ROP plans do not
meet the requirement of demonstrating a nine percent reduction in VOC
emissions from 1999 to 2002 and a further nine percent from 2002 to
2005 because the NOX substitution in the ROP plans is
impermissible. The comment asserts that the ROP plans do not meet
section 182(c)(2)(c) of the Act because they do not show that a nine
percent reduction in NOX emissions will result in the same
reduction in ozone concentration as a nine percent reduction in VOC
emissions. The comment claims that EPA's own guidance requires
photochemical grid modeling to show equivalent changes in ozone
concentrations.
The comment also asserts that EPA's reliance on our December 1993
NOX Substitution Guidance is flawed because the plain
language of the Act requires proof of equivalent benefits of
NOX substitution. The comment also asserts that because the
1999-2005 ROP plan relies solely upon NOX reductions the
plans do not meet the requirement of section 182(c)(2)(C) because the
plan does not provide for some percentage of VOC reduction during each
period. The comment claims that the Act requires some non-zero
percentage reduction in VOC emissions for any ROP period.
The comment asserts that the Act requires the ROP plans to have VOC
reductions by November 15, 2002 to
[[Page 25694]]
prevent a net increase in VOC emissions by the 2002 milestone date,
which would offset the progress achieved by the nine percent
NOX reductions. The comment asserts that while the ROP plans
do provide for such reductions, EPA cannot approve the 1999-2005 ROP
plans because they do not provide for all of these reductions by the
2002 milestone date.
Response: NOX Substitution in General. The EPA believes
States have the opportunity to substitute NOX reductions for
required VOC reductions under certain circumstances. The opportunity
for NOX substitution originates in section 182(c)(2)(C) of
the Act which specifically allows NOX emissions reductions
to be substituted for VOC reductions required under section
182(c)(2)(B) for reasonable further progress (RFP), sometimes called
ROP.
EPA issued guidance to the States on how to implement the
NOX substitution provisions for the post-1996 ROP plans in
December 1993 (the December 1993 NOX Substitution Guidance).
The guidance allows States to substitute NOX emission
reductions for VOC emission reductions if that substitution is
consistent with the demonstration of attainment in the SIP. The modeled
demonstration of attainment in the SIP establishes the overall
reductions of VOC and/or NOX reductions required for
attainment in the attainment year. The ROP plan is a tool to phase in
emission reductions between the time the plan is prepared and the
attainment date. When substituting NOX for VOC in post-1996
ROP plans, we are mindful that if too many NOX reductions
are substituted for VOC reductions, the modeled demonstration of
attainment may no longer be valid. Our December 1993 NOX
Substitution Guidance allows substitution on a percentage basis (i.e.,
one percent of NOX emissions reductions can be substituted
for one percent of VOC emissions reductions).
Results of the Application of EPA's December 1993 NOX Substitution
Guidance in the Washington Area. EPA believes that NOX
substitution as applied to the Washington area based on our December
1993 NOX Substitution Guidance yields ROP plans that result
in reductions in ozone concentrations that are better than those which
would have resulted from ROP plans relying upon an equal percent of VOC
reductions.
Applying our December 1993 NOX Substitution Guidance to
the Washington area we substitute one percent of VOC ROP reductions
with one percent of NOX reductions. One percent of
NOX represents a larger quantity of emissions reduction than
does one percent of VOC. This is the case because ROP reductions are
computed from baseline emissions, which are defined in section
182(b)(2)(B) of the Clean Air Act to be ``the total amount of actual
VOC or NOX emissions from all anthropogenic sources in the
area during the calendar year 1990,'' excluding the emissions that
would be eliminated by the programs specified in sections 182(b)(1)(C)
and (D) of the Act. The reduction of baseline emissions by the programs
specified in sections 182(b)(1)(C) and (D) yields the adjusted 1990
base year inventory for each milestone year (which is discussed further
in the January 5, 2005 technical support document (TSD) \10\). The
adjusted 1990 base year inventory is the baseline from which the
necessary ROP reductions are computed. Section 182(c)(2) of the Act
requires that a set percentage of reductions in baseline emissions be
achieved every three years after 1996 until the area's attainment date.
To determine the reductions in tons required for any given ROP
milestone year, the percentage is multiplied by the adjusted 1990 base
year inventory for that milestone year. For example, in the case of the
Washington area, the ``Adjusted 1990 Base Year Inventory for 2005'' for
VOC is 412.1 tons per day (TPD), and, thus, a one percent ROP reduction
equates to 4.1 TPD. For NOX emissions the ``Adjusted 1990
Base Year Inventory for 2005'' is 735.6 TPD, and, thus, a one percent
ROP reduction equates to 7.4 TPD.
---------------------------------------------------------------------------
\10\ Technical Support Document for Approval and Promulgation of
Air Quality Implementation Plans; District of Columbia, Maryland,
and Virginia; Post-1996 Rate-of-Progress Plan, Contingency Measures,
Transportation Control Measures, 1990 Base Year Inventory Changes,
and VMT Offset SIP for the Metropolitan Washington, DC Nonattainment
Area, January 5, 2005
---------------------------------------------------------------------------
The States only modeled changes in anthropogenic (man-made)
emissions to see how sensitive the Washington area was to changes in
VOC and to NOX emission reductions. They did not model
changes in biogenic emissions which are VOC emissions from plants. The
air quality model responds to changes in emission between the 1990 base
year inventory and the emissions resulting from the control strategy to
be modeled.\11\
---------------------------------------------------------------------------
\11\ For a summary of the photochemical grid modeling for the
Washington area refer to the February 9, 2005 (70 FR 6796) NPR, and,
for a discussion in depth, see Technical Support Document for
Approval and Promulgation of Air Quality Implementation Plans;
District of Columbia, Maryland, and Virginia; Attainment
Demonstration for the Metropolitan Washington, DC Nonattainment
Area, dated January 31, 2005.
---------------------------------------------------------------------------
The States used the results of this sensitivity modeling to
determine that a one ton reduction in NOX emissions within
the Washington area would result in a peak ozone concentration
reduction of 0.114 parts per billion (ppb) (0.114 ppb/ton of
NOX); a similar analysis for VOC emissions indicated that a
one ton reduction in VOC emissions would result in a peak ozone
concentration reduction of 0.029 ppb (0.029 ppb/ton of VOC reduced).
The States concluded that emissions reductions of 34.0 tons/day of VOC
or 8.8 tons/day NOX would have to be required within the
Washington area would reduce ozone concentrations by 1 ppb. That is,
NOX reductions in the Washington area have greater ozone
reducing potential than an equivalent amount of VOC reductions.
Therefore, substituting a percentage of VOC reductions with an equal
percentage of NOX reductions should result in greater ozone
concentration reduction than if the substitution were not done.
The 1990 base year VOC inventory for the Washington area is
comprised of 578.7 TPD of anthropogenic emissions and of 376.5 TPD
biogenic emissions for a total of 955.2 TPD of VOC. The 1990 base year
NOX inventory (all of which is anthropogenic) for the
Washington area is 869.3 TPD of NOX. Given that 39 percent
(376.5/955.2) of the VOC emissions inventory is biogenic emissions, it
is not surprising that reductions in anthropogenic VOC emissions would
show less ozone response than an equal percentage reduction in
anthropogenic NOX emissions. The NOX emissions
are all anthropogenic, and, a one percent reduction in NOX
emissions equates to more tons of emission reduction than does one
percent reduction of the anthropogenic VOC emissions.
This is not to say VOC reductions are not beneficial towards
attainment, but rather that reductions in anthropogenic VOC emissions
are not as effective on a TPD or ROP percentage basis as NOX
reductions. However, the States are free to fashion their attainment
demonstrations and ROP plans to include whatever mix of VOC and
NOX reductions they choose, so long as the plans demonstrate
timely attainment and timely ROP in accordance with the requirements of
the Clean Air Act.
The following table compares a 9 percent reduction in baseline VOC
emissions by each post-1996 milestone year to the chosen levels of
NOX substitution in the ROP plans in terms
[[Page 25695]]
of TPD reductions and of ozone concentration decreases resulting from
these reductions.
Table 4.--Results of NOX Substitution in the Washington Area
----------------------------------------------------------------------------------------------------------------
Milestone year 1999 2002 2005
----------------------------------------------------------------------------------------------------------------
9 percent reduction in VOC baseline emissions (TPD)................ 39 37.8 37.1
Ozone Concentration Change to 9 percent VOC (at 0.029 ppb/ton 1.1 1.1 1.1
rounded to nearest tenth).........................................
Percent NOX reduction Substituted (percent of baseline NOX 8 9 9
emissions)........................................................
Substituted NOX Reductions (TPD)................................... 62.8 68.1 66.2
Ozone Concentration Change to Substituted NOX Reductions ( 0.114 7.2 7.8 7.5
ppb/ton rounded to nearest tenth).................................
----------------------------------------------------------------------------------------------------------------
Technical and Practical Reasons for our December 1993
NOX Substitution Guidance. The modeling performed for
demonstration of attainment basically establishes the relationship
between emission reductions--either of VOC, NOX, or both--
and ozone reductions. This relationship is established for the
attainment year. As noted previously, the modeled attainment
demonstration establishes the overall VOC and/or NOX
emission targets that are consistent with attainment of the standard in
the attainment year. When EPA determines that a demonstration of
attainment is approvable, i.e., it demonstrates that the relevant area
will timely attain the NAAQS, we are making an implicit corollary
conclusion that the mix of VOC and/or NOX control measures
included in the area's demonstration of attainment is sufficient for
timely attainment.
The post-1996 ROP plan requirement is used to phase-in emission
reductions between the time of plan adoption and the attainment date.
EPA does not require modeling of interim years for the purpose of
trying to update the NOX/VOC/ozone relationship for a number
of reasons, including the following that are provided in our December
1993 NOX Substitution Guidance:
a. The strong likelihood that optimum ``exchange'' rates vary from
year to year and across a geographic area as an area's emissions
distribution and atmospheric chemistry change over time;
b. Uncertainty in modeling analyses, particularly when attempting
to ascertain responses from small percentage perturbations in
emissions; and
c. Resource limitations associated with modeling specific control
measures during interim years before attainment dates.
EPA continues to believe in the validity of this guidance and in
the reasoning set forth therein as it relates to NOX
substitution under the post-1996 ROP plan requirements.
Legal Rationale for EPA's December 1993 NOX Substitution
Guidance. The comment focuses exclusively upon the phrase ``result in a
reduction in ozone concentrations at least equivalent to that which
would result from the amount of VOC emission reductions required* * *
'' to the exclusion of remaining language of section 182(c)(2)(C). The
comment would completely ``write-out'' of the statutory text provisions
such as ``in lieu of the demonstration required under subparagraph (B),
a demonstration to the satisfaction of the Administrator * * * '' and
``in accord with such guidance [the substitution guidance required by
section 182(c)(2)(C)] a lesser percentage of VOCs may be accepted as an
adequate demonstration * * * '' (emphases added). In the plain text of
the statute Congress explicitly and affirmatively granted EPA broad
discretion as to what sort of demonstration is acceptable on this
technical and science-driven issue. See, e.g., Sierra Club v. EPA, 294
F.3d at 162-163.
In addition, EPA still stands behind its legal rationale underlying
the interpretation of ``equivalency'' that appears in our December 1993
NOX Substitution Guidance in section 4. In that guidance,
the basis for equivalency is the ability of a given control strategy
(i.e., any particular mix of NOX and VOC emission
reductions) to effect attainment of the ozone NAAQS by the designated
attainment year (December 1993 NOX Substitution Guidance, p.
2). Further, as we previously set out, the NOX emission
reductions credited toward ROP may be limited to the amount of
NOX reductions required in the demonstration of attainment.
In allowing a combination of NOX and VOC controls or the
substitution of NOX emissions reductions for VOC emissions
reductions, section 182(c)(2)(C) of the statute states that the
resulting reductions ``in ozone concentrations'' must be ``at least
equivalent'' to that which would result from the 3 percent VOC
reductions required as a demonstration of ROP under section
182(c)(2)(B).\12\ The second sentence of section 182(c)(2)(C) requires
EPA to issue guidance ``concerning the conditions under which
NOX control may be substituted for [or combined with] VOC
control.'' In particular, the Agency has been authorized by Congress to
address in the guidance the appropriate amounts of VOC control and
NOX control needed, in combination, ``in order to maximize
the reduction in ozone air pollution.'' Further, the Act explicitly
provides that the guidance may permit ROP demonstrations that allow a
lower percentage of VOC emission reductions as long as compensating
NOX reductions are achieved. In light of the language in the
Act evidencing Congressional intent under this subsection to maximize
the opportunity for ozone reductions, EPA believes that section
182(c)(2)(C) confers on the Agency the discretion to select, for
purposes of determining ``at least equivalent'' reductions, a
percentage of NOX emission reductions that is reasonably
calculated to achieve the statutorily required ozone reduction and
attainment progress goals intended by Congress. See Chevron U.S.A.,
Inc. v. NRDC, 467 U.S. 837, 842-44 (1984), Sierra Club v. EPA, 294 F.3d
at 162-163.
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\12\ Equivalent means: ``equal in value, force, amount, effect
or significance,'' or ``corresponding in effect or function; nearly
equal; virtually identical.'' Black's Law Dictionary, Eighth
Edition, 2004. (emphasis added).
---------------------------------------------------------------------------
As we have previously stated, when we determine that a
demonstration of attainment is approvable, we are making an implicit
corollary conclusion that the mix of VOC and/or NOX control
measures included in the area's demonstration of attainment is
sufficient for timely attainment.
As additional evidence that Congress was concerned with getting
more than minimal reductions in ozone concentrations through
substitution, EPA notes that the ROP demonstration described in section
182(c)(2)(B) focuses on reductions of a specified quantity of VOC
emissions per year (similarly, the 15 percent ROP reductions required
for
[[Page 25696]]
moderate ozone nonattainment areas focuses on reductions of that
specific quantity of VOC emissions per year). By contrast, the
alternative ROP demonstration in section 182(c)(2)(C) allows flexible
VOC/NOX emission reduction strategies, but only so long as
the overall quantitative reduction in ozone concentrations is
equivalent to the amount which, for serious ozone nonattainment areas,
Congress initially determined must be met (i.e., the ozone
concentrations achieved by VOC reductions of 3 percent per year) in
order to ensure expeditious progress towards attainment. In this regard
the House Committee Report states: ``NOX reductions may not
be substituted for VOC reductions in a manner that delays attainment of
the ozone standard or that results in lesser annual reductions in ozone
concentration than provided for in the demonstration of attainment.''
H.R. Rep. No. 490, 101st Cong., 2d Sess. 239 (1990).
Additional support for EPA's view that our December 1993
NOX Substitution Guidance's focus on the NOX and
VOC reductions necessary for attainment is consistent with
Congressional intent is found in section 182(g), which waives the
requirement for a milestone demonstration for a milestone that
coincides with an area's attainment date for an area that attains the
standard by that date.
EPA disagrees with the comment that EPA's ``Guidance on the Post-
1996 Rate-of-Progress Plan and Attainment Demonstration'' (corrected
version as of 2/18/94) specifies a different test, that is, a modeled
showing of equivalency, than does EPA's December 15, 1993
NOX Substitution Guidance. In section 4.1 of the ``Guidance
on the Post-1996 Rate-of-Progress Plan and Attainment Demonstration,''
EPA restated the equivalency test set forth in sections 2 and 3 of our
December 1993 NOX Substitution Guidance.
With regard to the photochemical grid modeling. section 4.1 of the
``Guidance on the Post-1996 Rate-of-Progress Plan and Attainment
Demonstration'' reads:
Section 182(c)(2)(C) states that actual NOX emission
reductions which occur after 1990 can be used to meet post-1996
emission reduction requirements, provided that such reductions meet
the criteria outlined in EPA's December 15, 1993 NOX
Substitution Guidance. The condition for meeting the rate-of-
progress requirement is that the sum of all creditable VOC and
NOX emission reductions must equal 3 percent per year
averaged over each applicable milestone period. The percent VOC
reduction is determined from the VOC rate-of-progress inventory and
the percent NOX reduction is determined from the
NOX rate-of-progress inventory. In addition, the overall
VOC and NOX reductions must be consistent with the area's
modeled attainment demonstration. In other words, the NOX
emission reductions creditable toward the rate-of-progress plan
cannot be greater than the cumulative reductions dictated by the
modeled attainment demonstration.
This portion of the 1994 guidance merely summarizes, and does not
alter, the guidance provided in our December 1993 NOX
Substitution Guidance. With regard to the photochemical grid modeling,
section 2 of our December 1993 NOX Substitution Guidance
specifies that the provision for NOX substitution recognizes
that a VOC-only control pathway may not be the most effective approach
for effecting attainment in all areas. Consequently, NOX
reductions are placed on a near equal footing with VOC through
substitution. The December 1993 NOX Substitution Guidance
establishes two conditions pursuant to both the substitution and RFP
provisions in the Act. The first condition requires that control
strategies incorporating NOX emission reduction measures
must demonstrate that the ozone NAAQS will be attained within time
periods mandated by the Act.