Determination of Attainment, Approval and Promulgation of Implementation Plans and Designation of Areas for Air Quality Planning Purposes; Indiana; Redesignation of Central Indiana To Attainment of the 8-Hour Ozone Standard, 41658-41669 [E7-14741]
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41658
Federal Register / Vol. 72, No. 146 / Tuesday, July 31, 2007 / Proposed Rules
INFORMATION CONTACT section to view
the hard copy of the docket. You may
view the hard copy of the docket
Monday through Friday, 8 a.m. to 4
p.m., excluding federal holidays.
FOR FURTHER INFORMATION CONTACT: For
Arizona issues, contact Wienke Tax,
Office of Air Planning, U.S.
Environmental Protection Agency,
Region IX, (520) 622–1622, e-mail:
tax.wienke@epa.gov. For Nevada issues,
contact Karina O’Connor, Office of Air
Planning, U.S. Environmental
Protection Agency, Region IX, (775)
833–1276, oconnor.karina@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, wherever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, we mean
the EPA.
EPA is proposing to approve state
implementation plans submitted by the
States of Arizona and Nevada that
address interstate transport with respect
to the 8-hour ozone and fine particulate
matter national ambient air quality
standards. In so doing, EPA has
determined that the plans submitted by
Arizona and Nevada and approved
herein satisfy requirements under Clean
Air Act section 110(a)(2)(D)(i) for each
State to submit a plan containing
adequate provisions to prohibit
interstate transport with respect to the
standards for 8-hour ozone and fine
particulate matter. The effect of this
proposal would be to approve the
Arizona and Nevada state
implementation plans addressing
interstate transport with respect to the
8-hour ozone and fine particulate
standards and to eliminate obligations
on the Agency to promulgate Federal
Implementation Plans for these States
addressing this same requirement.
In the Rules and Regulations section
of this Federal Register, we are taking
direct final action to take these actions
because we believe that they are not
controversial. If we receive adverse
comments, however, we will publish a
timely withdrawal of the direct final
rule and address the comments in
subsequent action based on this
proposed rule. We do not plan to open
a second comment period, so anyone
interested in commenting should do so
at this time. If we do not receive
comments, no further activity is
planned. For further information on this
proposal and the rationale underlying
our proposed action, please see the
direct final rule.
Dated: June 11, 2007.
Laura Yoshii,
Acting Regional Administrator, Region IX.
[FR Doc. E7–14475 Filed 7–30–07; 8:45 am]
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 52 and 81
[EPA–R05–OAR–2007–0173; FRL–8448–1]
Determination of Attainment, Approval
and Promulgation of Implementation
Plans and Designation of Areas for Air
Quality Planning Purposes; Indiana;
Redesignation of Central Indiana To
Attainment of the 8-Hour Ozone
Standard
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
SUMMARY: On March 26, 2007, the
Indiana Department of Environmental
Management (IDEM) submitted a
request for EPA approval of a
redesignation of Boone, Hamilton,
Hancock, Hendricks, Johnson, Madison,
Marion, Morgan, and Shelby Counties
(the Central Indiana Area) to attainment
of the 8-hour ozone National Ambient
Air Quality Standard (NAAQS). IDEM
also requested EPA approval of an
ozone maintenance plan for this area as
a revision of the Indiana State
Implementation Plan (SIP). EPA
proposes to determine that the Central
Indiana Area has attained the 8-hour
ozone NAAQS. EPA proposes to
approve Indiana’s request to redesignate
the Central Indiana Area to attainment
of the 8-hour ozone NAAQS and to
approve the State’s ozone maintenance
plan for this area as a revision of the
Indiana SIP. Finally, EPA proposes to
approve Volatile Organic Compounds
(VOC) and Nitrogen Oxides (NOX)
Motor Vehicle Emission Budgets
(MVEBs) for the Central Indiana Area, as
supported by the ozone maintenance
plan for this area, for purposes of
transportation conformity
determinations.
Comments must be received on
or before August 30, 2007.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R05–
OAR–2007–0173, by one of the
following methods:
• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
• E-mail: mooney.john@epa.gov.
• Fax: (312) 886–5824.
• Mail: John M. Mooney, Chief,
Criteria Pollutant Section, Air Programs
Branch (AR–18J), U.S. Environmental
Protection Agency, 77 West Jackson
Boulevard, Chicago, Illinois 60604.
• Hand Delivery: John M. Mooney,
Chief, Criteria Pollutant Section, Air
Programs Branch (AR–18J), U.S.
DATES:
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Environmental Protection Agency, 77
West Jackson Boulevard, Chicago,
Illinois. Such deliveries are only
accepted during the Regional Office’s
normal hours of operation, and special
arrangements should be made for
deliveries of boxed information. The
Regional Office’s official hours of
operation are Monday through Friday,
8:30 a.m. to 4:30 p.m., excluding
Federal holidays.
Instructions: Direct your comments to
Docket ID No. EPA–R05–OAR–2007–
0173. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI, or otherwise
protected, through www.regulations.gov
or e-mail. The www.regulations.gov
Web site is an ‘‘anonymous access’’
system, which means EPA will not
know your identity or contact
information unless you provide it in the
body of your comment. If you send an
e-mail comment directly to EPA without
going through www.regulations.gov,
your e-mail address will be
automatically captured and included as
part of the comment that is placed in the
public docket and made available on the
Internet. If you submit an electronic
comment, EPA recommends that you
include your name and other contact
information in the body of your
comment and with any disk or CD–ROM
you submit. If EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should avoid
the use of special characters and any
form of encryption, and should be free
of any defects or viruses. For additional
instructions on submitting comments,
go to section I of the SUPPLEMENTARY
INFORMATION section of this document.
Docket: All documents in the docket
are listed in the www.regulations.gov
index. Although listed in the index,
some information is not publicly
available, e.g., CBI or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, will be publicly
available only in hardcopy. Publicly
available docket materials are available
either electronically in
www.regulations.gov or in hardcopy at
the Environmental Protection Agency,
Region 5, Air and Radiation Division, 77
West Jackson Boulevard, Chicago,
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Illinois 60604. This facility is open from
8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding Federal holidays. It is
recommended that you telephone
Edward Doty, Environmental Scientist,
at (312) 886–6057, before visiting the
Region 5 office.
FOR FURTHER INFORMATION CONTACT:
Edward Doty, Environmental Scientist,
Criteria Pollutant Section, Air Programs
Branch (AR–18J), Environmental
Protection Agency, Region 5, 77 West
Jackson Boulevard, Chicago, Illinois
60604, (312) 886–6057,
doty.edward@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this proposed rule
whenever ‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used,
we mean the EPA. This supplementary
information section is arranged as
follows:
I. What Action is EPA Proposing to Take?
II. What is the Background for This Action?
A. General Background Information
B. What is the Impact of December 22,
2006, and June 8, 2007, United States
Court of Appeals Decisions Regarding
EPA’s Phase 1 Implementation Rule?
1. Summary of Court Decision
2. Requirements Under the 8-Hour Ozone
Standard
3. Requirements Under the 1-Hour Ozone
Standard
III. What are the Criteria for Redesignations
to Attainment?
IV. What Are EPA’s Analyses and Opinions
of the State’s Requests and What Are the
Bases for EPA’s Proposed Action?
A. Has the Central Indiana Area Attained
the 8-Hour Ozone NAAQS?
B. Has the State of Indiana Committed to
Maintain the Ozone Monitoring System
in the Central Indiana Area?
C. Have the Central Indiana Area and the
State of Indiana Met All of the
Applicable Requirements of Section 110
and Part D of the Clean Air Act, and
Does the Central Indiana Area Have a
Fully Approved SIP Under Section
110(k) of the Clean Air Act?
1. The Central Indiana Area Has Met All
Applicable Requirements of Section 110
and Part D of the Clean Air Act
a. Section 110 and General SIP
Requirements
b. Part D SIP Requirements
c. Part D, Subpart 1 SIP Requirements
d. Section 176 Conformity Requirements
e. Part D New Source Review (NSR)
Requirements
2. The Central Indiana Area Has a Fully
Approved SIP Under Section 110(k) of
the Clean Air Act (CAA)
D. Are the Air Quality Improvements in the
Central Indiana Area Due to Permanent
and Enforceable Emission Reductions
Resulting from the Implementation of the
Indiana SIP and Applicable Federal Air
Pollution Control Regulations and Other
Permanent and Enforceable Emission
Reductions?
E. Does the Central Indiana Area Have a
Fully Approvable Ozone Maintenance
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Plan Pursuant to Section 175A of the
CAA?
1. What Is Required in an Ozone
Maintenance Plan?
2. What Are the Attainment Emission
Inventories for the Central Indiana Area?
a. Point Sources
b. Area Sources
c. On-Road Mobile Sources
d. Non-Road Mobile Sources
3. Has the State Demonstrated Maintenance
of the Ozone Standard in the Central
Indiana Area?
4. What Is the Contingency Plan for the
Central Indiana Area?
5. Has the State Committed to Update the
Ozone Maintenance Plan in Eight Years
After the Redesignation of the Central
Indiana Area to Attainment of the 8-Hour
Ozone NAAQS?
V. Has the State Adopted Acceptable Motor
Vehicle Emissions Budgets for the End
Year of the Ozone Maintenance Period
Which Can Be Used to Support
Conformity Determinations?
A. How Are the Motor Vehicle Emission
Budgets Developed, and What Are the
Motor Vehicle Emission Budgets for the
Central Indiana Area?
B. Are the MVEBs Approvable?
VI. What Are the Effects of EPA’s Proposed
Actions?
VII. Statutory and Executive Order Reviews
I. What Action Is EPA Proposing to
Take?
We are proposing to take several
related actions for the Central Indiana
Area (Boone, Hamilton, Hancock,
Hendricks, Johnson, Madison, Marion,
Morgan, and Shelby Counties). First, we
are proposing to determine that this area
has attained the 8-hour ozone NAAQS.
Second, we are proposing to approve
Indiana’s ozone maintenance plan for
this area as a revision of the Indiana SIP.
The maintenance plan is designed to
keep this area in attainment of the 8hour ozone NAAQS through 2020.
Third, as supported by and consistent
with the ozone maintenance plan, we
are proposing to approve the 2006 and
2020 VOC and NOX MVEBs (54.32 tons
VOC/day and 106.19 tons NOX/day in
2006, and 29.52 tons VOC/day and
35.69 tons NOX/day in 2020) for the
nine counties in the Central Indiana
Area for transportation conformity
determination purposes. Finally, we are
proposing to approve the redesignation
of the Central Indiana Area to
attainment of the 8-hour ozone NAAQS.
II. What Is the Background for This
Action?
A. General Background Information
EPA has determined that ground-level
ozone is detrimental to human health.
On July 18, 1997, EPA promulgated an
8-hour ozone NAAQS (62 FR 38856) of
0.08 parts per million parts of air (0.08
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ppm) (80 parts per billion (ppb)).1 This
8-hour ozone standard replaced a prior
1-hour ozone NAAQS, which was
promulgated on February 8, 1979 (44 FR
8202), and which EPA revoked on June
15, 2005 (69 FR 23858).
Ground-level ozone is generally not
emitted directly by emission sources.
Rather, emitted NOX and VOC react in
the presence of sunlight to form groundlevel ozone along with other secondary
compounds. NOX and VOC are referred
to as ‘‘ozone precursors.’’ Control of
ground-level ozone concentrations is
achieved through controlling VOC and
NOX emissions.
Section 107 of the CAA requires EPA
to designate as nonattainment any area
that violates the 8-hour ozone NAAQS.
A Federal Register notice promulgating
8-hour ozone designations and
classifications was published on April
30, 2004 (69 FR 23857).
The CAA contains two sets of
provisions—subpart 1 and subpart 2—
that address planning and emission
control requirements for nonattainment
areas. Both are found in title I, part D
of the CAA. Subpart 1 contains general,
less prescriptive requirements for all
nonattainment areas for any pollutant
governed by a NAAQS. Subpart 2
contains more specific requirements for
certain ozone nonattainment areas, and
applies to ozone nonattainment areas
classified under section 181 of the CAA.
In the April 30, 2004, designation
rulemaking, EPA divided 8-hour ozone
nonattainment areas into the categories
of subpart 1 nonattainment (‘‘basic’’
nonattainment) and subpart 2
nonattainment (‘‘classified’’
nonattainment). EPA based this division
on the areas’ 8-hour ozone design values
(i.e., on the three-year averages of the
annual fourth-highest daily maximum 8hour ozone concentrations at the worstcase monitoring sites in the designated
areas) and on their 1-hour ozone design
values (i.e., on the fourth-highest daily
maximum 1-hour ozone concentrations
over the three-year period at the worstcase monitoring sites in the designated
areas) 2 using ozone data from the
period of 2001–2003. EPA classified 8hour ozone nonattainment areas with 1hour ozone design values equaling or
1 This standard is violated in an area when any
ozone monitor in the area (or in its nearby
downwind environs) records 8-hour ozone
concentrations with a three-year average of the
annual fourth-highest daily maximum 8-hour ozone
concentrations equaling or exceeding 85 ppb. See
40 CFR 50.10.
2 The 8-hour ozone design value and the 1-hour
ozone design value for each area were not
necessarily recorded at the same monitoring site.
The worst-case monitoring site for each ozone
concentration averaging time was considered for
each area.
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exceeding 121 ppb as subpart 2,
classified nonattainment areas. EPA
classified all other 8-hour
nonattainment areas as subpart 1, basic
nonattainment areas. The basis for area
classification was defined in a separate
April 30, 2004, final rule (the Phase 1
implementation rule) (69 FR 23951). In
the April 30, 2004, ozone designation/
classification rulemaking, EPA
designated the Central Indiana Area, as
a subpart 1, basic nonattainment area for
the 8-hour ozone NAAQS.
On March 26, 2007, the State of
Indiana requested redesignation of the
Central Indiana Area to attainment of
the 8-hour ozone NAAQS based on
ozone data collected in this area during
the period of 2004–2006.
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B. What Is the Impact of December 22,
2006, and June 8, 2007, United States
Court of Appeals Decisions Regarding
EPA’s Phase 1 Implementation Rule?
1. Summary of Court Decision
On December 22, 2006, the U.S. Court
of Appeals for the District of Columbia
Circuit (D.C. Circuit) vacated EPA’s
Phase 1 implementation rule for the 8hour ozone standard (69 FR 23951,
April 30, 2004). South Coast Air Quality
Management Dist. v. EPA, 472 F.3d 882
(DC Cir. 2006). On June 8, 2007, in
South Coast Air Quality Management
Dist. v. EPA, Docket No. 04–1201, in
response to several petitions for
rehearing, the DC Circuit clarified that
the Phase 1 rule was vacated only with
regard to those parts of the rule that had
been successfully challenged. Therefore,
the Phase 1 rule provisions related to
classifications for areas currently
classified under subpart 2 of title I, part
D of the CAA as 8-hour nonattainment
areas, the 8-hour attainment dates and
the timing of emissions reductions
needed for attainment of the 8-hour
ozone NAAQS remain effective. The
June 8th decision left intact the Court’s
rejection of EPA’s reasons for
implementing the 8-hour standard in
certain nonattainment areas under
subpart 1 in lieu of subpart 2. By
limiting the vacatur, the Court let stand
EPA’s revocation of the 1-hour ozone
standard and those anti-backsliding
provisions of the Phase 1 rule that had
not been successfully challenged. The
June 8th decision reaffirmed the
December 22, 2006, decision that EPA
had improperly failed to retain
measures required for 1-hour
nonattainment areas under the antibacksliding provisions of the
regulations: (1) Nonattainment area New
Source Review (NSR) requirements
based on an area’s 1-hour nonattainment
classification; (2) section 185 penalty
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fees for 1-hour severe and extreme
nonattainment areas; and, (3) measures
to be implemented pursuant to section
172(c)(9) or 182(c)(9) of the CAA, on the
contingency of an area not making
reasonable further progress toward
attainment of the 1-hour NAAQS, or for
failure to attain that NAAQS. In
addition, the June 8th decision clarified
that the Court’s reference to conformity
requirements for anti-backsliding
purposes was limited to requiring the
continued use of 1-hour motor vehicle
emission budgets until 8-hour budgets
are available for 8-hour conformity
determinations, which is already
required under EPA’s conformity
regulations. The Court, thus, clarified
that 1-hour conformity determinations
are not required for anti-backsliding
purposes.
This section sets forth EPA’s views on
the potential effect of the Court’s rulings
on this proposed redesignation action.
For the reasons set forth below, EPA
does not believe that the Court’s rulings
alter any requirements relevant to this
redesignation action so as to preclude
redesignation, and do not prevent EPA
from proposing or ultimately finalizing
this redesignation. EPA believes that the
Court’s December 22, 2006, and June 8,
2007, decisions impose no impediment
to moving forward with redesignation of
this area to attainment, because even in
light of the Court’s decisions,
redesignation is appropriate under the
relevant redesignation provisions of the
CAA and longstanding policies
regarding redesignation requests.
2. Requirements Under the 8-Hour
Ozone Standard
With respect to the 8-hour ozone
standard, EPA notes that the Court’s
ruling rejected EPA’s reasons for
classifying areas under subpart 1 for the
8-hour ozone standard, and remanded
that matter to the EPA. Consequently, it
is possible that the Central Indiana Area
could, during a remand to EPA, be
reclassified under subpart 2. Although
any future decision by EPA to classify
this area under subpart 2 might trigger
additional future requirements for this
area, EPA believes that this does not
mean that redesignation of the area
cannot now go forward. This belief is
based upon (1) EPA’s longstanding
policy of evaluating redesignation
requests in accordance with the
requirements due at the time the
redesignation request is submitted; and,
(2) consideration of the inequity of
applying retroactively any future
requirements.
First, at the time the redesignation
request was submitted by the State, the
Central Indiana Area was classified
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under subpart 1 and was obligated to
meet only subpart 1 requirements.
Under EPA’s longstanding
interpretation of section 107(d)(3)(E) of
the CAA, to qualify for redesignation,
states requesting redesignation to
attainment must meet only the relevant
SIP requirements that came due prior to
the submittal of a complete
redesignation request. September 4,
1992, Calcagni memorandum
(‘‘Procedures for Processing Requests to
Redesignate Areas to Attainment,’’
Memorandum from John Calcagni,
Director, Air Quality Management
Division). See also September 17, 1993,
Michael Shapiro memorandum, 60 FR
12459, 12465–66 (March 7, 1995)
(redesignation of Detroit-Ann Arbor),
and Sierra Club v. EPA, 375 F.3d 537
(7th Cir. 2004), which upheld this
interpretation. See, e.g. also 68 FR
25418, 25424, 25427 (May 12, 2003)
(redesignation of St. Louis).
Moreover, it would be inequitable to
retroactively apply any new SIP
requirements that were not applicable at
the time the redesignation request was
submitted. The DC Circuit has
recognized the inequity in such
retroactive rulemaking. See Sierra Club
v. Whitman, 285 F.3d 63 (DC Cir. 2002),
in which the DC Circuit upheld a
District Court’s ruling refusing to make
retroactive an EPA determination of
nonattainment that was past the
statutory due date. Such a
determination would have resulted in
the imposition of additional
requirements on the area. The Court
stated: ‘‘Although EPA failed to make
the nonattainment determination within
the statutory timeframe, Sierra Club’s
proposed solution only makes the
situation worse. Retroactive relief would
likely impose large costs on the States,
which would face fines and suits for not
implementing air pollution prevention
plans in 1997, even though they were
not on notice at the time.’’ Id. at 68.
Similarly, here it would be unfair to
penalize the area by applying to it, for
purposes of redesignation, additional
SIP requirements under subpart 2 that
were not in effect at the time the State
submitted its redesignation request.
3. Requirements Under the 1-Hour
Ozone Standard
With respect to the requirements
under the 1-hour ozone standard, we
note that the Central Indiana Area was
made up of two types of areas relative
to the 1-hour ozone standard at the time
the 8-hour ozone standard was
promulgated. First, Marion County was
an ozone maintenance area, having been
previously designated as a
nonattainment area under the 1-hour
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preclude EPA from finalizing the
redesignation of this area.
ozone standard and having
subsequently been redesignated to
attainment of the 1-hour ozone
standard. Second, all remaining
Counties in the Central Indiana Area
were designated as attainment/
unclassifiable areas under the 1-hour
ozone standard, having never been
designated as 1-hour ozone
nonattainment areas. The Court’s ruling
on EPA’s Phase 1 rule does not impact
redesignation requests for either of these
types of areas.
First, because Boone, Hamilton,
Hancock, Hendricks, Johnson, Madison,
Morgan, and Shelby Counties were
designated as attainment/unclassifiable
under the 1-hour ozone standard, and
were never designated nonattainment
for the 1-hour ozone standard, there are
no outstanding 1-hour ozone
nonattainment requirements that these
counties would be required to meet.
Thus, we find that the Court’s ruling
does not result in any additional 1-hour
requirements for purposes of
redesignation.
Second, with respect to the 1-hour
ozone standard requirements for Marion
County, this area was an attainment area
subject to a Clean Air Act section 175A
maintenance plan under the 1-hour
ozone standard. The Court’s decisions
do not impact redesignation requests for
these types of areas, except to the extent
that the Court in its June 8th decision
clarified that for those areas with 1-hour
motor vehicle emissions budgets in their
1-hour ozone maintenance plans, antibacksliding requires that those 1-hour
budgets must be used for 8-hour
conformity determinations until
replaced by 8-hour budgets. To meet
this requirement, conformity
determinations in such areas must
continue to comply with the applicable
requirements of EPA’s conformity
regulations at 40 CFR part 93. The Court
clarified that 1-hour conformity
determinations are not required for antibacksliding purposes.
With respect to the three other antibacksliding provisions for the 1-hour
ozone standard that the Court found
were not properly retained, Marion
County is an attainment area subject to
a maintenance plan for the 1-hour ozone
standard, and the NSR, contingency
measures (pursuant to section 172(c)(9)
or 182(c)(9)), and fee provision
requirements no longer apply to this
area because it has been redesignated to
attainment of the 1-hour ozone
standard.
Thus, the decision in South Coast Air
Quality Management Dist. should not
The CAA provides the basic
requirements for redesignating a
nonattainment area to attainment.
Specifically, section 107(d)(3)(E) of the
CAA authorizes the EPA to redesignate
an area to attainment of the NAAQS
provided that: (1) The Administrator
determines that the area has attained the
applicable NAAQS based on current air
quality data; (2) the Administrator has
fully approved an applicable SIP for the
area under section 110(k) of the CAA;
(3) the Administrator determines that
the improvement in air quality is due to
permanent and enforceable emission
reductions resulting from
implementation of the applicable SIP,
Federal air pollution control
regulations, and other permanent and
enforceable emission reductions; (4) the
Administrator has fully approved a
maintenance plan for the area meeting
the requirements of section 175A of the
CAA; and, (5) the State containing the
area has met all requirements applicable
to the area under section 110 and part
D of the CAA.
EPA provided guidance on
redesignations in the General Preamble
for the Implementation of Title I of the
CAA Amendments of 1900 on April 16,
1992 (57 FR 13498), and supplemented
this guidance on April 28, 1992 (57 FR
18070). The two main policy guidelines
affecting the review of ozone
redesignation requests are the following:
‘‘Procedures for Processing Requests to
Redesignate Areas to Attainment,’’
Memorandum from John Calcagni,
Director, Air Quality Management
Division, September 4, 1992 (the
September 4, 1992 Calcagni
memorandum); and, ‘‘Reasonable
Further Progress, Attainment
Demonstration, and Related
Requirements for Ozone Nonattainment
Areas Meeting the Ozone National
Ambient Air Quality Standard,’’
Memorandum from John S. Seitz,
Director, Office of Air Quality Planning
and Standards, May 10, 1995 (the May
10, 1995 Seitz memorandum). For
additional policy guidelines used in the
review of ozone redesignation requests,
see our proposed rule for the
redesignation of the Evansville, Indiana
ozone nonattainment area at 70 FR
53606 (September 9, 2005).
3 The worst-case monitoring site-specific ozone
design value in the area and in its nearby
downwind environs.
IV. What Are EPA’s Analyses and
Opinions of the State’s Requests and
What Are the Bases for EPA’s Proposed
Action?
4 Three-year averages are specified for the last
year of each three-year period and specify the
monitoring site design values.
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III. What Are the Criteria for
Redesignations to Attainment?
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EPA is proposing to: (1) Determine
that the Central Indiana Area has
attained the 8-hour ozone standard; (2)
approve the ozone maintenance plan for
the Central Indiana Area and the VOC
and NOX MVEBs supported by the
maintenance plan; and, (3) approve the
redesignation of the Central Indiana
Area to attainment of the 8-hour ozone
NAAQS. The bases for our proposed
determination and approvals follow.
A. Has the Central Indiana Area
Attained the 8-Hour Ozone NAAQS?
For ozone, an area may be considered
to be attaining the 8-hour ozone NAAQS
if there are no violations of the NAAQS,
as determined in accordance with 40
CFR 50.10 and appendix I, based on the
most recent three complete, consecutive
calendar years of quality-assured air
quality monitoring data at all ozone
monitoring sites in the area and in its
nearby downwind environs. To attain
this standard, the average of the annual
fourth-high daily maximum 8-hour
average ozone concentrations measured
and recorded at each monitor (the
monitoring site’s ozone design value)
within the area and in its nearby
downwind environs over the most
recent three-year period must not
exceed the ozone standard. Based on an
ozone data rounding convention
described in 40 CFR 50, appendix I, the
8-hour ozone standard is attained if the
area’s ozone design value 3 is 0.084 ppm
(84 ppb) or less. The data must be
collected and quality-assured in
accordance with 40 CFR 58, and must
be recorded in EPA’s Air Quality
System (AQS). The ozone monitors
generally should have remained at the
same locations for the duration of the
monitoring period required to
demonstrate attainment (for three years
or more). The data supporting
attainment of the standard must be
complete in accordance with 40 CFR 50,
appendix I.
As part of the ozone redesignation
request, IDEM submitted summarized
2004–2006 peak 8-hour ozone
monitoring data for the Central Indiana
Area. These ozone concentrations are
part of the quality-assured ozone data
recorded in the Air Quality System. The
annual fourth-high 8-hour daily
maximum concentrations for each year,
along with the three-year averages,4 are
summarized in Table 1.
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TABLE 1.—ANNUAL FOURTH-HIGH DAILY MAXIMUM 8-HOUR OZONE CONCENTRATIONS IN PARTS PER MILLION (PPM)
Site Id
County
Site name
Year
Percent
observations
ozone season
Fourth-high
concentration
18–011–0001 ....................
Boone ...............................
18–057–1001 ....................
Hamilton ...........................
18–059–0003 ....................
Hancock ...........................
18–063–0004 ....................
Hendricks .........................
18–081–0002 ....................
Johnson ............................
18–095–0010 ....................
Madison ............................
18–097–0050 ....................
Marion ..............................
18–097–0057 ....................
Marion ..............................
18–097–0042 ....................
Marion ..............................
18–097–0073 ....................
Marion ..............................
18–109–0005 ....................
Morgan .............................
18–145–0001 ....................
Shelby ..............................
Whitestown .......................
Whitestown .......................
Whitestown .......................
Noblesville ........................
Noblesville ........................
Noblesville ........................
Fortville .............................
Fortville .............................
Fortville .............................
Avon .................................
Avon .................................
Avon .................................
Trafalgar ...........................
Trafalgar ...........................
Trafalgar ...........................
Emporia ............................
Emporia ............................
Emporia ............................
Ft. Benjamin Harrison ......
Ft. Benjamin Harrison ......
Ft. Benjamin Harrison ......
Harding St. .......................
Harding St. .......................
Harding St. .......................
Mann Road ......................
Mann Road ......................
Mann Road ......................
Naval Air Warfare Center
Naval Air Warfare Center
Naval Air Warfare Center
Monrovia ..........................
Monrovia ..........................
Monrovia ..........................
Fairland ............................
Fairland ............................
Fairland ............................
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
2004
2005
2006
100
100
100
99
99
100
100
99
99
100
100
100
100
100
98
100
100
97
99
99
100
100
100
93
99
100
98
100
100
93
99
100
100
99
100
98
0.072
0.082
0.080
0.075
0.087
0.077
0.072
0.080
0.075
0.071
0.078
0.073
0.073
0.077
0.078
0.072
0.078
0.073
0.073
0.080
0.076
0.066
0.081
0.076
0.065
0.076
0.074
0.071
0.080
0.072
0.072
0.078
0.077
0.071
0.080
0.073
The above data show that, during the
period of 2004–2006, no violations of
the 8-hour ozone standard were
recorded in the Central Indiana Area. In
addition, we find that the ozone data for
the years considered meet data
completeness requirements of 40 CFR
part 50, appendix I. Based on these data,
we conclude and find that the Central
Indiana Area has attained the 8-hour
ozone NAAQS.
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B. Has the State of Indiana Committed
To Maintain the Ozone Monitoring
System in the Central Indiana Area?
IDEM commits to maintain the ozone
monitoring network in the Central
Indiana Area during the ozone
maintenance period. Any necessary
changes in the ozone monitoring system
will be discussed in advance with the
EPA. This commitment is acceptable.
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C. Have the Central Indiana Area and
the State of Indiana Met All of the
Applicable Requirements of Section 110
and Part D of the Clean Air Act, and
Does the Central Indiana Area Have a
Fully Approved SIP Under Section
110(k) of the Clean Air Act?
We have determined that the Central
Indiana Area and the State of Indiana
have met all currently applicable SIP
requirements for the Central Indiana
Area, including the requirements under
section 110 of the CAA (general SIP
requirements) and the requirements
under subpart 1 part D of title I of the
CAA (requirements specific to all ozone
nonattainment areas). See section
107(d)(3)(E)(v) of the CAA. In addition,
EPA has fully approved the pertinent
elements of the Indiana SIP. See section
107(d)(3)(E)(ii) of the CAA. We note that
SIPs must be fully approved only with
respect to currently applicable
requirements of the CAA, which were
those CAA requirements applicable to
the Central Indiana Area at the time the
State of Indiana submitted the final,
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Three-year
average
........................
........................
0.078
........................
........................
0.079
........................
........................
0.075
........................
........................
0.074
........................
........................
0.076
........................
........................
0.074
........................
........................
0.076
........................
........................
0.074
........................
........................
0.071
........................
........................
0.074
........................
........................
0.075
........................
........................
0.074
complete ozone redesignation request
for this area, March 26, 2007.
1. The Central Indiana Area Has Met All
Applicable Requirements of Section 110
and Part D of the Clean Air Act
The September 4, 1992, Calcagni
memorandum describes EPA’s
interpretation of section 107(d)(3)(E) of
the CAA. To qualify for redesignation of
an area to attainment under this
interpretation, the State and the area
must meet the relevant CAA
requirements that come due prior to the
State’s submittal of a complete
redesignation request for the area. See
also the September 17, 1993, Michael
Shapiro memorandum and 66 FR 12459,
12465–12466 (March 7, 1995,
redesignating Detroit-Ann Arbor,
Michigan to attainment of the 1-hour
ozone NAAQS). Applicable
requirements of the CAA that come due
subsequent to the State’s submittal of a
complete redesignation request remain
applicable until a redesignation of the
area to attainment of the standard is
approved, but are not required as
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prerequisites to redesignation. See
section 175A(c) of the CAA. Sierra Club
v. EPA, 375 F.3d 537 (7th Cir. 2004). See
also 66 FR 25424, 25427 (May 12, 2003,
redesignation of the St. Louis/East St.
Louis area to attainment of the 1-hour
ozone NAAQS).
a. Section 110 and General SIP
Requirements
Section 110(a) of title I of the CAA
contains the general requirements for a
SIP, which include: enforceable
emission limitations and other emission
control measures, means, or techniques;
provisions for the establishment and
operation of appropriate devices
necessary to collect data on ambient air
quality; programs to enforce the
emission limitations; submittal of a SIP
that has been adopted by the State after
reasonable public notice and a hearing;
implementation of a source permit
program; provisions for the
implementation of part C requirements
(Prevention of Significant Deterioration
(PSD)) and part D requirements (NSR for
new sources or major source
modifications); criteria for stationary
source emission control measures,
monitoring, and reporting; provisions
for air quality modeling; and provisions
for public and local agency
participation.
SIP requirements and elements are
discussed in the following EPA
documents: ‘‘Procedures for Processing
Requests to Redesignate Areas to
Attainment,’’ Memorandum from John
Calcagni, Director, Air Quality
Management Division, September 4,
1992; ‘‘State Implementation Plan (SIP)
Actions Submitted in Response to Clean
Air Act (CAA) Deadlines,’’
Memorandum from John Calcagni,
Director, Air Quality Management
Division, October 28, 1992; and ‘‘State
Implementation Plan (SIP)
Requirements for Areas Submitting
Requests for Redesignation to
Attainment of the Ozone and Carbon
Monoxide (CO) National Ambient Air
Quality Standards (NAAQS) on or after
November 15, 1992,’’ Memorandum
from Michael H. Shapiro, Acting
Assistant Administrator, September 17,
1993. See also other guidance
documents listed above.
Section 110(a)(2)(D) of the CAA
requires SIPs to contain certain
measures to prevent sources in a State
from significantly contributing to air
quality problems in another State. To
implement this provision, EPA required
States to establish programs to address
transport of air pollutants (NOX SIP call
and Clean Air InterState Rule (CAIR)).
EPA has also found, generally, that
States have not submitted SIPs under
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section 110(a)(1) of the CAA to meet the
interstate transport requirements of
section 110(a)(2)(D)(i) of the CAA (70 FR
21147, April 25, 2005). However, the
section 110(a)(2)(D) requirements for a
State are not linked with a particular
area’s designation. EPA believes that the
requirements linked with a particular
area’s nonattainment designation and
classification are the relevant measures
to evaluate in reviewing a redesignation
request. The transport SIP submittal
requirements, where applicable,
continue to apply to a State regardless
of the designation of any one particular
area in the State.
We believe that these requirements
should not be construed to be applicable
requirements for purposes of
redesignation. Further, we believe that
the other section 110 elements
described above that are not connected
with nonattainment plan submissions
and that are not linked with an area’s
attainment status are also not applicable
requirements for purposes of
redesignation. A State remains subject
to these requirements after an area is
redesignated to attainment. We
conclude that only the section 110 and
part D requirements which are linked
with an area’s designation and
classification are the relevant measures
for evaluating this aspect of a
redesignation request. This approach is
consistent with EPA’s existing policy on
applicability of conformity and
oxygenated fuels requirements for
redesignation purposes, as well as with
section 184 ozone transport
requirements. See: Reading,
Pennsylvania proposed and final
rulemakings (61 FR 53174–53176,
October 10, 1996 and 62 FR 24826, May
7, 1997); Cleveland-Akron-Lorain, Ohio
final rulemaking (61 FR 20458, May 7,
1996); and Tampa, Florida final
rulemaking (60 FR 62748, December 7,
1995). See also the discussion on this
issue in the Cincinnati, Ohio ozone
redesignation (65 FR 37890, June 19,
2000), and the Pittsburgh, Pennsylvania
ozone redesignation (66 FR 50399,
October 19, 2001).
We believe that section 110 elements
not linked to the area’s nonattainment
status are not applicable for purposes of
redesignation. Nonetheless, we also note
that EPA has previously approved
provisions in the Indiana SIP addressing
section 110 elements under the 1-hour
ozone standard. We have analyzed the
Indiana SIP as codified in 40 CFR part
52, subpart P and have determined that
it is consistent with the requirements of
section 110(a)(2) of the CAA. The SIP,
which has been adopted after reasonable
public notice and hearing, contains
enforceable emission limitations;
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41663
requires monitoring, compiling, and
analyzing ambient air quality data;
requires preconstruction review of new
major stationary sources and major
modifications of existing sources;
provisions for adequate funding, staff,
and associated resources necessary to
implement its requirements; requires
stationary source emissions monitoring
and reporting; and otherwise satisfies
the applicable requirements of section
110(a)(2).
b. Part D SIP Requirements
EPA has determined that the Indiana
SIP meets applicable SIP requirements
under part D of the CAA. Under part D,
an area’s classification—either subpart 1
or subpart 2 (marginal, moderate,
serious, severe, and extreme)—indicates
the requirements to which it will be
subject. Subpart 1 of part D, found in
sections 172–176 of the CAA, sets forth
the basic nonattainment area plan
requirements applicable to all
nonattainment areas. Subpart 2 of part
D, found in section 182 of the CAA,
establishes additional specific
requirements depending on the area’s
nonattainment classification. Since the
Central Indiana Area is designated as a
subpart 1 nonattainment area for the 8hour ozone standard, the subpart 2 part
D requirements do not apply to these
Counties.
c. Part D, Subpart 1 SIP Requirements
For purposes of evaluating this
redesignation request, the applicable
subpart 1 part D requirements are
contained in sections 172(c)(1)–(9) and
176. A thorough discussion of the
requirements of section 172 can be
found in the General Preamble for
Implementation of Title I (57 FR 13498).
See also 68 FR 4852–4853, an ozone
redesignation notice of proposed
rulemaking for the St. Louis area, for a
discussion of section 172 requirements.
No requirements for the 8-hour ozone
standard under part D, subpart 1 of the
CAA came due for the Central Indiana
Area prior to when the State submitted
the complete ozone redesignation
request. For example, the requirement
for an ozone attainment demonstration,
as contained in section 172(c)(1), was
not yet due when the State submitted
the ozone redesignation request for
these counties, nor were the
requirements for Reasonably Available
Control Measures (RACM) and
Reasonably Available Control
Technology (RACT) (section 172(c)(1)),
Reasonable Further Progress (RFP)
(section 172(c)(2)), and attainment plan
and RFP contingency measures (section
172(c)(9)). All of these SIP elements are
required for submittal after Indiana
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submitted the complete, adopted ozone
redesignation request and maintenance
plan for the Central Indiana Area.
Therefore, none of the part D
requirements for the 8-hour ozone
standard are considered to be applicable
to the Central Indiana Area for purposes
of redesignation.
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d. Section 176 Conformity Requirements
Section 176(c) of the CAA requires
States to establish criteria and
procedures to ensure that Federallysupported or funded activities,
including highway projects, conform to
the air planning goals in the applicable
SIP. The requirement to determine
conformity applies to transportation
plans, programs, and projects
developed, funded, or approved under
Title 23 U.S.C. and the Federal Transit
Act (transportation conformity), as well
as to all other Federally-supported or
funded projects (general conformity).
State conformity SIP revisions must be
consistent with Federal conformity
regulations that the CAA required the
EPA to promulgate.
As with other part D requirements,
EPA interprets the conformity
requirements as not applying for
purposes of evaluating the ozone
redesignation request under section
107(d) of the CAA. In addition, please
note that conformity rules are required
for areas that are redesignated to
attainment of a NAAQS, and that
Federal conformity rules apply where
State rules have not been approved. See
Wall v. EPA, 265 F.3d 426 (6th Cir.
2001). See also 60 FR 62748 (December
7, 1995) (Tampa, Florida).
e. Part D New Source Review (NSR)
Requirements
EPA has determined that areas being
redesignated need not comply with the
requirement that a NSR program be
approved prior to redesignation,
provided that the area demonstrates
maintenance of the standard without
emission reductions from part D NSR,
since Prevention of Significant
Deterioration (PSD) requirements will
apply after redesignation. A more
detailed rationale for this view is
described in a memorandum from Mary
Nichols, Assistant Administrator for Air
and Radiation, dated October 14, 1994,
entitled, ‘‘Part D New Source Review
Requirements for Areas Requesting
Redesignation to Attainment.’’ Indiana
has demonstrated that the Central
Indiana Area will be able to maintain
the 8-hour ozone standard without part
D NSR in effect, and therefore, we
conclude that the State need not have a
fully approved part D NSR program
prior to approval of the redesignation
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14:56 Jul 30, 2007
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request. The State’s PSD program will
become effective in the Central Indiana
Area upon redesignation to attainment.
See rulemakings for Detroit, Michigan
(60 FR 12467–12468, March 7, 1995);
Cleveland-Akron-Lorain, Ohio (61 FR
20458, 20469–20470, May 7, 1996);
Louisville, Kentucky (66 FR 53665,
October 23, 2001); Grand Rapids,
Michigan (61 FR 31834–31837, June 21,
1996).
We conclude that the Central Indiana
Area has satisfied all applicable
requirements under section 110 and part
D of the CAA to the extent that these
requirements apply for purposes of
reviewing the State’s ozone
redesignation request.
2. The Central Indiana Area Has a Fully
Approved SIP Under Section 110(k) of
the Clean Air Act (CAA)
EPA has fully approved the Indiana
SIP for the Central Indiana Area under
section 110(k) of the CAA for all
applicable requirements. EPA may rely
on prior SIP approvals in approving a
redesignation request (See the
September 4, 1992, John Calcagni
memorandum, page 3; Southwestern
Pennsylvania Growth Alliance v.
Browner, 144 F.3d 984, 989–990 (6th
Cir. 1998); and, Wall v. EPA, 265 F.3d
426 (6th Cir. 2001)), plus any additional
measures it may approve in conjunction
with a redesignation action. See 68 FR
25426 (May 12, 2003). Since the passage
of the CAA of 1970, Indiana has adopted
and submitted, and EPA has fully
approved, provisions addressing the
various required SIP elements
applicable to the Central Indiana Area
for purposes of ozone redesignation. No
SIP provisions relevant to the Central
Indiana Area are currently disapproved,
conditionally approved, or partially
approved. As indicated above, EPA
believes that the section 110 elements
not connected with nonattainment plan
submissions and not linked to the area’s
nonattainment status are not applicable
requirements for purposes of review of
the State’s redesignation request. EPA
believes that approval of section 110 SIP
elements under the 1-hour ozone
standard satisfies the prerequisite for
approval of the ozone redesignation
request for purposes of attaining and
maintaining the 8-hour ozone standard.
EPA also believes that since the part D
requirements for the 8-hour ozone
standard did not become due prior to
Indiana’s submittal of the final,
complete redesignation request, they
also are not applicable requirements for
purposes of redesignation.
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D. Are the Air Quality Improvements in
the Central Indiana Area Due to
Permanent and Enforceable Emission
Reductions Resulting From the
Implementation of the Indiana SIP and
Applicable Federal Air Pollution
Control Regulations and Other
Permanent and Enforceable Emission
Reductions?
We believe that the State of Indiana
has adequately demonstrated that the
observed air quality improvements in
the Central Indiana Area are due to
permanent and enforceable emission
reductions resulting from the
implementation of the SIP, Federal
measures, and other State-adopted
measures. In making this demonstration,
the State has documented the changes
in VOC and NOX emissions from
anthropogenic (man-made or manbased) sources in the Central Indiana
Area and the changes in NOX emissions
from Electric Generating Units (EGUs)
Statewide occurring over the period of
1999–2005. This period includes 2002,
an ozone standard violation year, and
2005, the year in the middle of the
2004–2006 attainment period. The State
has also identified the emission control
regulations that have been implemented
in the Central Indiana Area and that
have contributed to attainment of the
ozone standard.
Table 2 summarizes the VOC and
NOX emissions totals from the
anthropogenic sources in the Central
Indiana Area for 1999, 2002, and 2005
as documented in the State’s
redesignation request. Table 3
summarizes the NOX emissions trend
for EGUs in the Central Indiana Area,
and Table 4 summarizes the NOX
emissions trend for EGUs Statewide.
TABLE 2.—VOC AND NOX EMISSIONS
TOTALS IN THE CENTRAL INDIANA
AREA IN TONS PER SUMMER DAY
Year
1999 ..............................
2002 ..............................
2005 ..............................
VOC
NOX
290.84
249.67
199.25
293.15
264.69
220.18
TABLE 3.—NOX EMISSIONS TOTALS
FOR EGUS IN THE CENTRAL INDIANA
AREA IN TONS PER OZONE SEASON
(APRIL–SEPTEMBER)
Year
1999
2000
2001
2002
2003
2004
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..........................
..........................
..........................
..........................
..........................
..........................
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31,815
25,028
27,394
22,661
17,984
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41665
1. What Is Required in an Ozone
326 IAC 8–4 Petroleum Sources
TABLE 3.—NOX EMISSIONS TOTALS
Maintenance Plan?
Controls
FOR EGUS IN THE CENTRAL INDIANA
AREA IN TONS PER OZONE SEASON 326 IAC 8–5 Miscellaneous Operations
Section 175A of the CAA sets forth
the required elements of air quality
Controls
(APRIL–SEPTEMBER)—Continued
326 IAC 8–6 Organic Solvent Emission
Limitations
2005 ..........................
10,591 326 IAC 8–8.1–1 Municipal Solid
Waste Landfills Not Located in Clark,
Floyd, Lake and Porter Counties
TABLE 4.—NOX EMISSIONS TOTALS
Controls.
Year
NOX emissions
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FOR EGUS IN INDIANA STATEWIDE
IN TONS PER OZONE SEASON
In addition, because EPA had initially
designated Marion County as
Year
NOX emissions
nonattainment under the 1-hour ozone
standard, VOC sources that existed after
1999 ..........................
149,827 July 1, 1990, in Marion County are also
2000 ..........................
133,881
2001 ..........................
136,052 subject to RACT rules. Sources in the
2002 ..........................
113,996 surrounding Counties (Boone, Hancock,
2003 ..........................
99,283 Hamilton, Johnson, Morgan, and Shelby
2004 ..........................
66,568 Counties) are subject to portions of 326
2005 ..........................
55,486 IAC 8–4 (326 IAC 8–4–4 through 8–4–
7 and 8–4–9) that do not apply
Information in the above tables
Statewide. These emission control
indicates that both VOC and NOX
requirements have led to reduced VOC
emissions significantly decreased in the emissions in the Central Indiana Area.
Central Indiana Area between 2002 and
Finally, the State notes that several
2005. In particular, the NOX emissions
nationwide rules have been
from EGUs in this area significantly
implemented (or will be implemented
decreased during this period due to the
in the near future), resulting in VOC and
implementation of EPA’s NOX SIP call
NOX emission reductions subsequent to
and acid rain control requirements. As
discussed further below, these emission 2002 in the Central Indiana Area and
Statewide. These emission reduction
reductions are primarily due to the
rules include: (a) Tier II emission
implementation of permanent and
standards for vehicles and gasoline
enforceable emission controls, which
sulfur standards; (b) heavy-duty diesel
are believed to have significantly
engine standard and low-sulfur diesel
contributed to the attainment of the 8fuel standards; and, (c) Clean Air Nonhour ozone standard in this area.
The Statewide NOX emission
road Diesel Rule. These emission
reductions for EGUs are believed to
reduction rules will provide additional
have significantly reduced ozone
emission reductions in the future.
transport into the Central Indiana Area,
The State commits to maintain
further reducing the peak ozone
existing emission control measures after
concentrations in this area. These
the redesignation of the Central Indiana
emission reductions are primarily due
Area to attainment of the 8-hour ozone
to the implementation of the State’s
NAAQS. If an emission control rule
NOX emission control rules stemming
must be changed, the State will submit
from EPA’s NOX SIP call and acid rain
the rule change as a requested SIP
control requirements. These NOX
revision to the EPA. IDEM maintains
emission control rules are permanent
that it has the legal authority and
and enforceable. We agree with the State
necessary resources to enforce any
that these NOX control rules have
violations of the existing emission
significantly reduced ozone levels in
control rules.
and ozone transport to the Central
Indiana Area.
E. Does the Central Indiana Area Have
Besides the NOX SIP call regulations,
a Fully Approvable Ozone Maintenance
IDEM notes that the following VOC
Plan Pursuant to Section 175A of the
emission control regulations have been
CAA?
implemented in the Central Indiana
In conjunction with its request to
Area (‘‘IAC’’ is the Indiana
redesignate the Central Indiana Area to
Administrative Code):
attainment of the 8-hour ozone NAAQS,
326 IAC 8–1–6 Best Available Control
Indiana submitted a SIP revision request
Technology (BACT) for non-specific
to provide for maintenance of the 8-hour
sources
326 IAC 8–2 Surface Coating Emission ozone NAAQS in the Central Indiana
Area through 2020, exceeding the 10
Limitations
326 IAC 8–3 Organic Solvent
year minimum maintenance period
Degreasing Operation Controls
required by the CAA.
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Sfmt 4702
maintenance plans for areas seeking
redesignation to attainment of a
NAAQS. Under section 175A, a
maintenance plan must demonstrate
continued attainment of the applicable
NAAQS for at least 10 years after the
Administrator approves the
redesignation to attainment. Eight years
after the redesignation, the State must
submit a revised maintenance plan
which demonstrates that maintenance of
the standard will continue for 10 years
following the initial 10-year
maintenance period. The maintenance
plan must commit the State to submit
this revised maintenance plan to the
EPA. To address the possibility of future
NAAQS violations, the maintenance
plan must contain such contingency
measures, with a schedule for
implementation, as EPA deems
necessary, to assure prompt correction
of any future NAAQS violations.
The September 4, 1992, John Calcagni
memorandum provides additional
guidance on the content of maintenance
plans. An ozone maintenance plan
should, at minimum, address the
following items: (1) The attainment VOC
and NOX emissions inventories; (2) a
maintenance demonstration showing
maintenance for the first 10 years of the
maintenance period; (3) a commitment
to maintain the existing monitoring
network; (4) factors and procedures to
be used for verification of continued
attainment; and, (5) a contingency plan
to prevent and/or correct a future
violation of the NAAQS.
2. What Are the Attainment Emission
Inventories for the Central Indiana
Area?
IDEM estimated future VOC and NOX
emissions for the Central Indiana Area
for 2010, 2015, and 2020 to compare
with the 2005 VOC and NOX emissions
for this area and to demonstrate
maintenance of the ozone standard in
this area. Future emissions were
estimated for point (significant
stationary sources), area (smaller point
and/or widely distributed stationary
sources), on-road mobile, and non-road
mobile sources for this area. To develop
the 2010, 2015, and 2020 emissions,
IDEM projected the 2002 base year
emissions applying various source
category-specific growth factors and
emission control factors or growth
estimates collected directly from the
sources. The following summarizes the
procedures and data sources used by
IDEM to derive the projected emissions.
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a. Point Sources
The primary source of point source
information for the base period, 2002,
was facility-specific emissions and
source activity data collected annually
by the State for inclusion in IDEM’s
annual emissions statement database.
This information includes emissions,
process rates, source operating
schedules, emissions control data, and
other relevant source information.
Emission growth factors and future
emission control factors provided by the
Lake Michigan Air Directors Consortium
(LADCO) were used to project the point
source VOC and non-EGU NOX
emissions to 2005, 2010, 2015, and
2020. The NOX emissions from EGUs
were projected based on the EGU NOX
emission budget contained in the
Indiana NOX rule.
b. Area Sources
Area sources are those sources which
are generally small, numerous, and have
not been inventoried as specific point,
mobile, or non-road mobile sources. The
emissions for these sources are generally
calculated using various surrogates,
such as population by county, estimates
of employees in various occupational
groups, etc., and grouped by general
source types. The area source emissions
are typically defined at the county level.
IDEM developed area source
emissions for a 2002 periodic emissions
inventory submitted to the EPA. The
surrogate data used to derive these
emissions were grown to 2005, 2010,
2015, and 2020. The projected
surrogates or other assumed annual
growth rates were used to calculate the
projected VOC and NOX emissions for
each area source type.
c. On-Road Mobile Sources
On-road mobile source emissions
were calculated using the MOBILE 6.2
emission factor model and other mobile
source data, including estimated traffic
levels and vehicle type and age
distribution data, extracted from the
area’s travel-demand model.
d. Non-Road Mobile Sources
Non-road mobile source emissions
were based on emissions in the 2002
National Emissions Inventory (NEI). The
2005, 2010, 2015, and 2020 non-road
mobile source emissions were grown
from the 2002 NEI emissions. To
address concerns about the accuracy of
the emissions derived for some of the
non-road mobile source categories in
EPA’s non-road emissions model,
LADCO contracted with several
companies to review the base data used
in the emissions model. A contractor
also estimated emissions for two nonroad source categories not included in
EPA’s non-road emissions model,
commercial marine vessels and
railroads. Recreational motorboat
emissions were significantly updated.
The equipment population and spatial
surrogate data for other source types
were also significantly updated. A new
non-road estimation model was also
provided by the EPA for the 2002
emissions analysis. The updated 2002
emissions were used to project the
emissions to 2005, 2010, 2015, and
2020.
3. Has the State Demonstrated
Maintenance of the Ozone Standard in
the Central Indiana Area?
As part of the redesignation request
submittal, IDEM requested a revision of
the Indiana SIP to incorporate an ozone
maintenance plan for the Central
Indiana Area as required under section
175A of the CAA. The maintenance plan
demonstrates maintenance of the 8-hour
ozone NAAQS through 2020 by
documenting the attainment year (2005)
and future VOC and NOX emissions.
Indiana has shown that VOC and NOX
emissions will remain below the
attainment year levels through 2020. An
ozone maintenance demonstration need
not be based on ozone modeling. See
Wall v. EPA, 265 F.3d 426 (6th Cir.
2001), Sierra Club v. EPA, 375 F.3d 537
(7th Cir. 2004). See also 66 FR 53094,
53099–53100 (October 19, 2001), and 68
FR 25430–25432 (May 12, 2003).
Table 5 summarizes the VOC and
NOX emissions projected to occur in the
entire Central Indiana Area during the
demonstrated maintenance period. The
State of Indiana chose 2020 as a
maintenance year to meet the 10-year
maintenance requirement of the CAA,
allowing several years for the EPA to
complete the redesignation rulemaking
process. The State also chose 2010 and
2015 as interim years to demonstrate
that VOC and NOX emissions will
remain below the attainment year levels
throughout the maintenance period.
TABLE 5.—VOC AND NOX EMISSIONS IN THE CENTRAL INDIANA AREA DURING THE
OZONE MAINTENANCE PERIOD IN TONS PER SUMMER DAY
Source sector
2005
2010
2015
2020
VOC Emissions
Area .................................................................................................................
Point .................................................................................................................
Non-Road Mobile .............................................................................................
On-Road Mobile ...............................................................................................
94.85
13.54
30.36
60.50
99.29
14.34
28.77
44.19
106.31
16.00
24.06
35.33
100.81
14.85
25.29
26.47
Total ..........................................................................................................
199.25
186.59
181.70
167.42
Area .................................................................................................................
Point .................................................................................................................
Non-Road Mobile .............................................................................................
On-Road Mobile ...............................................................................................
24.26
56.63
22.55
116.74
22.39
33.31
33.05
78.40
23.12
32.41
24.06
55.42
22.74
32.77
18.36
32.45
Total ..........................................................................................................
220.18
167.15
135.01
106.32
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NOX Emissions
IDEM notes that the State’s EGU NOX
emissions control rules stemming from
EPA’s NOX SIP call and CAIR, to be
implemented primarily after 2006, will
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further lower NOX emissions throughout
the State of Indiana and upwind of the
Central Indiana Area. This will result in
reduced ozone and ozone precursor
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transport into the Central Indiana Area,
and will support maintenance of the
8-hour ozone NAAQS in this area.
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The emissions projections for the
Central Indiana Area lead to the
conclusion that this area should
maintain the 8-hour ozone NAAQS
throughout the required 10-year
maintenance period and through 2020.
The projected decreases in local VOC
and local and regional NOX emissions
indicate that peak ozone levels in the
Central Indiana Area may further
decline during the maintenance period.
We conclude that IDEM has
successfully demonstrated that the
8-hour ozone standard will be
maintained in the Central Indiana Area.
4. What Is the Contingency Plan for the
Central Indiana Area?
Section 175A of the CAA requires that
a maintenance plan include such
contingency measures as EPA deems
necessary to assure that the State will
promptly correct a violation of the
NAAQS that might occur after
redesignation. The maintenance plan
must identify the contingency measures
to be considered for possible adoption,
a schedule and procedure for adoption
and implementation of the selected
contingency measures, and a time limit
for action by the State. The State should
also identify specific indicators to be
used to determine when the
contingency measures need to be
adopted and implemented. The
maintenance plan must include a
commitment that the State will continue
to implement all emission control
measures that were included in the SIP
before the redesignation of the area to
attainment. See section 175A(d) of the
CAA.
As required by the CAA, Indiana has
adopted a contingency plan to address
possible future ozone air quality
problems in the Central Indiana Area.
The contingency plan has two levels of
actions/responses depending on
whether a violation of the 8-hour ozone
standard is only threatened (Warning
Level Response) or has actually
occurred or appears to be imminent
(Action Level Response).
A Warning Level Response will be
triggered whenever an annual (1-year)
fourth-high monitored 8-hour ozone
concentration of 0.089 ppm occurs in a
single ozone season, or a 2-year average
fourth-high monitored 8-hour ozone
concentration of 0.085 ppm or higher
occurs within the Central Indiana
maintenance area (within the Central
Indiana Area). A Warning Level
Response will consist of a study to
determine whether the high ozone
concentration indicates a trend toward
higher ozone values or whether
emissions appear to be increasing. The
study will determine if the trend toward
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high ozone concentrations is likely to
continue. If so, the emission control
measures necessary to reverse the trend,
taking into consideration ease and
timing of implementation and economic
and social considerations, will be
adopted and implemented.
Implementation of necessary emission
controls will take place no later than 12
months from the conclusion of the most
recent ozone season (September 30).
An Action Level Response will be
triggered when a violation of the 8-hour
ozone standard is monitored, when the
three-year average annual fourth-high
daily maximum 8-hour concentration is
0.085 ppm or higher at any monitor, in
the Central Indiana Area. In the event
that an Action Level Response is
triggered and is not found to be due to
an exceptional event, malfunction, or
noncompliance with a permit condition
or rule requirement, IDEM will
determine the additional emission
control measures needed to assure
future attainment of the ozone NAAQS.
Emission control measures that can be
implemented in a short time will be
selected in order to be in place within
18 months from the close of the ozone
season in which the Action Level
Response is triggered.
Assuming that new emission controls
are needed, if a new emission control
measure is already promulgated and
scheduled to be implemented at the
Federal or State level and that control
measure is determined to be sufficient
to address the upward trend in ozone
concentrations, additional local
emission control measures may be
unnecessary. The State will submit to
EPA an analysis to demonstrate that the
proposed emission control measures are
adequate to return the area to attainment
or to correct the air quality trend.
The selection of emission control
measures for implementation will be
based on cost-effectiveness, emission
reduction potential, economic and
social considerations, and other factors
that IDEM deems appropriate. IDEM
will solicit input from interested and
affected persons in the maintenance
area prior to selecting appropriate
contingency measures. IDEM has not
specified a definitive list of measures
that will be considered and may
consider emission control measures not
included in the list of potential
emission control measures summarized
in the ozone maintenance plan.
The ozone maintenance plan lists the
following emission control measures as
possible contingency measures that
have been selected and reviewed by the
Central Indiana Air Quality Advisory
Group (a group of industrial
representatives, individuals, and local
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41667
government representatives from the
Central Indiana Area):
• Lower Reid vapor pressure gasoline;
• Broader geographic applicability of
existing emission control requirements;
• Tightening of RACT on existing
sources covered by EPA control
technique guidelines issued in response
to the 1990 Clean Air Act revisions;
• Application of RACT to smaller
existing sources;
• Vehicle inspection/maintenance
program;
• One or more transportation control
measure sufficient to achieve at least a
half of a percent (0.5 percent) reduction
of actual area-wide VOC emissions.
Transportation control measures will be
selected from the following based on the
factors discussed above and after
consultation with the affected local
governments:
(a) Trip reduction programs,
including employer-based
transportation management plans, areawide rideshare programs, work schedule
changes, and telecommuting;
(b) Transit improvements;
(c) Traffic flow improvements; and,
(d) Other new or innovative
transportation measures;
• Alternative fuel and diesel retrofit
programs for fleet vehicle operations;
• VOC or NOX emission offsets for
new and modified major sources;
• VOC or NOX emission offsets for
new and modified minor sources;
• Increase the ratio of emission offsets
required for new sources; and,
• VOC or NOX emission controls on
new minor sources.
No contingency measure will be
implemented without providing the
opportunity for public participation in
the selection process, during which the
relative costs and benefits of individual
emission control measures will be
evaluated.
5. Has the State Committed to Update
the Ozone Maintenance Plan in Eight
Years After the Redesignation of the
Central Indiana Area to Attainment of
the 8-Hour Ozone NAAQS?
As required by section 175A(b) of the
CAA, the State commits to review the
maintenance plan 8 years after
redesignation of the Central Indiana
Area and to submit a revised
maintenance plan to the EPA extending
the maintenance period for 10 years
beyond the initial 10-year maintenance
period.
We find Indiana’s ozone maintenance
demonstration, contingency plan, and
commitment to update the maintenance
plan to be acceptable.
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V. Has the State Adopted Acceptable
Motor Vehicle Emissions Budgets for
the End Year of the Ozone Maintenance
Period Which Can Be Used To Support
Conformity Determinations?
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A. How Are the Motor Vehicle Emission
Budgets Developed, and What Are the
Motor Vehicle Emission Budgets for the
Central Indiana Area?
Under the CAA, States are required to
submit, at various times, SIP revisions
and ozone maintenance plans for
applicable areas (for ozone
nonattainment areas and for areas
seeking redesignations to attainment of
the ozone standard or revising existing
ozone maintenance plans). These
emission control SIP revisions (e.g.,
reasonable further progress and
attainment SIP revisions), including
ozone maintenance plans, must create
MVEBs based on on-road mobile source
emissions that are allocated to highway
and transit vehicle use and that,
together with emissions from all other
sources in the area, will provide for
attainment or maintenance of the ozone
NAAQS.
Under 40 CFR part 93, MVEBs for an
area seeking a redesignation to
attainment of the NAAQS are
established for the last year of the
maintenance period (for the
maintenance demonstration year). The
MVEBs serve as ceilings on mobile
source emissions from an area’s planned
transportation system, and are used to
test planned transportation system
changes or projects to assure
compliance with the emission limits
assumed in the SIP. The MVEB concept
is further explained in the preamble to
the November 24, 1993, transportation
conformity rule (58 FR 62188). The
preamble also describes how to
establish the MVEBs in the SIP and how
to revise the MVEBs if needed.
Under section 176(c) of the CAA, new
transportation projects, such as the
construction of new highways, must
‘‘conform’’ to (i.e., be consistent with)
the part of the SIP that addresses
emissions from cars, trucks, and other
on-road vehicles. Conformity to the SIP
means that transportation activities
should not cause new air quality
standard violations, or delay timely
attainment of the NAAQS. If a
transportation plan does not conform,
most new transportation projects that
would expand the vehicle capacity of
the roadways cannot go forward.
Regulations at 40 CFR part 93 set forth
EPA’s policy, criteria, and procedures
for demonstrating and assuring
conformity of transportation activities to
a SIP.
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When reviewing SIP revisions
containing MVEBs, including
attainment strategies, rate-of-progress
plans, and maintenance plans, EPA
must find that the MVEBs are
‘‘adequate’’ for use in determining
transportation conformity. Once EPA
finds the submitted MVEBs to be
adequate for transportation conformity
purposes, the MVEBs are used by State
and Federal agencies in determining
whether proposed transportation
projects conform to the SIPs as required
by section 176(c) of the CAA. EPA’s
substantive criteria for determining the
adequacy of MVEBs are specified in 40
CFR 93.118(e)(4).
EPA’s process of determining
adequacy of MVEBs consists of three
basic steps: (1) Providing public
notification of a SIP submission; (2)
providing the public the opportunity to
comment on the MVEBs during a public
comment period; and (3) making a
finding of adequacy. The process of
determining the adequacy of submitted
SIP MVEBs was initially outlined in
EPA’s May 14, 1999, guidance,
‘‘Conformity Guidance on
Implementation of March 2, 1999,
Conformity Court Decision.’’ This
guidance was finalized in the
Transportation Conformity Rule
Amendments for the ‘‘New 8-Hour
Ozone and PM2.5 National Ambient Air
Quality Standards and Miscellaneous
Rule Amendments—Response to Court
Decision and Additional Rule Change’’
published on July 1, 2004 (69 FR
40004). EPA follows this guidance and
rulemaking in making its adequacy
determinations.
The Transportation Conformity Rule,
in 40 CFR 93.118(f), provides for
adequacy findings through two
mechanisms. First, 40 CFR 93.118(f)(1)
provides for posting a notice to the EPA
conformity Web site at: https://
www.epa.gov/otaq/Stateresources/
transconf/adequacy.htm and providing
a 30-day public comment period.
Second, a mechanism is described in 40
CFR 93.118(f)(2) which provides that
EPA can review the adequacy of an
implementation plan submission
simultaneously with its review of the
implementation plan itself.
The Central Indiana Area ozone
maintenance plan contains VOC and
NOX MVEBs for 2006 and 2020. An
interagency group of consultation
partners chose to include MVEBs for
2006 to assist in streamlining the
transportation conformity process. The
year 2006 was chosen because it
represents one of the years the Central
Indiana Area attained the 8-hour ozone
standard and because the travel demand
models used in transportation planning
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contain a defined mobile source
network for 2006.
The 2006 MVEBs are 54.32 tons VOC/
day and 106.19 tons NOX/day. The 2020
MVEBs are 29.52 tons VOC/day and
35.69 tons NOX/day. Note that the 2020
MVEBs contain safety margins
(emission levels exceeding the on-road
mobile source emissions levels actually
projected for the area and included in
the maintenance demonstration). See
the 2020 on-road mobile source
emissions specified in Table 5 above.
The State is applying safety margins
in specifying the 2020 MVEBs to
accommodate the assumptions and
associated potential estimate errors that
are factored into the projection of future
emission estimates. Since assumptions
change over time or are shown to be
incorrect, some errors may actually
occur in estimated future emissions.
Therefore, it is reasonable, if not
necessary, to incorporate safety margins
into the setting of MVEBs.
A ‘‘margin of safety’’ is the difference
between the attainment level emissions
from all sources and the projected levels
of emissions from all sources in the
maintenance plan for the maintenance
year. As noted in Table 5 above, the
Central Indiana Area is projected to
have a VOC margin of safety of 31.83
tons/day and a NOX margin of safety of
113.86 tons/day in 2020. These margins
of safety significantly exceed the safety
margins incorporated into the 2020
MVEBs (the 2020 MVEB VOC safety
margin is 3.05 tons/day and the 2020
MVEB NOX safety margin is 3.24 tons/
day, the differences between the 2020
MVEBs and the projected on-road
mobile source emissions). Therefore, the
safety margins incorporated into the
2020 MVEBs will not threaten
maintenance of the 8-hour ozone
standard in the Central Indiana Area.
No safety margins were applied to the
2006 MVEBs. These MVEBs are the onroad mobile emission estimates for this
year.
B. Are the MVEBs Approvable?
EPA, through this rulemaking, is
proposing to approve the 2006 and 2020
MVEBs for use in demonstrating
transportation conformity in the Central
Indiana Area because EPA has
determined that the MVEBs are
consistent with the emission control
measures and future emissions
projected in the SIP and because the
Central Indiana Area can maintain
attainment of the 8-hour ozone NAAQS
for the required maintenance period
with on-road mobile source emissions at
the levels of the MVEBs. The VOC and
NOX MVEBs are approvable because
they maintain the total emissions for the
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Central Indiana Area at or below the
attainment year emission levels, as
required by the transportation
conformity regulations.
VI. What Are the Effects of EPA’s
Proposed Actions?
Approval of the redesignation request
would change the official designation of
Boone, Hamilton, Hancock, Hendricks,
Johnson, Madison, Marion, Morgan, and
Shelby Counties, Indiana for the 8-hour
ozone NAAQS, found at 40 CFR part 81,
from nonattainment to attainment. Final
rulemaking approving the redesignation
request would incorporate into the
Indiana SIP a plan for maintaining the
ozone NAAQS through 2020 in these
Counties. The maintenance plan
includes contingency measures to
remedy possible future violations of the
8-hour ozone NAAQS, and establishes
2006 and 2020 MVEBs for these
counties.
VII. Statutory and Executive Order
Reviews
Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, September 30, 1993), this action
is not a ‘‘significant regulatory action’’,
and therefore, is not subject to review by
the Office of Management and Budget.
Paperwork Reduction Act
This proposed 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.).
rmajette on PROD1PC64 with PROPOSALS
Regulatory Flexibility Act
This proposed action merely proposes
to approve State law as meeting Federal
requirements and imposes no additional
requirements beyond those imposed by
State law. Accordingly, the
Administrator certifies that this
proposed 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.).
Unfunded Mandates Reform Act
Because this rule proposes to approve
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).
Executive Order 13132: Federalism
This action also does not have
Federalism implications because it does
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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
proposes to approve a State rule
implementing a Federal standard, and
does not alter the relationship or the
distribution of power and
responsibilities established in the Clean
Air Act.
Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This proposed 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).
Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
This proposed 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.
Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
Because it is not a ‘‘significant
regulatory action’’ under Executive
Order 12866 or a ‘‘significant regulatory
action,’’ 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).
National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (NTTAA), 15 U.S.C. 272,
requires Federal agencies to use
technical standards that are developed
or adopted by voluntary consensus to
carry out policy objectives, so long as
such standards are not inconsistent with
applicable law or otherwise impractical.
In reviewing SIP submissions, EPA’s
role is to approve State choices,
provided that they meet the criteria of
the Clean Air Act. Absent a prior
existing requirement for the State to use
voluntary consensus standards, EPA has
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41669
no authority to disapprove a SIP
submission for failure to use such
standards, and it would thus be
inconsistent with applicable law for
EPA to use voluntary consensus
standards in place of a program
submission that otherwise satisfies the
provisions of the Clean Air Act.
Therefore, the requirements of section
12(d) of the NTTA do not apply.
List of Subjects
40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
regulations, Nitrogen dioxide, Ozone,
Volatile organic compounds.
40 CFR Part 81
Air pollution control, Environmental
protection, National parks, Wilderness
areas.
Dated: July 23, 2007.
Bharat Mathur,
Acting Regional Administrator, Region 5.
[FR Doc. E7–14741 Filed 7–30–07; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 52 and 97
[EPA–R05–OAR–2007–0405; FRL–8446–5]
Approval of Implementation Plans;
Wisconsin; Clean Air Interstate Rule
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
SUMMARY: EPA is proposing to partially
approve and partially disapprove a
revision to the Wisconsin State
Implementation Plan (SIP) submitted on
June 19, 2007. This revision
incorporates provisions related to the
implementation of EPA’s Clean Air
Interstate Rule (CAIR), promulgated on
May 12, 2005, and subsequently revised
on April 28, 2006, and December 13,
2006, and the CAIR Federal
Implementation Plan (FIP) which
concerns sulfur dioxide (SO2), oxides of
nitrogen (NOX) annual, and NOX ozone
season emissions for the State of
Wisconsin, promulgated on April 28,
2006, and subsequently revised
December 13, 2006. EPA is not
proposing to make any changes to the
CAIR FIP, but is proposing, to the extent
EPA approves Wisconsin’s SIP revision,
to amend the appropriate appendices in
the CAIR FIP trading rules simply to
note that approval.
The SIP revision that EPA is
proposing to approve is an abbreviated
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Agencies
[Federal Register Volume 72, Number 146 (Tuesday, July 31, 2007)]
[Proposed Rules]
[Pages 41658-41669]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-14741]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 52 and 81
[EPA-R05-OAR-2007-0173; FRL-8448-1]
Determination of Attainment, Approval and Promulgation of
Implementation Plans and Designation of Areas for Air Quality Planning
Purposes; Indiana; Redesignation of Central Indiana To Attainment of
the 8-Hour Ozone Standard
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
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SUMMARY: On March 26, 2007, the Indiana Department of Environmental
Management (IDEM) submitted a request for EPA approval of a
redesignation of Boone, Hamilton, Hancock, Hendricks, Johnson, Madison,
Marion, Morgan, and Shelby Counties (the Central Indiana Area) to
attainment of the 8-hour ozone National Ambient Air Quality Standard
(NAAQS). IDEM also requested EPA approval of an ozone maintenance plan
for this area as a revision of the Indiana State Implementation Plan
(SIP). EPA proposes to determine that the Central Indiana Area has
attained the 8-hour ozone NAAQS. EPA proposes to approve Indiana's
request to redesignate the Central Indiana Area to attainment of the 8-
hour ozone NAAQS and to approve the State's ozone maintenance plan for
this area as a revision of the Indiana SIP. Finally, EPA proposes to
approve Volatile Organic Compounds (VOC) and Nitrogen Oxides
(NOX) Motor Vehicle Emission Budgets (MVEBs) for the Central
Indiana Area, as supported by the ozone maintenance plan for this area,
for purposes of transportation conformity determinations.
DATES: Comments must be received on or before August 30, 2007.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R05-
OAR-2007-0173, by one of the following methods:
https://www.regulations.gov: Follow the on-line
instructions for submitting comments.
E-mail: mooney.john@epa.gov.
Fax: (312) 886-5824.
Mail: John M. Mooney, Chief, Criteria Pollutant Section,
Air Programs Branch (AR-18J), U.S. Environmental Protection Agency, 77
West Jackson Boulevard, Chicago, Illinois 60604.
Hand Delivery: John M. Mooney, Chief, Criteria Pollutant
Section, Air Programs Branch (AR-18J), U.S. Environmental Protection
Agency, 77 West Jackson Boulevard, Chicago, Illinois. Such deliveries
are only accepted during the Regional Office's normal hours of
operation, and special arrangements should be made for deliveries of
boxed information. The Regional Office's official hours of operation
are Monday through Friday, 8:30 a.m. to 4:30 p.m., excluding Federal
holidays.
Instructions: Direct your comments to Docket ID No. EPA-R05-OAR-
2007-0173. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI, or otherwise protected, through www.regulations.gov
or e-mail. The www.regulations.gov Web site is an ``anonymous access''
system, which means EPA will not know your identity or contact
information unless you provide it in the body of your comment. If you
send an e-mail comment directly to EPA without going through
www.regulations.gov, your e-mail address will be automatically captured
and included as part of the comment that is placed in the public docket
and made available on the Internet. If you submit an electronic
comment, EPA recommends that you include your name and other contact
information in the body of your comment and with any disk or CD-ROM you
submit. If EPA cannot read your comment due to technical difficulties
and cannot contact you for clarification, EPA may not be able to
consider your comment. Electronic files should avoid the use of special
characters and any form of encryption, and should be free of any
defects or viruses. For additional instructions on submitting comments,
go to section I of the SUPPLEMENTARY INFORMATION section of this
document.
Docket: All documents in the docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hardcopy.
Publicly available docket materials are available either electronically
in www.regulations.gov or in hardcopy at the Environmental Protection
Agency, Region 5, Air and Radiation Division, 77 West Jackson
Boulevard, Chicago,
[[Page 41659]]
Illinois 60604. This facility is open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding Federal holidays. It is recommended
that you telephone Edward Doty, Environmental Scientist, at (312) 886-
6057, before visiting the Region 5 office.
FOR FURTHER INFORMATION CONTACT: Edward Doty, Environmental Scientist,
Criteria Pollutant Section, Air Programs Branch (AR-18J), Environmental
Protection Agency, Region 5, 77 West Jackson Boulevard, Chicago,
Illinois 60604, (312) 886-6057, doty.edward@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this proposed rule whenever
``we,'' ``us,'' or ``our'' is used, we mean the EPA. This supplementary
information section is arranged as follows:
I. What Action is EPA Proposing to Take?
II. What is the Background for This Action?
A. General Background Information
B. What is the Impact of December 22, 2006, and June 8, 2007,
United States Court of Appeals Decisions Regarding EPA's Phase 1
Implementation Rule?
1. Summary of Court Decision
2. Requirements Under the 8-Hour Ozone Standard
3. Requirements Under the 1-Hour Ozone Standard
III. What are the Criteria for Redesignations to Attainment?
IV. What Are EPA's Analyses and Opinions of the State's Requests and
What Are the Bases for EPA's Proposed Action?
A. Has the Central Indiana Area Attained the 8-Hour Ozone NAAQS?
B. Has the State of Indiana Committed to Maintain the Ozone
Monitoring System in the Central Indiana Area?
C. Have the Central Indiana Area and the State of Indiana Met
All of the Applicable Requirements of Section 110 and Part D of the
Clean Air Act, and Does the Central Indiana Area Have a Fully
Approved SIP Under Section 110(k) of the Clean Air Act?
1. The Central Indiana Area Has Met All Applicable Requirements
of Section 110 and Part D of the Clean Air Act
a. Section 110 and General SIP Requirements
b. Part D SIP Requirements
c. Part D, Subpart 1 SIP Requirements
d. Section 176 Conformity Requirements
e. Part D New Source Review (NSR) Requirements
2. The Central Indiana Area Has a Fully Approved SIP Under
Section 110(k) of the Clean Air Act (CAA)
D. Are the Air Quality Improvements in the Central Indiana Area
Due to Permanent and Enforceable Emission Reductions Resulting from
the Implementation of the Indiana SIP and Applicable Federal Air
Pollution Control Regulations and Other Permanent and Enforceable
Emission Reductions?
E. Does the Central Indiana Area Have a Fully Approvable Ozone
Maintenance Plan Pursuant to Section 175A of the CAA?
1. What Is Required in an Ozone Maintenance Plan?
2. What Are the Attainment Emission Inventories for the Central
Indiana Area?
a. Point Sources
b. Area Sources
c. On-Road Mobile Sources
d. Non-Road Mobile Sources
3. Has the State Demonstrated Maintenance of the Ozone Standard
in the Central Indiana Area?
4. What Is the Contingency Plan for the Central Indiana Area?
5. Has the State Committed to Update the Ozone Maintenance Plan
in Eight Years After the Redesignation of the Central Indiana Area
to Attainment of the 8-Hour Ozone NAAQS?
V. Has the State Adopted Acceptable Motor Vehicle Emissions Budgets
for the End Year of the Ozone Maintenance Period Which Can Be Used
to Support Conformity Determinations?
A. How Are the Motor Vehicle Emission Budgets Developed, and
What Are the Motor Vehicle Emission Budgets for the Central Indiana
Area?
B. Are the MVEBs Approvable?
VI. What Are the Effects of EPA's Proposed Actions?
VII. Statutory and Executive Order Reviews
I. What Action Is EPA Proposing to Take?
We are proposing to take several related actions for the Central
Indiana Area (Boone, Hamilton, Hancock, Hendricks, Johnson, Madison,
Marion, Morgan, and Shelby Counties). First, we are proposing to
determine that this area has attained the 8-hour ozone NAAQS. Second,
we are proposing to approve Indiana's ozone maintenance plan for this
area as a revision of the Indiana SIP. The maintenance plan is designed
to keep this area in attainment of the 8-hour ozone NAAQS through 2020.
Third, as supported by and consistent with the ozone maintenance plan,
we are proposing to approve the 2006 and 2020 VOC and NOX
MVEBs (54.32 tons VOC/day and 106.19 tons NOX/day in 2006,
and 29.52 tons VOC/day and 35.69 tons NOX/day in 2020) for
the nine counties in the Central Indiana Area for transportation
conformity determination purposes. Finally, we are proposing to approve
the redesignation of the Central Indiana Area to attainment of the 8-
hour ozone NAAQS.
II. What Is the Background for This Action?
A. General Background Information
EPA has determined that ground-level ozone is detrimental to human
health. On July 18, 1997, EPA promulgated an 8-hour ozone NAAQS (62 FR
38856) of 0.08 parts per million parts of air (0.08 ppm) (80 parts per
billion (ppb)).\1\ This 8-hour ozone standard replaced a prior 1-hour
ozone NAAQS, which was promulgated on February 8, 1979 (44 FR 8202),
and which EPA revoked on June 15, 2005 (69 FR 23858).
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\1\ This standard is violated in an area when any ozone monitor
in the area (or in its nearby downwind environs) records 8-hour
ozone concentrations with a three-year average of the annual fourth-
highest daily maximum 8-hour ozone concentrations equaling or
exceeding 85 ppb. See 40 CFR 50.10.
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Ground-level ozone is generally not emitted directly by emission
sources. Rather, emitted NOX and VOC react in the presence
of sunlight to form ground-level ozone along with other secondary
compounds. NOX and VOC are referred to as ``ozone
precursors.'' Control of ground-level ozone concentrations is achieved
through controlling VOC and NOX emissions.
Section 107 of the CAA requires EPA to designate as nonattainment
any area that violates the 8-hour ozone NAAQS. A Federal Register
notice promulgating 8-hour ozone designations and classifications was
published on April 30, 2004 (69 FR 23857).
The CAA contains two sets of provisions--subpart 1 and subpart 2--
that address planning and emission control requirements for
nonattainment areas. Both are found in title I, part D of the CAA.
Subpart 1 contains general, less prescriptive requirements for all
nonattainment areas for any pollutant governed by a NAAQS. Subpart 2
contains more specific requirements for certain ozone nonattainment
areas, and applies to ozone nonattainment areas classified under
section 181 of the CAA.
In the April 30, 2004, designation rulemaking, EPA divided 8-hour
ozone nonattainment areas into the categories of subpart 1
nonattainment (``basic'' nonattainment) and subpart 2 nonattainment
(``classified'' nonattainment). EPA based this division on the areas'
8-hour ozone design values (i.e., on the three-year averages of the
annual fourth-highest daily maximum 8-hour ozone concentrations at the
worst-case monitoring sites in the designated areas) and on their 1-
hour ozone design values (i.e., on the fourth-highest daily maximum 1-
hour ozone concentrations over the three-year period at the worst-case
monitoring sites in the designated areas) \2\ using ozone data from the
period of 2001-2003. EPA classified 8-hour ozone nonattainment areas
with 1-hour ozone design values equaling or
[[Page 41660]]
exceeding 121 ppb as subpart 2, classified nonattainment areas. EPA
classified all other 8-hour nonattainment areas as subpart 1, basic
nonattainment areas. The basis for area classification was defined in a
separate April 30, 2004, final rule (the Phase 1 implementation rule)
(69 FR 23951). In the April 30, 2004, ozone designation/classification
rulemaking, EPA designated the Central Indiana Area, as a subpart 1,
basic nonattainment area for the 8-hour ozone NAAQS.
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\2\ The 8-hour ozone design value and the 1-hour ozone design
value for each area were not necessarily recorded at the same
monitoring site. The worst-case monitoring site for each ozone
concentration averaging time was considered for each area.
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On March 26, 2007, the State of Indiana requested redesignation of
the Central Indiana Area to attainment of the 8-hour ozone NAAQS based
on ozone data collected in this area during the period of 2004-2006.
B. What Is the Impact of December 22, 2006, and June 8, 2007, United
States Court of Appeals Decisions Regarding EPA's Phase 1
Implementation Rule?
1. Summary of Court Decision
On December 22, 2006, the U.S. Court of Appeals for the District of
Columbia Circuit (D.C. Circuit) vacated EPA's Phase 1 implementation
rule for the 8-hour ozone standard (69 FR 23951, April 30, 2004). South
Coast Air Quality Management Dist. v. EPA, 472 F.3d 882 (DC Cir. 2006).
On June 8, 2007, in South Coast Air Quality Management Dist. v. EPA,
Docket No. 04-1201, in response to several petitions for rehearing, the
DC Circuit clarified that the Phase 1 rule was vacated only with regard
to those parts of the rule that had been successfully challenged.
Therefore, the Phase 1 rule provisions related to classifications for
areas currently classified under subpart 2 of title I, part D of the
CAA as 8-hour nonattainment areas, the 8-hour attainment dates and the
timing of emissions reductions needed for attainment of the 8-hour
ozone NAAQS remain effective. The June 8th decision left intact the
Court's rejection of EPA's reasons for implementing the 8-hour standard
in certain nonattainment areas under subpart 1 in lieu of subpart 2. By
limiting the vacatur, the Court let stand EPA's revocation of the 1-
hour ozone standard and those anti-backsliding provisions of the Phase
1 rule that had not been successfully challenged. The June 8th decision
reaffirmed the December 22, 2006, decision that EPA had improperly
failed to retain measures required for 1-hour nonattainment areas under
the anti-backsliding provisions of the regulations: (1) Nonattainment
area New Source Review (NSR) requirements based on an area's 1-hour
nonattainment classification; (2) section 185 penalty fees for 1-hour
severe and extreme nonattainment areas; and, (3) measures to be
implemented pursuant to section 172(c)(9) or 182(c)(9) of the CAA, on
the contingency of an area not making reasonable further progress
toward attainment of the 1-hour NAAQS, or for failure to attain that
NAAQS. In addition, the June 8th decision clarified that the Court's
reference to conformity requirements for anti-backsliding purposes was
limited to requiring the continued use of 1-hour motor vehicle emission
budgets until 8-hour budgets are available for 8-hour conformity
determinations, which is already required under EPA's conformity
regulations. The Court, thus, clarified that 1-hour conformity
determinations are not required for anti-backsliding purposes.
This section sets forth EPA's views on the potential effect of the
Court's rulings on this proposed redesignation action. For the reasons
set forth below, EPA does not believe that the Court's rulings alter
any requirements relevant to this redesignation action so as to
preclude redesignation, and do not prevent EPA from proposing or
ultimately finalizing this redesignation. EPA believes that the Court's
December 22, 2006, and June 8, 2007, decisions impose no impediment to
moving forward with redesignation of this area to attainment, because
even in light of the Court's decisions, redesignation is appropriate
under the relevant redesignation provisions of the CAA and longstanding
policies regarding redesignation requests.
2. Requirements Under the 8-Hour Ozone Standard
With respect to the 8-hour ozone standard, EPA notes that the
Court's ruling rejected EPA's reasons for classifying areas under
subpart 1 for the 8-hour ozone standard, and remanded that matter to
the EPA. Consequently, it is possible that the Central Indiana Area
could, during a remand to EPA, be reclassified under subpart 2.
Although any future decision by EPA to classify this area under subpart
2 might trigger additional future requirements for this area, EPA
believes that this does not mean that redesignation of the area cannot
now go forward. This belief is based upon (1) EPA's longstanding policy
of evaluating redesignation requests in accordance with the
requirements due at the time the redesignation request is submitted;
and, (2) consideration of the inequity of applying retroactively any
future requirements.
First, at the time the redesignation request was submitted by the
State, the Central Indiana Area was classified under subpart 1 and was
obligated to meet only subpart 1 requirements. Under EPA's longstanding
interpretation of section 107(d)(3)(E) of the CAA, to qualify for
redesignation, states requesting redesignation to attainment must meet
only the relevant SIP requirements that came due prior to the submittal
of a complete redesignation request. September 4, 1992, Calcagni
memorandum (``Procedures for Processing Requests to Redesignate Areas
to Attainment,'' Memorandum from John Calcagni, Director, Air Quality
Management Division). See also September 17, 1993, Michael Shapiro
memorandum, 60 FR 12459, 12465-66 (March 7, 1995) (redesignation of
Detroit-Ann Arbor), and Sierra Club v. EPA, 375 F.3d 537 (7th Cir.
2004), which upheld this interpretation. See, e.g. also 68 FR 25418,
25424, 25427 (May 12, 2003) (redesignation of St. Louis).
Moreover, it would be inequitable to retroactively apply any new
SIP requirements that were not applicable at the time the redesignation
request was submitted. The DC Circuit has recognized the inequity in
such retroactive rulemaking. See Sierra Club v. Whitman, 285 F.3d 63
(DC Cir. 2002), in which the DC Circuit upheld a District Court's
ruling refusing to make retroactive an EPA determination of
nonattainment that was past the statutory due date. Such a
determination would have resulted in the imposition of additional
requirements on the area. The Court stated: ``Although EPA failed to
make the nonattainment determination within the statutory timeframe,
Sierra Club's proposed solution only makes the situation worse.
Retroactive relief would likely impose large costs on the States, which
would face fines and suits for not implementing air pollution
prevention plans in 1997, even though they were not on notice at the
time.'' Id. at 68. Similarly, here it would be unfair to penalize the
area by applying to it, for purposes of redesignation, additional SIP
requirements under subpart 2 that were not in effect at the time the
State submitted its redesignation request.
3. Requirements Under the 1-Hour Ozone Standard
With respect to the requirements under the 1-hour ozone standard,
we note that the Central Indiana Area was made up of two types of areas
relative to the 1-hour ozone standard at the time the 8-hour ozone
standard was promulgated. First, Marion County was an ozone maintenance
area, having been previously designated as a nonattainment area under
the 1-hour
[[Page 41661]]
ozone standard and having subsequently been redesignated to attainment
of the 1-hour ozone standard. Second, all remaining Counties in the
Central Indiana Area were designated as attainment/unclassifiable areas
under the 1-hour ozone standard, having never been designated as 1-hour
ozone nonattainment areas. The Court's ruling on EPA's Phase 1 rule
does not impact redesignation requests for either of these types of
areas.
First, because Boone, Hamilton, Hancock, Hendricks, Johnson,
Madison, Morgan, and Shelby Counties were designated as attainment/
unclassifiable under the 1-hour ozone standard, and were never
designated nonattainment for the 1-hour ozone standard, there are no
outstanding 1-hour ozone nonattainment requirements that these counties
would be required to meet. Thus, we find that the Court's ruling does
not result in any additional 1-hour requirements for purposes of
redesignation.
Second, with respect to the 1-hour ozone standard requirements for
Marion County, this area was an attainment area subject to a Clean Air
Act section 175A maintenance plan under the 1-hour ozone standard. The
Court's decisions do not impact redesignation requests for these types
of areas, except to the extent that the Court in its June 8th decision
clarified that for those areas with 1-hour motor vehicle emissions
budgets in their 1-hour ozone maintenance plans, anti-backsliding
requires that those 1-hour budgets must be used for 8-hour conformity
determinations until replaced by 8-hour budgets. To meet this
requirement, conformity determinations in such areas must continue to
comply with the applicable requirements of EPA's conformity regulations
at 40 CFR part 93. The Court clarified that 1-hour conformity
determinations are not required for anti-backsliding purposes.
With respect to the three other anti-backsliding provisions for the
1-hour ozone standard that the Court found were not properly retained,
Marion County is an attainment area subject to a maintenance plan for
the 1-hour ozone standard, and the NSR, contingency measures (pursuant
to section 172(c)(9) or 182(c)(9)), and fee provision requirements no
longer apply to this area because it has been redesignated to
attainment of the 1-hour ozone standard.
Thus, the decision in South Coast Air Quality Management Dist.
should not preclude EPA from finalizing the redesignation of this area.
III. What Are the Criteria for Redesignations to Attainment?
The CAA provides the basic requirements for redesignating a
nonattainment area to attainment. Specifically, section 107(d)(3)(E) of
the CAA authorizes the EPA to redesignate an area to attainment of the
NAAQS provided that: (1) The Administrator determines that the area has
attained the applicable NAAQS based on current air quality data; (2)
the Administrator has fully approved an applicable SIP for the area
under section 110(k) of the CAA; (3) the Administrator determines that
the improvement in air quality is due to permanent and enforceable
emission reductions resulting from implementation of the applicable
SIP, Federal air pollution control regulations, and other permanent and
enforceable emission reductions; (4) the Administrator has fully
approved a maintenance plan for the area meeting the requirements of
section 175A of the CAA; and, (5) the State containing the area has met
all requirements applicable to the area under section 110 and part D of
the CAA.
EPA provided guidance on redesignations in the General Preamble for
the Implementation of Title I of the CAA Amendments of 1900 on April
16, 1992 (57 FR 13498), and supplemented this guidance on April 28,
1992 (57 FR 18070). The two main policy guidelines affecting the review
of ozone redesignation requests are the following: ``Procedures for
Processing Requests to Redesignate Areas to Attainment,'' Memorandum
from John Calcagni, Director, Air Quality Management Division,
September 4, 1992 (the September 4, 1992 Calcagni memorandum); and,
``Reasonable Further Progress, Attainment Demonstration, and Related
Requirements for Ozone Nonattainment Areas Meeting the Ozone National
Ambient Air Quality Standard,'' Memorandum from John S. Seitz,
Director, Office of Air Quality Planning and Standards, May 10, 1995
(the May 10, 1995 Seitz memorandum). For additional policy guidelines
used in the review of ozone redesignation requests, see our proposed
rule for the redesignation of the Evansville, Indiana ozone
nonattainment area at 70 FR 53606 (September 9, 2005).
IV. What Are EPA's Analyses and Opinions of the State's Requests and
What Are the Bases for EPA's Proposed Action?
EPA is proposing to: (1) Determine that the Central Indiana Area
has attained the 8-hour ozone standard; (2) approve the ozone
maintenance plan for the Central Indiana Area and the VOC and
NOX MVEBs supported by the maintenance plan; and, (3)
approve the redesignation of the Central Indiana Area to attainment of
the 8-hour ozone NAAQS. The bases for our proposed determination and
approvals follow.
A. Has the Central Indiana Area Attained the 8-Hour Ozone NAAQS?
For ozone, an area may be considered to be attaining the 8-hour
ozone NAAQS if there are no violations of the NAAQS, as determined in
accordance with 40 CFR 50.10 and appendix I, based on the most recent
three complete, consecutive calendar years of quality-assured air
quality monitoring data at all ozone monitoring sites in the area and
in its nearby downwind environs. To attain this standard, the average
of the annual fourth-high daily maximum 8-hour average ozone
concentrations measured and recorded at each monitor (the monitoring
site's ozone design value) within the area and in its nearby downwind
environs over the most recent three-year period must not exceed the
ozone standard. Based on an ozone data rounding convention described in
40 CFR 50, appendix I, the 8-hour ozone standard is attained if the
area's ozone design value \3\ is 0.084 ppm (84 ppb) or less. The data
must be collected and quality-assured in accordance with 40 CFR 58, and
must be recorded in EPA's Air Quality System (AQS). The ozone monitors
generally should have remained at the same locations for the duration
of the monitoring period required to demonstrate attainment (for three
years or more). The data supporting attainment of the standard must be
complete in accordance with 40 CFR 50, appendix I.
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\3\ The worst-case monitoring site-specific ozone design value
in the area and in its nearby downwind environs.
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As part of the ozone redesignation request, IDEM submitted
summarized 2004-2006 peak 8-hour ozone monitoring data for the Central
Indiana Area. These ozone concentrations are part of the quality-
assured ozone data recorded in the Air Quality System. The annual
fourth-high 8-hour daily maximum concentrations for each year, along
with the three-year averages,\4\ are summarized in Table 1.
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\4\ Three-year averages are specified for the last year of each
three-year period and specify the monitoring site design values.
[[Page 41662]]
Table 1.--Annual Fourth-High Daily Maximum 8-Hour Ozone Concentrations in Parts per Million (ppm)
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Percent
Site Id County Site name Year observations Fourth-high Three-year
ozone season concentration average
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18-011-0001............................. Boone..................... Whitestown................ 2004 100 0.072 ..............
Whitestown................ 2005 100 0.082 ..............
Whitestown................ 2006 100 0.080 0.078
18-057-1001............................. Hamilton.................. Noblesville............... 2004 99 0.075 ..............
Noblesville............... 2005 99 0.087 ..............
Noblesville............... 2006 100 0.077 0.079
18-059-0003............................. Hancock................... Fortville................. 2004 100 0.072 ..............
Fortville................. 2005 99 0.080 ..............
Fortville................. 2006 99 0.075 0.075
18-063-0004............................. Hendricks................. Avon...................... 2004 100 0.071 ..............
Avon...................... 2005 100 0.078 ..............
Avon...................... 2006 100 0.073 0.074
18-081-0002............................. Johnson................... Trafalgar................. 2004 100 0.073 ..............
Trafalgar................. 2005 100 0.077 ..............
Trafalgar................. 2006 98 0.078 0.076
18-095-0010............................. Madison................... Emporia................... 2004 100 0.072 ..............
Emporia................... 2005 100 0.078 ..............
Emporia................... 2006 97 0.073 0.074
18-097-0050............................. Marion.................... Ft. Benjamin Harrison..... 2004 99 0.073 ..............
Ft. Benjamin Harrison..... 2005 99 0.080 ..............
Ft. Benjamin Harrison..... 2006 100 0.076 0.076
18-097-0057............................. Marion.................... Harding St................ 2004 100 0.066 ..............
Harding St................ 2005 100 0.081 ..............
Harding St................ 2006 93 0.076 0.074
18-097-0042............................. Marion.................... Mann Road................. 2004 99 0.065 ..............
Mann Road................. 2005 100 0.076 ..............
Mann Road................. 2006 98 0.074 0.071
18-097-0073............................. Marion.................... Naval Air Warfare Center.. 2004 100 0.071 ..............
Naval Air Warfare Center.. 2005 100 0.080 ..............
Naval Air Warfare Center.. 2006 93 0.072 0.074
18-109-0005............................. Morgan.................... Monrovia.................. 2004 99 0.072 ..............
Monrovia.................. 2005 100 0.078 ..............
Monrovia.................. 2006 100 0.077 0.075
18-145-0001............................. Shelby.................... Fairland.................. 2004 99 0.071 ..............
Fairland.................. 2005 100 0.080 ..............
Fairland.................. 2006 98 0.073 0.074
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The above data show that, during the period of 2004-2006, no
violations of the 8-hour ozone standard were recorded in the Central
Indiana Area. In addition, we find that the ozone data for the years
considered meet data completeness requirements of 40 CFR part 50,
appendix I. Based on these data, we conclude and find that the Central
Indiana Area has attained the 8-hour ozone NAAQS.
B. Has the State of Indiana Committed To Maintain the Ozone Monitoring
System in the Central Indiana Area?
IDEM commits to maintain the ozone monitoring network in the
Central Indiana Area during the ozone maintenance period. Any necessary
changes in the ozone monitoring system will be discussed in advance
with the EPA. This commitment is acceptable.
C. Have the Central Indiana Area and the State of Indiana Met All of
the Applicable Requirements of Section 110 and Part D of the Clean Air
Act, and Does the Central Indiana Area Have a Fully Approved SIP Under
Section 110(k) of the Clean Air Act?
We have determined that the Central Indiana Area and the State of
Indiana have met all currently applicable SIP requirements for the
Central Indiana Area, including the requirements under section 110 of
the CAA (general SIP requirements) and the requirements under subpart 1
part D of title I of the CAA (requirements specific to all ozone
nonattainment areas). See section 107(d)(3)(E)(v) of the CAA. In
addition, EPA has fully approved the pertinent elements of the Indiana
SIP. See section 107(d)(3)(E)(ii) of the CAA. We note that SIPs must be
fully approved only with respect to currently applicable requirements
of the CAA, which were those CAA requirements applicable to the Central
Indiana Area at the time the State of Indiana submitted the final,
complete ozone redesignation request for this area, March 26, 2007.
1. The Central Indiana Area Has Met All Applicable Requirements of
Section 110 and Part D of the Clean Air Act
The September 4, 1992, Calcagni memorandum describes EPA's
interpretation of section 107(d)(3)(E) of the CAA. To qualify for
redesignation of an area to attainment under this interpretation, the
State and the area must meet the relevant CAA requirements that come
due prior to the State's submittal of a complete redesignation request
for the area. See also the September 17, 1993, Michael Shapiro
memorandum and 66 FR 12459, 12465-12466 (March 7, 1995, redesignating
Detroit-Ann Arbor, Michigan to attainment of the 1-hour ozone NAAQS).
Applicable requirements of the CAA that come due subsequent to the
State's submittal of a complete redesignation request remain applicable
until a redesignation of the area to attainment of the standard is
approved, but are not required as
[[Page 41663]]
prerequisites to redesignation. See section 175A(c) of the CAA. Sierra
Club v. EPA, 375 F.3d 537 (7th Cir. 2004). See also 66 FR 25424, 25427
(May 12, 2003, redesignation of the St. Louis/East St. Louis area to
attainment of the 1-hour ozone NAAQS).
a. Section 110 and General SIP Requirements
Section 110(a) of title I of the CAA contains the general
requirements for a SIP, which include: enforceable emission limitations
and other emission control measures, means, or techniques; provisions
for the establishment and operation of appropriate devices necessary to
collect data on ambient air quality; programs to enforce the emission
limitations; submittal of a SIP that has been adopted by the State
after reasonable public notice and a hearing; implementation of a
source permit program; provisions for the implementation of part C
requirements (Prevention of Significant Deterioration (PSD)) and part D
requirements (NSR for new sources or major source modifications);
criteria for stationary source emission control measures, monitoring,
and reporting; provisions for air quality modeling; and provisions for
public and local agency participation.
SIP requirements and elements are discussed in the following EPA
documents: ``Procedures for Processing Requests to Redesignate Areas to
Attainment,'' Memorandum from John Calcagni, Director, Air Quality
Management Division, September 4, 1992; ``State Implementation Plan
(SIP) Actions Submitted in Response to Clean Air Act (CAA) Deadlines,''
Memorandum from John Calcagni, Director, Air Quality Management
Division, October 28, 1992; and ``State Implementation Plan (SIP)
Requirements for Areas Submitting Requests for Redesignation to
Attainment of the Ozone and Carbon Monoxide (CO) National Ambient Air
Quality Standards (NAAQS) on or after November 15, 1992,'' Memorandum
from Michael H. Shapiro, Acting Assistant Administrator, September 17,
1993. See also other guidance documents listed above.
Section 110(a)(2)(D) of the CAA requires SIPs to contain certain
measures to prevent sources in a State from significantly contributing
to air quality problems in another State. To implement this provision,
EPA required States to establish programs to address transport of air
pollutants (NOX SIP call and Clean Air InterState Rule
(CAIR)). EPA has also found, generally, that States have not submitted
SIPs under section 110(a)(1) of the CAA to meet the interstate
transport requirements of section 110(a)(2)(D)(i) of the CAA (70 FR
21147, April 25, 2005). However, the section 110(a)(2)(D) requirements
for a State are not linked with a particular area's designation. EPA
believes that the requirements linked with a particular area's
nonattainment designation and classification are the relevant measures
to evaluate in reviewing a redesignation request. The transport SIP
submittal requirements, where applicable, continue to apply to a State
regardless of the designation of any one particular area in the State.
We believe that these requirements should not be construed to be
applicable requirements for purposes of redesignation. Further, we
believe that the other section 110 elements described above that are
not connected with nonattainment plan submissions and that are not
linked with an area's attainment status are also not applicable
requirements for purposes of redesignation. A State remains subject to
these requirements after an area is redesignated to attainment. We
conclude that only the section 110 and part D requirements which are
linked with an area's designation and classification are the relevant
measures for evaluating this aspect of a redesignation request. This
approach is consistent with EPA's existing policy on applicability of
conformity and oxygenated fuels requirements for redesignation
purposes, as well as with section 184 ozone transport requirements.
See: Reading, Pennsylvania proposed and final rulemakings (61 FR 53174-
53176, October 10, 1996 and 62 FR 24826, May 7, 1997); Cleveland-Akron-
Lorain, Ohio final rulemaking (61 FR 20458, May 7, 1996); and Tampa,
Florida final rulemaking (60 FR 62748, December 7, 1995). See also the
discussion on this issue in the Cincinnati, Ohio ozone redesignation
(65 FR 37890, June 19, 2000), and the Pittsburgh, Pennsylvania ozone
redesignation (66 FR 50399, October 19, 2001).
We believe that section 110 elements not linked to the area's
nonattainment status are not applicable for purposes of redesignation.
Nonetheless, we also note that EPA has previously approved provisions
in the Indiana SIP addressing section 110 elements under the 1-hour
ozone standard. We have analyzed the Indiana SIP as codified in 40 CFR
part 52, subpart P and have determined that it is consistent with the
requirements of section 110(a)(2) of the CAA. The SIP, which has been
adopted after reasonable public notice and hearing, contains
enforceable emission limitations; requires monitoring, compiling, and
analyzing ambient air quality data; requires preconstruction review of
new major stationary sources and major modifications of existing
sources; provisions for adequate funding, staff, and associated
resources necessary to implement its requirements; requires stationary
source emissions monitoring and reporting; and otherwise satisfies the
applicable requirements of section 110(a)(2).
b. Part D SIP Requirements
EPA has determined that the Indiana SIP meets applicable SIP
requirements under part D of the CAA. Under part D, an area's
classification--either subpart 1 or subpart 2 (marginal, moderate,
serious, severe, and extreme)--indicates the requirements to which it
will be subject. Subpart 1 of part D, found in sections 172-176 of the
CAA, sets forth the basic nonattainment area plan requirements
applicable to all nonattainment areas. Subpart 2 of part D, found in
section 182 of the CAA, establishes additional specific requirements
depending on the area's nonattainment classification. Since the Central
Indiana Area is designated as a subpart 1 nonattainment area for the 8-
hour ozone standard, the subpart 2 part D requirements do not apply to
these Counties.
c. Part D, Subpart 1 SIP Requirements
For purposes of evaluating this redesignation request, the
applicable subpart 1 part D requirements are contained in sections
172(c)(1)-(9) and 176. A thorough discussion of the requirements of
section 172 can be found in the General Preamble for Implementation of
Title I (57 FR 13498). See also 68 FR 4852-4853, an ozone redesignation
notice of proposed rulemaking for the St. Louis area, for a discussion
of section 172 requirements.
No requirements for the 8-hour ozone standard under part D, subpart
1 of the CAA came due for the Central Indiana Area prior to when the
State submitted the complete ozone redesignation request. For example,
the requirement for an ozone attainment demonstration, as contained in
section 172(c)(1), was not yet due when the State submitted the ozone
redesignation request for these counties, nor were the requirements for
Reasonably Available Control Measures (RACM) and Reasonably Available
Control Technology (RACT) (section 172(c)(1)), Reasonable Further
Progress (RFP) (section 172(c)(2)), and attainment plan and RFP
contingency measures (section 172(c)(9)). All of these SIP elements are
required for submittal after Indiana
[[Page 41664]]
submitted the complete, adopted ozone redesignation request and
maintenance plan for the Central Indiana Area. Therefore, none of the
part D requirements for the 8-hour ozone standard are considered to be
applicable to the Central Indiana Area for purposes of redesignation.
d. Section 176 Conformity Requirements
Section 176(c) of the CAA requires States to establish criteria and
procedures to ensure that Federally-supported or funded activities,
including highway projects, conform to the air planning goals in the
applicable SIP. The requirement to determine conformity applies to
transportation plans, programs, and projects developed, funded, or
approved under Title 23 U.S.C. and the Federal Transit Act
(transportation conformity), as well as to all other Federally-
supported or funded projects (general conformity). State conformity SIP
revisions must be consistent with Federal conformity regulations that
the CAA required the EPA to promulgate.
As with other part D requirements, EPA interprets the conformity
requirements as not applying for purposes of evaluating the ozone
redesignation request under section 107(d) of the CAA. In addition,
please note that conformity rules are required for areas that are
redesignated to attainment of a NAAQS, and that Federal conformity
rules apply where State rules have not been approved. See Wall v. EPA,
265 F.3d 426 (6th Cir. 2001). See also 60 FR 62748 (December 7, 1995)
(Tampa, Florida).
e. Part D New Source Review (NSR) Requirements
EPA has determined that areas being redesignated need not comply
with the requirement that a NSR program be approved prior to
redesignation, provided that the area demonstrates maintenance of the
standard without emission reductions from part D NSR, since Prevention
of Significant Deterioration (PSD) requirements will apply after
redesignation. A more detailed rationale for this view is described in
a memorandum from Mary Nichols, Assistant Administrator for Air and
Radiation, dated October 14, 1994, entitled, ``Part D New Source Review
Requirements for Areas Requesting Redesignation to Attainment.''
Indiana has demonstrated that the Central Indiana Area will be able to
maintain the 8-hour ozone standard without part D NSR in effect, and
therefore, we conclude that the State need not have a fully approved
part D NSR program prior to approval of the redesignation request. The
State's PSD program will become effective in the Central Indiana Area
upon redesignation to attainment. See rulemakings for Detroit, Michigan
(60 FR 12467-12468, March 7, 1995); Cleveland-Akron-Lorain, Ohio (61 FR
20458, 20469-20470, May 7, 1996); Louisville, Kentucky (66 FR 53665,
October 23, 2001); Grand Rapids, Michigan (61 FR 31834-31837, June 21,
1996).
We conclude that the Central Indiana Area has satisfied all
applicable requirements under section 110 and part D of the CAA to the
extent that these requirements apply for purposes of reviewing the
State's ozone redesignation request.
2. The Central Indiana Area Has a Fully Approved SIP Under Section
110(k) of the Clean Air Act (CAA)
EPA has fully approved the Indiana SIP for the Central Indiana Area
under section 110(k) of the CAA for all applicable requirements. EPA
may rely on prior SIP approvals in approving a redesignation request
(See the September 4, 1992, John Calcagni memorandum, page 3;
Southwestern Pennsylvania Growth Alliance v. Browner, 144 F.3d 984,
989-990 (6th Cir. 1998); and, Wall v. EPA, 265 F.3d 426 (6th Cir.
2001)), plus any additional measures it may approve in conjunction with
a redesignation action. See 68 FR 25426 (May 12, 2003). Since the
passage of the CAA of 1970, Indiana has adopted and submitted, and EPA
has fully approved, provisions addressing the various required SIP
elements applicable to the Central Indiana Area for purposes of ozone
redesignation. No SIP provisions relevant to the Central Indiana Area
are currently disapproved, conditionally approved, or partially
approved. As indicated above, EPA believes that the section 110
elements not connected with nonattainment plan submissions and not
linked to the area's nonattainment status are not applicable
requirements for purposes of review of the State's redesignation
request. EPA believes that approval of section 110 SIP elements under
the 1-hour ozone standard satisfies the prerequisite for approval of
the ozone redesignation request for purposes of attaining and
maintaining the 8-hour ozone standard. EPA also believes that since the
part D requirements for the 8-hour ozone standard did not become due
prior to Indiana's submittal of the final, complete redesignation
request, they also are not applicable requirements for purposes of
redesignation.
D. Are the Air Quality Improvements in the Central Indiana Area Due to
Permanent and Enforceable Emission Reductions Resulting From the
Implementation of the Indiana SIP and Applicable Federal Air Pollution
Control Regulations and Other Permanent and Enforceable Emission
Reductions?
We believe that the State of Indiana has adequately demonstrated
that the observed air quality improvements in the Central Indiana Area
are due to permanent and enforceable emission reductions resulting from
the implementation of the SIP, Federal measures, and other State-
adopted measures. In making this demonstration, the State has
documented the changes in VOC and NOX emissions from
anthropogenic (man-made or man-based) sources in the Central Indiana
Area and the changes in NOX emissions from Electric
Generating Units (EGUs) Statewide occurring over the period of 1999-
2005. This period includes 2002, an ozone standard violation year, and
2005, the year in the middle of the 2004-2006 attainment period. The
State has also identified the emission control regulations that have
been implemented in the Central Indiana Area and that have contributed
to attainment of the ozone standard.
Table 2 summarizes the VOC and NOX emissions totals from
the anthropogenic sources in the Central Indiana Area for 1999, 2002,
and 2005 as documented in the State's redesignation request. Table 3
summarizes the NOX emissions trend for EGUs in the Central
Indiana Area, and Table 4 summarizes the NOX emissions trend
for EGUs Statewide.
Table 2.--VOC and NOX Emissions Totals in the Central Indiana Area in
Tons per Summer Day
------------------------------------------------------------------------
Year VOC NOX
------------------------------------------------------------------------
1999................................................ 290.84 293.15
2002................................................ 249.67 264.69
2005................................................ 199.25 220.18
------------------------------------------------------------------------
Table 3.--NOX Emissions Totals for EGUs in the Central Indiana Area in
Tons per Ozone Season (April-September)
------------------------------------------------------------------------
Year NOX emissions
------------------------------------------------------------------------
1999...................................... 31,815
2000...................................... 25,028
2001...................................... 27,394
2002...................................... 22,661
2003...................................... 17,984
2004...................................... 11,798
[[Page 41665]]
2005...................................... 10,591
------------------------------------------------------------------------
Table 4.--NOX Emissions Totals for EGUs in Indiana Statewide In Tons per
Ozone Season
------------------------------------------------------------------------
Year NOX emissions
------------------------------------------------------------------------
1999...................................... 149,827
2000...................................... 133,881
2001...................................... 136,052
2002...................................... 113,996
2003...................................... 99,283
2004...................................... 66,568
2005...................................... 55,486
------------------------------------------------------------------------
Information in the above tables indicates that both VOC and
NOX emissions significantly decreased in the Central Indiana
Area between 2002 and 2005. In particular, the NOX emissions
from EGUs in this area significantly decreased during this period due
to the implementation of EPA's NOX SIP call and acid rain
control requirements. As discussed further below, these emission
reductions are primarily due to the implementation of permanent and
enforceable emission controls, which are believed to have significantly
contributed to the attainment of the 8-hour ozone standard in this
area.
The Statewide NOX emission reductions for EGUs are
believed to have significantly reduced ozone transport into the Central
Indiana Area, further reducing the peak ozone concentrations in this
area. These emission reductions are primarily due to the implementation
of the State's NOX emission control rules stemming from
EPA's NOX SIP call and acid rain control requirements. These
NOX emission control rules are permanent and enforceable. We
agree with the State that these NOX control rules have
significantly reduced ozone levels in and ozone transport to the
Central Indiana Area.
Besides the NOX SIP call regulations, IDEM notes that
the following VOC emission control regulations have been implemented in
the Central Indiana Area (``IAC'' is the Indiana Administrative Code):
326 IAC 8-1-6 Best Available Control Technology (BACT) for non-specific
sources
326 IAC 8-2 Surface Coating Emission Limitations
326 IAC 8-3 Organic Solvent Degreasing Operation Controls
326 IAC 8-4 Petroleum Sources Controls
326 IAC 8-5 Miscellaneous Operations Controls
326 IAC 8-6 Organic Solvent Emission Limitations
326 IAC 8-8.1-1 Municipal Solid Waste Landfills Not Located in Clark,
Floyd, Lake and Porter Counties Controls.
In addition, because EPA had initially designated Marion County as
nonattainment under the 1-hour ozone standard, VOC sources that existed
after July 1, 1990, in Marion County are also subject to RACT rules.
Sources in the surrounding Counties (Boone, Hancock, Hamilton, Johnson,
Morgan, and Shelby Counties) are subject to portions of 326 IAC 8-4
(326 IAC 8-4-4 through 8-4-7 and 8-4-9) that do not apply Statewide.
These emission control requirements have led to reduced VOC emissions
in the Central Indiana Area.
Finally, the State notes that several nationwide rules have been
implemented (or will be implemented in the near future), resulting in
VOC and NOX emission reductions subsequent to 2002 in the
Central Indiana Area and Statewide. These emission reduction rules
include: (a) Tier II emission standards for vehicles and gasoline
sulfur standards; (b) heavy-duty diesel engine standard and low-sulfur
diesel fuel standards; and, (c) Clean Air Non-road Diesel Rule. These
emission reduction rules will provide additional emission reductions in
the future.
The State commits to maintain existing emission control measures
after the redesignation of the Central Indiana Area to attainment of
the 8-hour ozone NAAQS. If an emission control rule must be changed,
the State will submit the rule change as a requested SIP revision to
the EPA. IDEM maintains that it has the legal authority and necessary
resources to enforce any violations of the existing emission control
rules.
E. Does the Central Indiana Area Have a Fully Approvable Ozone
Maintenance Plan Pursuant to Section 175A of the CAA?
In conjunction with its request to redesignate the Central Indiana
Area to attainment of the 8-hour ozone NAAQS, Indiana submitted a SIP
revision request to provide for maintenance of the 8-hour ozone NAAQS
in the Central Indiana Area through 2020, exceeding the 10 year minimum
maintenance period required by the CAA.
1. What Is Required in an Ozone Maintenance Plan?
Section 175A of the CAA sets forth the required elements of air
quality maintenance plans for areas seeking redesignation to attainment
of a NAAQS. Under section 175A, a maintenance plan must demonstrate
continued attainment of the applicable NAAQS for at least 10 years
after the Administrator approves the redesignation to attainment. Eight
years after the redesignation, the State must submit a revised
maintenance plan which demonstrates that maintenance of the standard
will continue for 10 years following the initial 10-year maintenance
period. The maintenance plan must commit the State to submit this
revised maintenance plan to the EPA. To address the possibility of
future NAAQS violations, the maintenance plan must contain such
contingency measures, with a schedule for implementation, as EPA deems
necessary, to assure prompt correction of any future NAAQS violations.
The September 4, 1992, John Calcagni memorandum provides additional
guidance on the content of maintenance plans. An ozone maintenance plan
should, at minimum, address the following items: (1) The attainment VOC
and NOX emissions inventories; (2) a maintenance
demonstration showing maintenance for the first 10 years of the
maintenance period; (3) a commitment to maintain the existing
monitoring network; (4) factors and procedures to be used for
verification of continued attainment; and, (5) a contingency plan to
prevent and/or correct a future violation of the NAAQS.
2. What Are the Attainment Emission Inventories for the Central Indiana
Area?
IDEM estimated future VOC and NOX emissions for the
Central Indiana Area for 2010, 2015, and 2020 to compare with the 2005
VOC and NOX emissions for this area and to demonstrate
maintenance of the ozone standard in this area. Future emissions were
estimated for point (significant stationary sources), area (smaller
point and/or widely distributed stationary sources), on-road mobile,
and non-road mobile sources for this area. To develop the 2010, 2015,
and 2020 emissions, IDEM projected the 2002 base year emissions
applying various source category-specific growth factors and emission
control factors or growth estimates collected directly from the
sources. The following summarizes the procedures and data sources used
by IDEM to derive the projected emissions.
[[Page 41666]]
a. Point Sources
The primary source of point source information for the base period,
2002, was facility-specific emissions and source activity data
collected annually by the State for inclusion in IDEM's annual
emissions statement database. This information includes emissions,
process rates, source operating schedules, emissions control data, and
other relevant source information. Emission growth factors and future
emission control factors provided by the Lake Michigan Air Directors
Consortium (LADCO) were used to project the point source VOC and non-
EGU NOX emissions to 2005, 2010, 2015, and 2020. The
NOX emissions from EGUs were projected based on the EGU
NOX emission budget contained in the Indiana NOX
rule.
b. Area Sources
Area sources are those sources which are generally small, numerous,
and have not been inventoried as specific point, mobile, or non-road
mobile sources. The emissions for these sources are generally
calculated using various surrogates, such as population by county,
estimates of employees in various occupational groups, etc., and
grouped by general source types. The area source emissions are
typically defined at the county level.
IDEM developed area source emissions for a 2002 periodic emissions
inventory submitted to the EPA. The surrogate data used to derive these
emissions were grown to 2005, 2010, 2015, and 2020. The projected
surrogates or other assumed annual growth rates were used to calculate
the projected VOC and NOX emissions for each area source
type.
c. On-Road Mobile Sources
On-road mobile source emissions were calculated using the MOBILE
6.2 emission factor model and other mobile source data, including
estimated traffic levels and vehicle type and age distribution data,
extracted from the area's travel-demand model.
d. Non-Road Mobile Sources
Non-road mobile source emissions were based on emissions in the
2002 National Emissions Inventory (NEI). The 2005, 2010, 2015, and 2020
non-road mobile source emissions were grown from the 2002 NEI
emissions. To address concerns about the accuracy of the emissions
derived for some of the non-road mobile source categories in EPA's non-
road emissions model, LADCO contracted with several companies to review
the base data used in the emissions model. A contractor also estimated
emissions for two non-road source categories not included in EPA's non-
road emissions model, commercial marine vessels and railroads.
Recreational motorboat emissions were significantly updated. The
equipment population and spatial surrogate data for other source types
were also significantly updated. A new non-road estimation model was
also provided by the EPA for the 2002 emissions analysis. The updated
2002 emissions were used to project the emissions to 2005, 2010, 2015,
and 2020.
3. Has the State Demonstrated Maintenance of the Ozone Standard in the
Central Indiana Area?
As part of the redesignation request submittal, IDEM requested a
revision of the Indiana SIP to incorporate an ozone maintenance plan
for the Central Indiana Area as required under section 175A of the CAA.
The maintenance plan demonstrates maintenance of the 8-hour ozone NAAQS
through 2020 by documenting the attainment year (2005) and future VOC
and NOX emissions. Indiana has shown that VOC and
NOX emissions will remain below the attainment year levels
through 2020. An ozone maintenance demonstration need not be based on
ozone modeling. See Wall v. EPA, 265 F.3d 426 (6th Cir. 2001), Sierra
Club v. EPA, 375 F.3d 537 (7th Cir. 2004). See also 66 FR 53094, 53099-
53100 (October 19, 2001), and 68 FR 25430-25432 (May 12, 2003).
Table 5 summarizes the VOC and NOX emissions projected
to occur in the entire Central Indiana Area during the demonstrated
maintenance period. The State of Indiana chose 2020 as a maintenance
year to meet the 10-year maintenance requirement of the CAA, allowing
several years for the EPA to complete the redesignation rulemaking
process. The State also chose 2010 and 2015 as interim years to
demonstrate that VOC and NOX emissions will remain below the
attainment year levels throughout the maintenance period.
Table 5.--VOC and NOX Emissions In the Central Indiana Area During the
Ozone Maintenance Period in Tons per Summer Day
----------------------------------------------------------------------------------------------------------------
Source sector 2005 2010 2015 2020
----------------------------------------------------------------------------------------------------------------
VOC Emissions
----------------------------------------------------------------------------------------------------------------
Area............................................ 94.85 99.29 106.31 100.81
Point........................................... 13.54 14.34 16.00 14.85
Non-Road Mobile................................. 30.36 28.77 24.06 25.29
On-Road Mobile...............................